Section Break  
Comments in opposition:  
1. Comment on attainment status for Southeast Michigan nonattainment area  
October 26, 2022  
Southeast Michigan Council of Governments  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Cc:  
Karll, Kelly C <  
@semcog.org>  
Wednesday, October 26, 2022 4:43 PM  
McDonald, Tracey (EGLE); Vaerten, Marissa (EGLE)  
Karll, Kelly C  
Subject:  
Attachments:  
SEMCOG Comment on Proposed Part 6 Rules  
SEMCOG_PublicComment_Part6APCRules26Oct2022.pdf  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Trace,  
Attached please find SEMCOG comments on the proposed RACT rules.  
Please let me know if you have any questions.  
Have a great day!  
Thanks,  
Kelly  
Kelly Karll, PE  
Manager, Environment & Infrastructure  
(cell)  
@semcog.org  
1001 Woodward Avenue, Suite 1400  
Detroit, MI 48226  
Main: 313-961-4266  
Visit: www.semcog.org  
To help  
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1
October 26, 2022  
Trace McDonald  
Environmental Engineer  
Air Quality Division  
SIP Development Unit  
Michigan Department of Environment, Great Lakes, and Energy  
RE: Proposed Revisions to Part 6 of Michigan’s Air Pollution Control Rules  
Dear Mr. McDonald:  
Thank you for the opportunity to provide comment on the proposed revisions to Part 6 of  
Michigan’s Air Pollution Control Rules.  
The Part 6 revisions, as currently drafted, will impact many sources in Michigan’s current ozone  
nonattainment areas, which includes SEMCOG’s entire seven-county region.  
As we continue to encourage a favorable response by EPA to redesignate the SEMCOG region to  
attainment for ozone, we recognize the State’s need to move forward with the proposed Part 6  
revisions that require Reasonable Available Control Technology (RACT) at specific sources. We  
understand that the proposed RACT rules are required if EPA issues an unfavorable decision and  
bumps the region up to moderate ozone nonattainment.  
Because the RACT rules are specific to moderate ozone nonattainment areas, we request that if  
EPA redesignates the area to attainment, that these proposed rules would not go into effect. Please  
consider rescinding these proposed rules following a favorable ozone attainment decision by EPA.  
Please feel free to contact me with any questions.  
Sincerely,  
Kelly Karll, PE  
Manager, Environment and Infrastructure  
1001 Woodward Ave., Suite 1400 • Detroit, Michigan 48226 • (313) 961-4266 • Fax (313) 961-4869 • semcog.org  
Chris Barnett  
Chairperson  
Supervisor,  
Mandy Grewal  
Vice Chairperson  
Supervisor,  
Laura Kropp  
Vice Chairperson  
Mayor,  
Jason Morgan  
Vice Chairperson  
Commissioner,  
Pauline Repp  
Vice Chairperson  
Mayor,  
Eric Sabree  
Vice Chairperson  
Treasurer,  
Donald Hubler  
Immediate Past Chair  
Secretary,  
Amy O’Leary  
Executive Director  
Orion Township  
Pittsfield Township  
Mount Clemens  
Washtenaw County  
City of Port Huron  
Wayne County  
Macomb ISD  
Section Break  
Other Comments:  
Mixed comments in support and opposition  
3. October 25, 2022  
Household & Commercial Products Association  
Nicholas Georges  
Comments requesting partial revisions  
4. October 12, 2022  
Fishbeck  
Lillian Woolley  
5. October 19, 2022  
American Coatings Association  
Rhett Cash  
6. October 19, 2022  
OLeary Paint  
David OLeary  
7. October 26, 2022  
Michigan Oil and Gas Association  
Jason Geer  
8. October 26, 2022  
Michigan Manufacturers Association  
Caroline Liethen  
9. October 26, 2022  
Consumers Energy  
Kathryn Ross  
10. October 26, 2022  
Willert Home Products, Inc.  
Troy Cummings  
11. October 26, 2022  
RadTech International  
Rita Loof  
12. October 26, 2022  
Saint Clair Systems  
Michael Bonner  
13. October 25, 2022  
PRINTING United Alliance  
Gary Jones  
14. October 11, 2022  
PRINTING United Alliance  
Gary Jones  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Nicholas Georges <  
Tuesday, October 25, 2022 6:02 PM  
McDonald, Tracey (EGLE)  
@thehcpa.org>  
Cc:  
Vaerten, Marissa (EGLE); Carrie Brown  
2022-18 EQ  
Outlook-cidimage00; HCPA Comments on Part 6 VOC RACT Proposal.pdf  
Subject:  
Attachments:  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Dear Mr. McDonald,  
The Household & Commercial Products Association appreciates the opportunity to provide the attached  
comments. Please do not hesitate to contact us if you have any questions or would like to discuss our  
letter. We look forward to participating in tomorrow's hearing.  
Respectfully submitted,  
Nicholas Georges  
Senior Vice President, Scientific & International Affairs  
Household & Commercial Products Association  
1667 K Street NW, Suite 300 | Washington, DC 20006  
Direct: 202-833-7304 - Office: 202-872-8110  
XPAND2022  
HCPA’s Annual Meeting  
December 4-7 | Fort Lauderdale, FL  
REGISTER TODAY  
Watch HCPA’s membership video  
HCPA is Here to Protect Your Business and Promote Your Story  
CONFIDENTIALITY NOTICE: This e-mail message (including any attachments or hyperlinks) contains strictly confidential information from the  
Household & Commercial Products Association (HCPA) and is solely intended for the named recipient(s). This e-mail may contain information that is  
1
confidential or otherwise protected from disclosure. If you are not the intended recipient, any use, dissemination, distribution or copying of this  
communication is prohibited and may be unlawful.  
2
October 25, 2022  
via electronic transmission  
Trace McDonald  
Environmental Engineer  
Michigan Department of Environment, Great Lakes, and Energy  
Air Quality Division  
SIP Development Unit  
525 West Allegan Street  
Lansing, MI 48933  
Subject:  
Part 6 VOC RACT Public Comment - 2022  
Dear Mr. McDonald,  
The Household & Commercial Products Association1 (HCPA) appreciates the opportunity to offer  
comments to the Michigan Department of Environment, Great Lakes, and Energy (EGLE) on their  
proposed rules for the implementation of reasonably available control technology (RACT) for  
sources of volatile organic compounds (VOCs). Among the RACT controls for VOCs are rules2 for  
consumer products. HCPA’s comments will be focused on the consumer products regulations.  
HCPA supports the long-standing commitment by EGLE to adopt regulatory provisions that are  
consistent with other states that have adopted more stringent volatile organic compound (VOC)  
limits for consumer products than the U.S. Environmental Protection Agency’s (U.S. EPA) National  
Volatile Organic Compound Emission Standards for Consumer and Commercial Products.3 The  
proposed amendments are based on the Ozone Transport Commission (OTC) 2012 Model Rule for  
Consumer Products4 (hereinafter referred to as “Phase IV OTC Model Rule”), updating from the  
OTC 2006 Model Rule for Consumer Products5 (hereinafter referred to as “Phase II OTC Model  
Rule”), and includes the 2013 technical update. The comments that HCPA provides are intended  
to identify revisions that will enhance consistency with the OTC Model Rule and the final consumer  
1 The Household & Commercial Products Association (HCPA) is the premier trade association representing companies  
that manufacture and sell $180 billion annually of trusted and familiar products used for cleaning, protecting,  
maintaining, and disinfecting homes and commercial environments. HCPA member companies employ 200,000 people  
in the U.S. whose work helps consumers and workers to create cleaner, healthier and more productive lives.  
2 Mich. Ann. Code R. 336.1660 and 336.1661  
3 40 CFR Part 59 Subpart C  
4 The text of the fourth OTC Model Rule for Consumer Products can be found at  
https://otcair.org/upload/Documents/Model%20Rules/OTC%20CP%20Model%20Rule%202012%20CLEAN_vs2010.20  
12%2005%2010.pdf  
5 The text of the second OTC Model Rule for Consumer Products can be found at  
https://otcair.org/upload/Documents/Model%20Rules/OTC%20Consumer%20Products%20Final%20MR1.doc  
1667 K Street NW, Suite 300, Washington, DC 20006 | 202-872-8110 | www.theHCPA.org  
Part 6 VOC RACT Public Comment - 2022  
October 25, 2022  
Page 2 of 5  
products regulations promulgated by Colorado,6 Connecticut,7 Delaware,8 Maryland,9 New  
Hampshire,10 New York,11 Ohio,12 Rhode Island,13 and Utah.14  
Statement of Interest  
HCPA member companies manufacture and market more than two-thirds of the broad product  
categories governed by both EGLE’s current regulation and the potential amendments.  
Comments  
A. HCPA supports adoption of regionally consistent consumer products regulations based on  
the OTC Model Rule.  
For over 20 years, HCPA has supported – and continues to support – the efforts by the OTC to  
develop a workable regional regulatory framework for states to achieve technologically and  
commercially feasible reductions that are necessary to demonstrate compliance with State  
Implementation Plan (SIP) commitments.  
HCPA participated as an active stakeholder in the previous rulemaking proceedings conducted by  
the EGLE, provided comments to EGLE in April 2022 on the draft rules and related guidance, and is  
on record as supporting the current Michigan consumer products regulation and the other final  
state regulations that are based on the Phase IV OTC Model Rule or the Phase II OTC Model Rule.15  
HCPA supports these regulations because consistent regional regulatory standards achieve  
significant improvements in air quality without impeding interstate commerce.  
6 5 CCR 1001-25 (took effect on May 1, 2020).  
https://www.sos.state.co.us/CCR/GenerateRulePdf.do?ruleVersionId=8227&fileName=5%20CCR%201001-25  
7 Conn. Agencies Regs. § 22a-174-40 (took effect May 1, 2018).  
https://eregulations.ct.gov/eRegsPortal/Browse/RCSA/Title_22aSubtitle_22a-174Section_22a-174-40/  
8 7 DE Admin. Code 1141 § 2 (took effect January 1, 2017).  
https://regulations.delaware.gov/AdminCode/title7/1000/1100/1141.pdf  
9 COMAR § 26.11.32 (took effect January 1, 2018). http://mdrules.elaws.us/comar/26.11.32  
10 N.H. Code Admin. Env-A 4100 (took effect January 1, 2017).  
https://www.des.nh.gov/sites/g/files/ehbemt341/files/documents/2020-01/Env-A%204100.pdf  
11 N.Y. Comp. Codes R & Regs. Title 6, Ch. III Subpt. 235 (took effect January 1, 2022).  
https://www.dec.ny.gov/docs/air_pdf/adopted235.pdf  
12 Ohio Admin. Code Chapter 3745-112 et seq. (took effect June 22, 2022). https://codes.ohio.gov/ohio-  
administrative-code/chapter-3745-112  
13 250-RICR-120-05-31 (took effect Jan. 1, 2020). https://rules.sos.ri.gov/regulations/part/250-120-05-31  
14 Utah Admin. Code R307-357 (took effect September 1, 2014). https://adminrules.utah.gov/public/search/R307-  
357/Current%20Rules  
15 Other states with VOC regulations for consumer products based on the Phase II OTC Model Rule include Illinois,  
Indiana, Maine, Massachusetts, New Jersey, Pennsylvania, and Virginia, as well as the District of Columbia  
Part 6 VOC RACT Public Comment - 2022  
October 25, 2022  
Page 3 of 5  
B. HCPA supports rescinding Rule 661.  
The draft proposal is to rescind Rule 661, definitions for consumer products. HCPA supports this  
action so that the definitions for the Consumer Products Rules are within the same section as the  
other provisions.  
C. HCPA requests that the proposed rules become effective one year after the date of  
publication of the final rules.  
As currently written, it is unclear when the EGLE would transition from the OTC Phase II Model  
Rule to the OTC Phase IV Model Rule. It would appear as though EGLE would stop using the OTC  
Phase II Model Rule on January 1, 2023, then have a period of a few months for which the U.S.  
EPA’s regulation would apply, and on May 1, 2023, EGLE would utilize the OTC Phase IV Model  
Rule. HCPA requests that these dates be updated such that it is clear to the regulated community  
when EGLE would seamlessly transition from the OTC Phase II Model Rule to the OTC Phase IV  
Model Rule. Further, HCPA requests a compliance date be one year after the date of publication  
of the final regulation to ensure sufficient time.  
Many HCPA member companies manufacture and market products on a nationwide basis and  
thus, these products already comply with the comparable VOC limits mandated by the current  
California regulation. However, other HCPA member companies that manufacture and/or  
distribute products on a regional basis need a reasonable amount of time to:  
Reformulate products to comply with the new VOC limits, conduct stability testing, efficacy  
testing and make the necessary changes to product labels and other documents such as  
Safety Data Sheets (SDSs) and Technical Data Sheets (TDSs); and/or,  
Make necessary changes in product distribution channels to ensure compliant products are  
supplied to retailers and distributors.  
Reformulating products and changing distribution systems is an expensive process. Moreover,  
there are instances in which proposed federal and state regulations (impacting other issues not  
related to VOC regulations) have been withdrawn, postponed and altered unexpectedly –  
sometimes at the last minute. Consequently, companies do not expend time and money to  
reformulate products or to restructure distribution networks to comply with new regulations until  
these requirements have binding legal effect.  
For the reasons stated above, the proposed compliance date of May 1, 2023, would not provide  
sufficient time for many regional and small product manufacturers and marketers to formulate (or  
reformulate) products or to make necessary changes in distribution channels to comply with the  
new/revised VOC limits and other provisions of the amended regulation. Therefore, HCPA  
requests a compliance date be at least one year after the date of publication of the final regulation  
to ensure sufficient time.  
Part 6 VOC RACT Public Comment - 2022  
October 25, 2022  
Page 4 of 5  
D. HCPA supports EGLE’s decision to use the federal definition of a “Volatile Organic  
Compound”.  
HCPA appreciates EGLE’s use of the federal definition16 for “Volatile Organic Compound”. By using  
the federal definition, EGLE automatically ensures that the definition of a VOC is consistent with  
the EPA and other states that use the federal definition whenever a new compound is exempted  
from the definition.  
E. HCPA requests an exclusion for “Solid Air Fresheners” which use PDCB.  
HCPA thanks EGLE for providing an exclusion for which “Toilet/Urinal Care Products” containing  
not less than 98% para-dichlorobenzene (PDCB). This proposed exclusion is similar to the  
exclusion granted by several other states,17 either explicitly as is the case with this proposal or by  
excluding the standards for “Toilet/Urinal Care Products”.  
For similar reasons, HCPA also requests an exclusion for “Solid Air Fresheners” which contain at  
least 98% PDCB. PDCB is a non-agricultural, non-food use pesticide with primary uses related to:  
(1) controlling moths and carpet beetles; and (2) to deodorize restrooms and waste containers.  
PDCB does not contribute significantly to ozone formation, yet the California Air Resources Board  
(CARB) prohibited18 its use in “Solid Air Fresheners” due to its potential of being a carcinogen. This  
prohibition carried into the OTC Model Rules, yet after the publication of the Phase II OTC Model  
Rule, EPA found19 that:  
In accordance with the EPA’s Final Guidelines for Carcinogen Risk  
Assessment (March 2007), the CARC classified para-dichlorobenzene as “Not  
Likely to be Carcinogenic to Humans” based on evidence that a non-  
mutagenic mode of action (MOA) involving mitogenesis was established for  
para-dichlorobenzene induced liver tumors in mice and that the  
carcinogenic effects are not likely below a defined dose that does not  
perturb normal liver homeostasis (e.g., increased liver cell proliferation).  
While the Phase IV OTC Model Rule was not updated to reflect EPA’s more recent determination  
regarding the hazardous nature of PDCB, HCPA asks that EGLE provides an exemption for “Solid Air  
Fresheners” containing at least 98% PDCB.  
Conclusion  
HCPA appreciates the opportunity to provide this letter to EGLE on the proposed rules for the  
implementation of RACT for sources of VOCs. HCPA is on record in Michigan and 16 other states  
(and the District of Columbia) as supporting regulations that are consistent with the OTC Model  
16 40 CFR § 51.100(s)  
17 Colorado, Illinois, Indiana, New Hampshire, Ohio, and Utah  
18 CARB’s Final Statement of Reasons on PDCB can be found at  
https://ww2.arb.ca.gov/sites/default/files/barcu/regact/conprod/fsor.pdf  
19 EPA. Reregistration Eligibility Decision for Para-dichlorobenzene. Sept. 2007. Found at  
https://www3.epa.gov/pesticides/chem_search/reg_actions/reregistration/red_PC-061501_28-Sep-07.pdf  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Woolley, Lillian  
@fishbeck.com>  
Friday, October 14, 2022 3:55 PM  
Vaerten, Marissa (EGLE); McDonald, Tracey (EGLE)  
VOC Rules?  
Subject:  
Follow Up Flag:  
Flag Status:  
Follow up  
Completed  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Hi,  
We are putting some comments together and I noticed a reference to “ (3) Subrule (2) of this rule notwithstanding,  
and as an alternative to the allowable emission rate established by table 63, the existing paper coating lines at  
Fletcher pPaper cCompany of Alpena may comply with subrule (2) of this rule by not exceeding a volatile  
organic compound emission rate of 180 tons per calendar year and 30 tons per calendar month. “ in Rule  
610. Can it be eliminated? I do not believe this facility exists anymore. It was abandoned several years ago. I think it was  
located at 318 Fletcher Street in Alpena if you want to look it up.  
Lillian L. Woolley, PE | Senior Chemical Engineer  
Fishbeck | w: 248.324.4785 | c:  
| Fishbeck.com  
1
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Rhett Cash <  
Wednesday, October 19, 2022 4:13 PM  
Vaerten, Marissa (EGLE)  
@paint.org>  
Cc:  
McDonald, Tracey (EGLE)  
Part 6 VOC RACT Public Comment - 2022 (ACA Comments)  
ACA Comments - MI EGLE VOC Rule Package.pdf  
Subject:  
Attachments:  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Hi Marissa –  
Please see attached for ACA’s comments on Michigan EGLE’s proposed VOC RACT Rule (Part 6). Thank you for your  
consideration of our comments and let me know if you have any questions or require additional clarification. Have a  
great rest of the week!  
All the best,  
Rhett  
Rhett Cash ▪ American Coatings Association ▪ Counsel, Government Affairs  
202.719.3680 (o) |  
(c) |  
@paint.org | www.paint.org  
901 New York Avenue NW ▪ Suite 300 West ▪ Washington, DC 20001  
Coatings protect. Coatings preserve. Coatings provide.  
1
October 26, 2022  
Ms. Marissa Vaerten  
Environmental Quality Analyst  
Air Quality Division, SIP Development Unit  
Michigan Department of Environment, Great Lakes, and Energy  
525 W Allegan St.  
Lansing, MI 48933  
RE:  
Michigan Department of Environment, Great Lakes, and Energy Proposed VOC RACT Rule  
(Part 6); ACA Comments  
Dear Ms. Vaerten:  
The American Coatings Association (ACA) submits the following comments to the Michigan Department of  
Environment, Great Lakes, and Energy (MI EGLE) regarding its proposed VOC RACT Rule (Part 6). ACA is a  
voluntary, nonprofit trade association working to advance the needs of the paint and coatings industry and the  
professionals who work in it. The organization represents paint and coatings manufacturers, raw materials  
suppliers, distributors, and technical professionals. ACA serves as an advocate and ally for members on  
legislative, regulatory, and judicial issues, and provides forums for the advancement and promotion of the  
industry through educational and professional development services. ACA appreciates the opportunity to  
comment on the proposal and looks forward to working with MI EGLE throughout the rulemaking process.  
Compliance Date  
ACA requests that MI EGLE adopt a compliance date of one year from the date of adoption of a final rule for  
the various coatings rules included in the proposed VOC RACT Rule (Part 6). The proposed compliance date of  
1/1/2023 is unreasonable and impractical. As a general matter, ACA members require sufficient lead time to  
adjust formulations and supply chain processes in order to ensure compliance with new VOC limits, labeling,  
and reporting requirements. The proposed 1/1/2023 compliance date will not allow the coatings industry  
sufficient time to adjust production, labeling, and distribution networks to efficiently and effectively  
implement the new rule’s requirements.  
Manufacturers, distributors, and retail stores employ extensive computer systems that require upgrades to  
incorporate new formulations and ensure non-compliant products are not sold into jurisdictions with new VOC  
limits. Furthermore, manufacturing and labeling costs are generally expensive, and coatings manufacturers  
tend to manage formulation changes to their products to minimize costs stemming from obsolete products  
and labels. Additionally, manufacturers will need sufficient time to properly communicate these changes to  
their distributors and retail customers to ensure compliance with new VOC limits. Finally, most companies wait  
until a rule is finalized and its requirements are certain before implementing changes to ensure compliance  
because it helps minimize costs. This means that companies will not implement changes during the early parts  
of a rulemaking and will need adequate time after finalization of a new rule to make appropriate changes. As  
such, industry typically needs at least a year to properly implement the necessary changes to comply with the  
new rule’s requirements.  
901 New York Avenue, NW – Suite 300 West | Washington, DC 20001 | 202-462-6272  
Given MI EGLE’s proposed compliance dates of 1/1/2023 and the need for industry to have adequate lead time  
for implementation and compliance, ACA respectfully requests that the Department change the compliance  
dates in the proposal to one year after the date of adoption of a final rule.  
Thank you for your consideration of our comments. Please do not hesitate to contact me if you have any  
questions or require additional clarification.  
Sincerely,  
Rhett Cash  
Counsel, Government Affairs  
**Submitted via email**  
2
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
David O'Leary <  
@olearypaint.com>  
Wednesday, October 19, 2022 12:02 PM  
Vaerten, Marissa (EGLE); McDonald, Tracey (EGLE)  
OTC Phase II concerns  
Subject:  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Marissa Stegman,  
Trace McDonald,  
I’d like to weigh in on the challenges that a move to OTC Phase II at this particular point in time raises which it makes it  
basically impossible for our company to comply with in the timeframe suggested.  
Passanno Paint (a 96 year old family business) in New York State actually was forced to stop  
manufacturing altogether when they couldn’t formulate fast enough to meet the new regulations, and  
we’d like to avoid that scenario ourselves.  
We currently have over 700 active formulas which have been developed over decades, a sudden  
reformulation isn’t feasible with the size of our staff and effort that would be involved.  
We have a significant monetary investment in current inventory of labels that would become worthless  
with a sudden change, which would also be true for some raw materials.  
Timing. Because of the Texas Deep Freeze/Covid/Supply Chain Issues, our primary Resin suppliers have  
called “Forced Majeure” and canceled supply contracts and put customers on allocation, with just a  
fraction of last years volume available, and no new customers or new products.  
Many products will require new technology resin to achieve a workable product at this new VOC limit,  
we don’t have access to this new resin until supply comes back and Force Majeure is lifted.  
The logical step from the current AIM standard would be to go to OTC Phase I, we have been assuming  
that would be the next step and our preparation has been with that in mind, we obviously misjudged  
but isn’t that a logical progression.  
Our specific request in order of preference would be:  
Make OTC Phase I the first step, followed up with OTC Phase II at a future date.  
Carve out an exclusion for O’Leary Paint because of our very unique circumstances.  
Carve out an exclusion for O’Leary Paint based on OTC Phase I rather than Phase II.  
Carve out an exclusion to OTC Phase I, for a Michigan Manufacturer.  
Carve out an exclusion for small producer (under 2,000,000 gallons)  
We appreciate your mission and the difficult position you are in trying to reasonably balance goals and results that could  
have significant impact on people and companies.  
Please don’t hesitate to reach out to me if I can clarify anything, or if you need additional information.  
David O’Leary  
1
President O’Leary Paint  
@olearypaint.com  
300 E. Oakland Ave.  
Lansing, MI 48906  
2
Vaerten, Marissa (EGLE)  
From:  
Sent:  
Jason Geer  
Wednesday, October 26, 2022 4:13 PM  
@michiganoilandgas.org>  
To:  
Cc:  
Vaerten, Marissa (EGLE); McDonald, Tracey (EGLE)  
Kownacki, Alec (EGLE); Eric Johnson; 'J. Scott Huber'; Tim Baker  
MOGA's Part 6 Public Comments  
Subject:  
Attachments:  
MOGA Public Comment on Part 6 - CTG Proposed Regulations 10-26-2022.pdf  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Marissa and Trace:  
Please find attached the Michigan Oil and Gas Association’s comments on EGLE’s part 6 draft rules.  
These comments were prepared by Eric Johnson and Scott Huber, so please feel free to reach out to them or myself if  
you have any questions.  
Please confirm receipt.  
Thanks,  
Jason Geer  
Michigan Oil and Gas Association  
C:  
1
October 26, 2022  
Alec Kownacki  
Meteorologist  
Air Quality Division  
Michigan Department of Environment, Great Lakes and Energy  
kownackiA@michigan.gov  
Re:  
Crude Oil and Natural Gas Industry’s Input to Part 6  
Emission Limitation and Prohibition  
Existing Sources of Volatile Organic Compound Emissions  
Dear Mr. Kownacki:  
The Michigan Oil and Gas Association (MOGA) is providing this document as a 2nd public  
comment response to the proposed Part 6 rules. MOGA had provided a public response on June  
16, 2022 and wishes to provide additional discussion and clarity related to the current Part 6  
proposal.  
MOGA is primarily concerned with the potential impact to marginal wells and the producers  
managing these wells. By definition, marginal wells produce 15 Barrels of Oil Equivalent per  
day (BOED) or less. The term “marginal” relates to the reduced income margins that impact the  
longevity and potential recovery of remaining resources. In many cases, these marginal wells  
receive a special exemption from the Internal Revenue Service (IRS) to reduce tax burdens to  
allow for continued production and prevent wasteful actions. Per section MCL 324.61504 of  
Michigan’s Natural Resources and Environmental Protection Act, Act 451 of 1994, the State of  
Michigan prohibits “waste”. “Waste” represents the would be plugging and abandonment of  
otherwise sustainable marginal production wells prematurely and before all viable production  
can be extracted. MOGA is concerned that additional regulations placed on existing marginal  
wells will exacerbate early plugging and abandonment. Early plugging and abandonment of  
producing wells not only affects the price of energy, but also impact beneficial government and  
social programs within the State of Michigan.  
Early plugging and abandonment of marginal wells would impact the Michigan Natural  
Resources Trust Fund’s (MNRTF) ability to purchase recreational lands, build facilities, create  
bike paths and trails and maintain current and future public land assets. On November 6, 1984,  
Michigan residents voted on Proposal B which amended our State Constitution to direct “oil, gas,  
and other mineral lease and royalty payments” to be placed into the MNRTF. The vast majority  
of Michigan’s oil and gas wells are considered marginal wells and as residents of the State of  
Michigan, MOGA is concerned that response to #13 of the required and completed Regulatory  
Impact Statement (RIS) for “Changes to R336.1601 – R336.1662” does not address the potential  
impacts to “revenue to other state or local governmental units”.  
Regarding the required and completed RIS “Changes to R336.1601 – R336.1662”, MOGA  
believes that the State of Michigan has not adequately addressed RIS questions #18 through #27  
relating to the potential impacts to Small Businesses. The Environmental Protection Agency  
(EPA) indicates that 98-99% of all US oil and gas production companies meet the definition of a  
small business. This percentage aligns with Michigan’s producers and operators. MOGA is  
providing a brief synopsis to illustrate our concerns with statements made in the RIS through the  
following examples: Question #19A indicates small businesses “will need to increase  
recordkeeping”. This statement does not align with costly proposed Optical Gas Imaging (OGI)  
survey and stack-testing requirements listed in Part 6 proposed Sections R336.1640 through  
R336.1644. The response to Question #20 of the RIS indicated “There is no known  
disproportionate impact on small businesses due to these rules” is completely false. Part 6  
proposed rules will adversely impact 98-99% of Michigan’s oil and gas producers. The response  
to Question #24 of the RIS states; “The rules revision are required by the USEPA and therefore  
must be met by all affected sources at whatever cost is necessary”. MOGA does not agree with  
this statement as all governmental agencies are required to provide a cost-benefit analysis to  
justify regulatory endeavors, especially when regulations will disproportionately impact small  
businesses.  
MOGA staff has been working with State of Michigan staff since the EPA’s publication of  
Control Technique Guideline for the Oil and Natural Gas Industryin October of 2016 and the  
subsequent Reasonable Available Control Technology Analysis for Volatile Organic  
Compoundsprepared by the Michigan Department of Environment, Great Lakes, and Energy  
(EGLE) in January of 2020. The EGLE document summarized the State of Michigan’s analysis  
to determine “what changes would potentially need to be made to Michigan’s Air Pollution  
Control Rules Part 6”. Table 1 listed “Oil and Natural Gas Industry – Compound Leaks from  
Petroleum Refinery Equipment” as a Top 10 Control Technique Guidelines (CTGs) based on  
VOC Emissions in Michigan. For clarification, upstream oil and gas production is not a  
petroleum refinery and is a completely different industry segment. On pages 7 and 8 of EGLE’s  
analysis report under the “Potential Negative Declarations” title heading, the State of Michigan  
indicated that “Further Analysis” was needed for industry segments listed under Table 5 titled  
“CTG Categories requiring further analysis”. Under Table 5, “Oil and Natural Gas Industry –  
Dependent on specific equipment, please see CTG” was listed as requiring further analysis. Per  
the report, categories listed under Table 5 had the potential to receive a “negative declaration”  
indicating that “CTG would not have any meaningful reductions to VOC emissions at facilities  
in the NAA”. Prior to the covid-19 crisis, MOGA staff had many discussions with EGLE staff  
via phone calls and email communication indicating a likelihood of a “negative declaration” on  
source categories, beginning with oil storage tanks. Unfortunately, covid-19 disrupted  
discussions and progress working towards a “deeper analysis” of oil and natural gas emissions  
sources outlined in the EGLE’s report. As covid-19 fears subsided, MOGA staff resumed  
discussions with a different group of EGLE staff members. MOGA is concerned that “further  
analysis” has not been properly conducted and will likely request evidence to substantiate  
EGLE’s “deeper analysis” of individually proposed Part 6 regulations based on statements made  
in the RIS, previous work endeavors and communications with EGLE staff and the required  
analysis proposed in the EGLE’s January 2020 document.  
The following information was initially submitted in MOGA’s June 16, 2022 public comment  
statement and is being re-submitted because of the validity and pertinence to the proposed Part 6  
regulations.  
MOGA collected the following information and provided the following discussion to help define  
and outline the scope and applicability of the proposed Part 6 rules and to further explain  
MOGA’s concerns. Responses #1 through #4 pertain to marginal wells and the necessity to have  
a marginal well exemption. The Responses #5 through #40 pertain directly to specific proposed  
Part 6 Rules and Subrules.  
1) MOGA felt that beginning with a stepwise explanation of the importance of marginal well  
exemption was beneficial to our discussion. Below is a list of the following  
nonattainment counties and a count of the oil and natural gas producing wells located in  
each county:  
County  
Allegan  
Producing wells  
70 (est.)  
Berrien  
0
Livingston  
Macomb  
Monroe  
Muskegon  
Oakland  
St. Clair  
Washtenaw  
Wayne  
13  
2
0
10  
13  
35  
40  
7
TOTAL  
190  
Michigan has roughly 14,000 oil and gas wells. Of the 14,000 oil and gas wells, roughly  
90% of the wells meet the definition of a marginal well. Of the approximately 14,000 oil  
and gas wells in Michigan, roughly 190 producing wells are located in the nonattainment  
counites. Of the roughly 190 wells in the nonattainment areas, approximately 75% or  
more meet the definition of a “marginal well”.  
A “marginal well” is defined as a well that operates with small economic return or profit  
margin based on this formula; Production Revenue minus Fixed & Variable Operating  
Expenditures = Small or “Marginal” Returns.  
For this reason, a “Marginal Well” is defined by the Internal Revenue Service (IRS) as a  
well that produces 15 barrels of oil equivalent (BOE) or less per day.  
2) To determine whether a well meets the IRS definition of “marginal well”, the BOE can be  
calculated using the following constants and illustrated by the two production examples:  
Barrel of Oil (Bbl)  
6000 standard cubic feet (scf) of Natural Gas  
=
=
1 BOE  
1 BOE  
Production Example #1:  
9 Bbls of Oil + 36000 scf Natural Gas = 15 BOE/day  
To scale the amount of natural gas produced, 36,000 scf = 36 mscf. “mscf” is Thousand  
Standard Cubic Feet and is the volume typically used in equipment operation and the  
commodities market for sale. At an average natural gas rate of $4.00 per mscf, the above  
well would generate $144.00 dollars per day from natural gas production.  
Most of Michigan’s marginal wells make far less than the above example. The typical  
marginal well in Michigan is calculated below:  
Production Example #2:  
2.3 Bbls of Oil + 1700 scf of Natural Gas = 2.58 BOE/day  
To scale the amount of natural gas produced by a typical marginal well in Michigan,  
1700 scf = 1.7 mscf. At an average natural gas rate of $4.00 per mscf, the above well  
would generate $6.80 dollars per day from natural gas production.  
The two production examples above highlight MOGA’s concern over the cost of  
implementation of regulations versus the derived benefit. The amount of potential  
emissions from marginal wells is minute compared to the cost of implementation, derived  
environmental benefit and potential long-term impact to energy prices.  
3) MOGA applauds the EGLE’s recognition of MOGA’s concerns regarding marginal wells  
and the proposed exemption from fugitive emissions monitoring outlined in  
R336.1644(a)(2) & (a)(3) of the proposed Part 6 Rules, but has additional operational  
concerns related to lack of marginal well exemption in the remaining proposed segments  
listed in R336.1640 through R336.1643.  
Proposed Part 6 Rules, R336.1640 through R336.1643 do not provide exemption for  
marginal wells with 15 BOE/day or less production or as stated in R336.1644(a)(3),  
“Have gas to oil ratios of less than 300 standard cubic feet of gas per barrel of oil  
produced”. These exemptions must be extended to proposed Part 6 Rules, R336.1640  
through R336.1643 for the following reasons:  
a) Existing marginal wells often do not produce enough gas to maintain a continuous  
pilot on an enclosed combustor, combustion device or process units. This means that  
a marginal well site or facility located in the nonattainment area would be required  
to purchase propane to maintain a pilot on a control device because the well site or  
facility does not produce enough natural gas on its own to maintain a continuous  
pilot light. This would cause more VOC hydrocarbon emissions than the well site  
alone would produce. In effect, the proposed control of emissions from sources at a  
marginal well site would increase the amount of VOC emissions rather than reduce  
emissions.  
b) All Conventional Wells (non-marginal wells) decline rapidly over a short period of  
time. Contrary to popular belief, you cannot “turn the pumps on” or “increase  
production” from a depleting resource. Initially, conventional wells have the profit  
margins and oil/natural gas volumes to meet the standards in the proposed Part 6  
Rules. MOGA does not dispute the attempt to control emissions from conventional  
wells with higher production and higher correlated emission potential. However,  
once a well reaches the operational threshold of 15 BOE/day, potential emissions  
drop to a point where proposed Part 6 regulations shown in R336.1640 through  
R336.1643 cannot be met.  
Below is real-life scenario from a Michigan producing company related to  
implementation of Subpart OOOOa regulations (very similar to proposed CTG  
regulations) and the absolute need for an off-ramp and exemption once a well  
reaches 15 BOE/day status:  
A small entity oil and gas producer in Michigan was subject to Subpart OOOOa  
regulations for tank emissions. The well and production facility utilized a flare to  
reduce tank emissions by 95%. The well experienced a rapid production decline  
and ultimately reached “dead oil” status in a couple years. The well no longer  
produced enough gas to keep a constant pilot on the flare burning to meet the  
Subpart OOOOa regulations for the tank battery with minimal working, standing  
and breathing losses. In order to continue producing the now marginal well  
while meeting the required Subpart OOOOa regulations, the small entity  
purchased and installed a propane tank to keep the pilot light burning. Over  
time, the cost of conducting semi-annual LDAR surveys, purchasing propane to  
keep a flare pilot lit and reporting costs for minimal to no tank emissions led the  
small entity producer to plug the well even though the well would likely produce  
at a marginal status for many more years at a constant rate below 15 BOE/day.  
The above scenarios illustrate the importance of a regulation off-rampfor marginal  
wells through exemption. It is worth pointing out that like reason #1 above, this real-life  
scenario also emitted more hydrocarbons during its production life via purchasing and  
burning propane to keep a pilot light lit than the facility would have emitted on its own.  
Unfortunately, the well mentioned above and many more like it have been plugged with  
the correlated lack of production contributing to the higher energy and gasoline prices.  
4) To further illustrate the importance of a marginal well exemptions, MOGA is providing a  
cost breakdown of a marginal wells recently submitted to the EPA during a public  
comment period. The data shows how razor-thin the operating margins are for marginal  
wells. The table also conveys the impact of OOOOa regulatory impacts to the  
operational viability of marginal oil and gas wells in Michigan.  
The well scenario depicted above would result in a plugged well unless a regulatory  
exemption is allowed. MOGA cannot overstate how important marginal well exemption  
is to the economic viability and continued operation of marginal wells in the Michigan  
Basin. Without these exemptions, many of 190 producing wells in the nonattainment  
areas will likely be plugged and further exacerbate the escalating energy prices.  
5) Part 6 title should include in the description “Located in Non-Attainment Areas” because  
throughout the rules the non-attainment counties are referred to and nothing is addressed  
in the attainment counties.  
MOGA is presenting the following individual analysis of applicable proposed Part 6 rules and  
regulations.  
General Comments:  
1) Rule 601(e)&(f)&(h) The petroleum industry is segregated into three (3) segments.  
They are referred to Upstream (for the production of commodities within the formations  
found below ground level), Mid-stream (for the processing, separation and conditioning  
of crude oil and natural gas) and Downstream (for the distribution of the final conditioned  
resources for manufacturing and utility distribution). The definitions for Rule  
601(e)&(f)&(h) should reflect the designations for clarity throughout the Rule.  
2) Rule 601(i) There are only three (3) segments in the industry. Comment #2 reflects the  
segregation.  
3) Rule 602(2) In the subsections pertaining to the upstream production and refining  
(1622, 1623, 1629 and 1640), reference within these sections calls upon 1602 for clarity,  
but Rule 602(2) refers back to the rule mentioned, thus there is a “closed loop” allowing  
some reference but no conclusions.  
4) Rule 602(4)(ii) As written this subsection is unclear.  
5) Rule 622 & 623 Upstream production engineers and operators do not have a  
comprehensive understanding of the refinery trains and the control schemes for operating  
fractionation, along with product storage within the plant area (floating roof tanks).  
MOGA will contact a company which operates refineries for comments on this section.  
6) Rule 629 MOGA will contact straddle plant operators and/or gas storage companies for  
comments on this rule.  
7) From Rule 629 to 639; none of these proposed regulations have applications for crude oil  
and natural gas production.  
8) Within any of the remaining rules for crude oil and natural gas production (640, 641, 642,  
643 and 644) there are references to “2015 ozone nonattainment areas.Is there any  
current (2020-2021) information highlighting the implementation of current federal  
regulations standards beginning in 2012? Current information about VOC and ozone  
emissions will support efforts by our industry to reduce environmental impacts. Eight  
years of no reporting or changes appears to be unreasonable.  
R336.1640 - Emission of volatile organic compounds from existing storage vessels in the oil  
and natural gas industry located in the 2015 ozone nonattainment areas.  
1) 336.1640(3)(a) How is this calculated? Each storage vessel evaluated separately?  
Production from multiple wells entering a facility through a header system with tank  
batteries having equilibrium piping and vapor collection system. The practice would be to  
divide PTE for production to a tank battery by the number of tanks connected to the  
shared vapor headspace and equilibrium piping. Note: These questions and comments  
were provided to AQD in the June 16, 2022 letter.  
2) 336.1640(3)(b) – “Storage vessels with uncontrolled actual organic compound emissions  
of less than 4 tons per 12-month rolling average.” Note: any further explanation makes  
this subpart confusing. The shortness of the explanation will allow an off-ramp status  
should the facility reach a marginal well classification for the remainder of the productive  
life. Note: This subpart was addressed in the June 16, 2022 letter.  
3) 336.1640(3)(f) Does this allow for the combination of standard oil tanks with  
equilibrium piping and shared vapor headspace to be considered as 1 tank to meet the  
exemption?  
4) 336.1640(3)(g) - VOC emission control requirements for storage vessels are subject to  
requirements for storage vessels in “Standards of Performance for Volatile Organic  
Liquid Storage Vessels (Including Petroleum Liquid Storage Vessels) for which  
constructed, reconstruction or modification commenced after July 23, 1984” 40 CFR part  
60. Note: the remaining references do NOT reflect upstream production for this Subpart  
an should be removed.  
5) 336.1640(4) - What if the amount of natural gas coming from the “stripper/marginal”  
well is so small that propane needs to be supplemented to keep a pilot flame burning?  
Wouldn’t that be emitting more emissions than the well’s production alone? These are  
questions that were posed in the June 16, 2022 letter.  
6) 336.1640(4)(a)(i) - Reference should be made to the method(s) for calculating the actual  
sample size then corrected to 3% oxygen.  
7) 336.1640(4)(b)(ii)(A)(B) These sentences are contradictory. A control device is  
considered a process unless otherwise defined. This separation and distinguishment is not  
specifically defined.  
8) 336.1640(4)(b)(ii)(D) - How often should the inspections be conducted?  
9) 336.1640(4)(c) - This section should be removed because floating roofs are not designed  
or utilized in upstream production.  
10) 336.1640(5)(a) - What are initial performance and compliance testing requirements?  
Where are they stated? In OOOO and OOOOa, no performance or compliance testing is  
necessary when meeting standards under 40CFR Part 60 60.18(b).  
11) 336.1640(5)(b)(ii) What type of inspection? OOOO(a) requires monthly Method 22  
inspections consisting of flare observations lasting 15 minutes.  
12) 336.1640(5)(c) - Note: The following comment was submitted in the June 16, 2022 letter,  
but never answered or addressed in the latest draft of the rules. “This is completed during  
initial facility design to handle maximum throughput, pressure and volumes. As a  
reminder, each oil and gas well is a depleting asset with initial production rates dropping  
quickly within the first year of production. There is not an option to “open up the tap” to  
produce more hydrocarbons. Does the analysis for existing facilities that have been in  
operation for more than 10-20 years now have to validate the original design parameters  
even though production has declined by as much as 90%?”  
13) 336.1640(5)(d) - What inspection? OOOO(a) requires monthly AVO (Auditory, Visual  
and Olfactory) inspections separated by 14 days for closed vent systems. Or is EGLE  
suggesting a “once-only” annual visual inspection?  
14) 336.1640(6)(a) - How often? Just initial or annual? Needs more definition. Has EGLE  
done a cost benefit analysis for any of this work?  
Rule 336.1641 - Emission of volatile organic compounds from existing pneumatic  
controllers in the oil and natural gas industry located in the 2015 ozone nonattainment  
areas.  
1) 336.1641(2)(a)(b) These subparts are unclear and do not address exemptions. The  
federal standard under Subpart OOOO and OOOOa stipulates bleed rates greater than 6  
standard cubic feet per hour. This should be explicitly stated.  
2) 336.1641(6)(a)(b) Low Bleed Pneumatic Devices are less than 6 scfh as described by  
the manufacturers’ specifications. For clarity, Intermittent Bleed Devices are not  
continuous bleed thus not subject to these rules as proposed? These devices also bleed  
less than 6 scfh as specified by the manufacturers. High bleed pneumatic devices have  
been removed from operation and they are not available from equipment supply vendors  
following implementation of Subpart OOOO in 2012.  
Rule 336.1642 Emissions of volatile organic compounds from existing pneumatic pumps  
in the oil and natural gas industry located in the 2015 ozone nonattainment areas.  
1) 336.1642(1)(a) – Delete the following: “of for freeze protection glycol circulation.The  
energy to activate a pneumatic pump for glycol dehydration comes from high pressure  
rich glycol discharged from the dehydration tower. There will be most likely electricity  
available to operate these pumps because of close approximation to residential utilities in  
nonattainment counties.  
2) 336.1642(2)(b) – MOGA could not find a stated definition of “well site” in the proposed  
Part 6 regulations or Part 1, General Provisions. Please define the term “well site”.  
3) 336.1642(3)(i) & (ii) – MOGA has advocated to the EPA for the allowance of an “in-  
house” engineer with technical expertise and experience to certify closed-loop system  
and technical infeasibility. To avoid conflicting regulations between the State of  
Michigan and Federal regulations, MOGA recommends the Federal allowance of an “in-  
house” engineer as stated in 40 CFR 60.5393a.  
4) 336.1642(5)(b) Stack testing a pneumatic pump is impractical and very costly.  
Pneumatic pumps have a fixed canister size to facilitate the operation of the pump. This  
would be specified in the manufacturer’s specifications sheet. Initial compliance and  
testing using the injection rate (actuations per minute) multiplied by the fixed cannister  
size or using a calibrated bag sampler. This would be more practical and cost effective.  
5) 336.1642(5)(c)(ii) What type of inspection? AVO? For many wells and facilities, AVO  
inspection to ensure proper operation and to reduce leaks is already taking place per  
Subpart OOOO and Subpart OOOOa regulations.  
6) 336.1642(6)(a) A stack test is costly and impracticable. If routed to a combustion  
device meeting 40CFR Part 60 60.18(b), OOOO(a) does not require testing. Stack tests  
range from $10K - $15K and are usually completed on compressors greater than 1,300  
horsepower. Any kind of elaborate testing equipment to capture a low volume sample and  
accurately report the level of emissions becomes nearly impossible. A technique that  
merits sampling such small samples would use a calibrated sample bag or engineering  
calculations.  
7) 336.1642(6)(d) Like other proposed regulations in R 336.1640 through R 336.1644,  
MOGA recommends changing submission of initial reporting to “made available upon  
request by department”. This would follow the trend for other emission sources and  
reduce the burden on small producers with limited staff.  
Rule 336.1643 Emissions of volatile organic compounds from existing compressors in the  
oil and natural gas industry located in the 2015 ozone nonattainment areas.  
1) 336.1643(1) thru (6) – MOGA has discussed the definition of “wet seal” and “wet seal  
fluid degassing system” with compressor vendors and service firms in the State of  
Michigan. Vendors and service personnel were not aware of this type of centrifugal  
compressor located within the State of Michigan.  
2) 336.1643(4)(b)(iii) – a “continuous parameter monitoring system” would be very costly  
to install and operate for both new and marginal wells and facilities. MOGA would like  
clarification whether a flare with an auto ignition and/or a continuous burning pilot  
qualify as a “continuous parameter monitoring system”?  
3) 336.1643(5)(a) & (b) MOGA spoke with compressor vendors and service company  
representatives regarding replacing rod packing every 36 months. The vendors and  
service company representatives indicated that rod packing is inspected during every  
inspection, oil change and service. Representatives indicated that rod packing venting is  
monitored very closely as an indicator for service since bad rod packing would result in  
costly consumption of lubricating oil and possible engine failure. Representatives  
explicitly stated a 36-month replacement is not practical as rod packing typically lasts  
longer than 36 months. Representatives indicated this would be very costly for small  
businesses and wasteful of resources since a rod packing replacement typical take 2-3  
days of work with 6 technician charging $100 to $150 dollars per hour. This would be an  
unnecessary cost considering R336.1643(b) also requires rod packing venting to be  
routed to a process. MOGA recommends making this an either/or statement. Either  
change the rod packing every 36 months or route rod packing emissions to a process.  
Rule 336.1644 Emissions of volatile organic compounds from existing compressors in the  
oil and natural gas industry located in the 2015 ozone nonattainment areas.  
1) 336.1644(1)(b)(ii) This request is not an upstream function but is handled by mid-  
stream operations.  
2) 336.1644(4) This program should not be developed if the facility and/or the well(s) are  
at marginal status, which would be 15 boe/day or less per well.  
3) 336.1644(4)(a)(i&ii) This is very expensive to complete. This would potentially be  
around $2,600 to check a single leak. AVO or a soap bubble test is acceptable for these  
evaluations. Has EGLE provided any financial cost benefits analyses to validate the  
testing suggested? OOOO(a) allows for leak repair verification using AVO or by  
implementing soap and water under Method 21, Section 8.3.3.  
4) 336.1644(4)(b) - “Booster stations in the production segment” do not exist. This  
statement needs to be removed.  
5) 336.1644(4)(b)(ii) replace with the following statement; “Each fugitive emission  
component repair or replacement equipment will be resurveyed to ensure there is no leak  
after the repair or replacement by the use of 40 CFR, part 60, Appendix A, Method 21 at  
the earliest convenience possible or 30 days after the repair.  
6) 336.1644(4)(c) The department should either simplify this statement by removing “with  
a repair threshold of 500 ppm” or further clarify to include all resurveying options listed  
under Method 21, including alternatives.  
7) 336.1644(5)(a)(i&ii&iii) MOGA proposes additional discussion with EGLE staff to  
justify the merits of the frequency, the impact and the reporting if there are no fugitive  
emission components.  
Conclusion:  
MOGA would like to meet with EGLE-AQD after their review of suggested rule changes to  
discuss manpower implementation and cost benefit analysis. Some proposed Part 6 regulations  
could impair the field operations of many small business producers leading to increased costs  
above the sustainability threshold for existing wells. As mentioned in the opening paragraphs,  
over regulation without justification could result in the early plugging and abandonment of  
producing wells resulting in waste, loss of revenue, increased energy costs, impacts to rural and  
underserved communities and disproportionate impacts to small businesses.  
MOGA would also like to further discuss how the 2015 ozone nonattainment review data can be  
misleading and not relevant to emissions in 2023. There are nearly 8 years between gathering  
county information and the current review of the contribution the producing wells have in each  
county. A similar type of review in the attainment areas has shown the producing industry has  
made major efforts to reduce VOC & ozone impacts. That same reduction has likely occurred in  
the nonattainment counties also. MOGA would like to review data generated under the “further  
analysis” tenant required in EGLE’s January 2020 “Reasonable Available Control Technology  
Analysis for Volatile Organic Compoundsto assist EGLE staff in reducing unnecessary impacts  
to small businesses through “negative declarations” on source categories without substantial  
impacts to the NAA.  
MOGA looks forward to our continued collaborative relationship with EGLE staff to ensure  
proposed regulations are practical, functional and allow small businesses to complete within the  
oil and natural gas market. Working together is an effort in cooperation and should make  
understanding the industry better for the regulators, while helping producers better  
communication with regulators to minimize confusion and streamline implementation of  
proposed regulations.  
Thank you for your time.  
Sincerely,  
Jason Geer  
President & CEO  
Michigan Oil and Gas Association  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Cc:  
Subject:  
Attachments:  
Caroline Liethen <  
@mimfg.org>  
Wednesday, October 26, 2022 4:49 PM  
McDonald, Tracey (EGLE); Vaerten, Marissa (EGLE)  
Kownacki, Alec (EGLE); Lillian Woolley; Eleanor Surtman  
MMA Part 6 Rule Comment  
cl_air_voc-ract-letter-signed_221026.pdf  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Good afternoon,  
I am writing on behalf of MMA to submit the attached comments regarding proposed changes to the Part 6: Emissions  
Limitations and Prohibitions – Existing Sources of VOC Emissions draft rule set.  
I appreciate your consideration of our comments. Please contact me if you have questions.  
Sincerely,  
Caroline  
Caroline Liethen | Director of Environmental and Regulatory Policy | Michigan Manufacturers Association  
620 S. Capitol Ave Lansing Michigan 48933  
Tel: 517.487.8543 | Fax: 517.853.3343 | Email:  
@mimfg.org  
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1
October 26, 2022  
Mr. Trace McDonald  
Michigan Department of Environment, Great Lakes, and Energy Air Quality Division  
5225 West Allegan Street  
Lansing, MI 48909  
RE: MMA Comments on the VOC RACT Rules Dated September 7, 2022  
Dear Mr. McDonald:  
I am writing on behalf of the Michigan Manufacturers Association to provide comments on the  
draft Volatile Organic Compound (VOC) Reasonably Available Control Technology (RACT)  
Rules in Part 6. I appreciate your work on these rules and the consideration of member feedback.  
Your monthly attendance of our Air Policy Committee meetings provided a welcomed  
opportunity for dialogue and the comments herein largely reflect those discussions. We  
appreciate your and Marissa Vaerten’s efforts to write fair rules. However, we believe that the  
Department of Environment, Great Lakes, and Energy (EGLE) has devoted a very small amount  
of resources to developing RACT rules considering other prioritized programs that are not Clean  
Air Act requirements.  
Limited Time to Plan for Compliance. First, the time allotted for VOC RACT Rule  
development and implementation was insufficient. The Lake Michigan Air Directors Consortium  
(LADCO) “White Paper: NOx Emission Controls for Stationary Sources in the LADCO Region  
(February 2022)” referenced in our meetings suggests that additional time is needed for  
implementation of new rules, especially those that require add-on control equipment. In several  
sections of this document, it explains that facilities are typically given time to comply with new  
rules to allow for planning, analysis, and infrastructure changes. The timeline to comply with  
Maximum Achievable Control Technology (MACT) standards is typically three years, though in  
most cases between one and four years are allowed depending on work required to achieve  
compliance. In addition, the document also suggests that two years should be adopted to allow  
for emission reductions before 2026. Michigan’s rules will go into effect almost immediately  
once they are approved, leaving facilities with no option than to enter a consent agreement for an  
alternative schedule, if that is to be allowed. This would create an unnecessary burden on EGLE  
permitting and enforcement staff. The Ohio Rule (see Attachment 1) should be adopted allowing  
for additional time beyond the date of rule promulgation for sources having to do site-specific  
studies. Additional time is also allotted for facilities that need to install control equipment.  
Adopting a rule that includes additional time as outlined in the attachment will avoid the use of  
additional resources in permitting and enforcement that would be required if site-specific plans  
and permits are needed for each facility that needs additional time. It should be noted that these  
rules will likely go into compliance almost immediately after promulgation and EGLE has done  
620 South Capitol Avenue • Lansing, MI 48933 • Phone: 517-372-5900 mimfg.org  
Manufacturing Focused. Member Driven.  
no outreach, suggesting there are facilities that do not know these rules will soon be in effect and  
that they must comply immediately.  
The compliance schedule for the various stages of the RACT analysis required by Rule 602(4)  
should be lengthened as follows:  
The requirement to submit the VOC Potential to Emit (PTE) information to EGLE in  
Rule 602(4)(a) within one month of promulgation should be increased to at least three  
months  
The requirement to provide a RACT analysis for each VOC source to EGLE in Rule  
602(4)(b) within three months of promulgation should be increased to at least 12 months  
o The Ohio EPA 3745-21-11 VOC RACT regulations allow 12 months to submit a  
RACT study.  
The requirement to implement each RACT proposal within six months of department  
approval should be increased to at least two years and to at least three years if add-on  
controls are required.  
The 15 pound per calendar day exemption criteria found in Rule 610a(3)(a)(iii) should be  
changed from a daily limit to a monthly limit or a twelve-month rolling average limit.  
The VOC testing requirements in Rule 610a(4)(e)(vii) should allow for alternate test  
methods to be used, especially previously approved alternate test methods, if a different  
or modified method would more accurately represent equipment operating conditions.  
Rule 602 should include an exemption from these RACT requirements for any VOC  
source that has been subject to a Rule 702 VOC Best Available Control Technology  
(BACT) analysis, PSD BACT analysis, or Nonattainment NSR VOC LAER analysis  
within the past ten years.  
Adding to our request for additional time to implement control strategies, the country continues  
to recover from the pandemic and supply chain issues. Pollution control equipment and  
electronic components needed to run it are in short supply and come with extensive delivery  
delays, some as much as 12 to 18 months. The immediate implementation and retroactive nature  
of the requirements are not reasonable and will be overly burdensome, placing currently  
compliant industrial sources into non-compliance status.  
Changes to RACT Criteria. Many of the Control Technology Guideline (CTG) documents  
developed by the U.S. EPA for use in establishing RACT rules include references to Michigan’s  
early VOC rules. Therefore, it is confusing to affected sources that the criteria for inclusion in  
Rules 610a, 621a, 632a and 633 is now 15 pounds per day instead of 2.7 tons per 12 month  
rolling time period. These rules are based on CTG documents that have not changed since the  
original Rules 610, 621 and 632 were established and when these rules were incorporated into  
the State Implementation Plan (SIP). While the U.S. EPA has suggested that these rules need to  
be updated, we cannot identify any quantifiable VOC emission reductions from changing these  
rules. It will only create an administrative burden for sources now having to review daily  
emissions instead of monthly emissions. The CTG document “Control Techniques Guidelines for  
Miscellaneous Metal and Plastic Parts Coatings” (CTG), is quite complimentary of Michigan’s  
Rule 632 and in several instances recognized its limits as representing VOC RACT. As such, it is  
unnecessary to update this rule to Rule 632a.  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
In addition, in the May 18, 2006 U.S. EPA document “RACT Qs and Qs,the U.S. EPA  
explained that states can rely on past EPA guidance like CTGs but would expect states to have  
considerable interaction with affected facilities who might have additional information available  
for review. This has not been the case in developing these rules. This document also suggests  
that states can rely on other Federal rules to show compliance with RACT requirements but must  
reference these rules in their SIPs. It also says that PTIs can be relied on as long as they are  
referenced in the SIP submittal. The Federal Surface Coating of Plastic Parts and Products:  
National Emission Standards for Hazardous Air Pollutants (NESHAP) and the Federal Surface  
Coating of Miscellaneous Metal Parts and Products: National Emission Standards for Hazardous  
Air Pollutants (NESHAP) are largely equivalent in these rules and if EGLE will not state this in  
the rule, affected sources should be allowed to petition to have them recognized in their Permits  
to Install/Renewable Operating Permit (PTI/ROP) and allowed to simply comply with the  
applicable NESHAP.  
Further, the rules are written such that existing sources in attainment areas will now retroactively  
be subject to existing Part 6 Rules, such as Rule 632, for coatings like adhesives that accepted de  
minimis air permit restrictions or general permit provisions necessary to manufacture parts. The  
immediate and retroactive nature of the rules is not in keeping with the Administrative  
Procedures Act, which would otherwise require the source to be “modified, constructed or  
reconstructed” as defined in the rules.  
Rule 602(3)(a) and (b). EGLE has proposed changes to the existing Rule 602 that now appear as  
Rule 602(3)(a) and (b) which eliminate the ability for EGLE to incorporate RACT derivatives  
during a permit to operate or Renewable Operating Permit. This language should be retained  
with the reference to permit to operate changed to Renewable Operating Permit. The ability to  
incorporate the revised RACT limits or requirements in the ROP program instead of the PTI  
program would allow flexibility to EGLE and could streamline the process. Currently changes to  
a PTI would take 240 days if the regulatory requirements are met, which is not always the case.  
Making changes through the ROP program would eliminate the load on the PTI engineers while  
streamlining the approval process as any changes need to be incorporated into ROPs anyway.  
Rule 633. Currently, the boating industry is trending away from pigmented gelcoat (colored  
fiberglass) and towards polyester automotive painting topcoats. This affords the use of compliant  
gelcoat formulations (for example white gelcoat) combined with robust outer coatings capable of  
withstanding marine and freshwater environments. This also improves serviceability and repair  
advantages associated with bumps and scratches. Product (boat) life expansion may be the result  
of this change away from colored gelcoats. The rules will force these manufacturers back into  
pigmented (form in color) gelcoat to avoid Rule 633 controls.  
Bottom paints, also known as ablative coatings, are specially formulated to prevent marine  
buildup on the undersides (running surfaces) of boats. These coatings and their formulations are  
not part of any CTG or NESHAP evaluation, and yet they would be lumped into the same  
compliance category as all other pleasure craft coatings for the marine industry. Simply stated,  
Rule 633 will cause manufacturers to stop the application of “bottom paints” in the  
manufacturing plants. Further, currently low volume exemptions for such coatings will no longer  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
be applicable, causing manufacturers to “transfer” the bottom coating application to dealer and  
distributor locations. Such transfers do not have a net environmental benefit and EGLE has not  
demonstrated that the cessation (or control) of these low volume, specialty extreme performance  
coatings will result in improvements in the non-attainment areas targeted by the rules. It should  
also be noted that there are only two sources in Michigan potentially subject to the fiberglass  
boat manufacturing rules. It is questionable to promulgate rules that would affect only two  
sources.  
Control Equipment Effectiveness. It should be noted that changes were made to control  
effectiveness requirements. For Rules 610a, 620, 621, 633 and 634, the overall control and  
capture efficiency has been updated to the language below:  
Collect and vent the emissions from equipment cleaning to a volatile organic compound  
emission control system that has an overall capture and control efficiency of not less than  
85%, by weight, for the volatile organic compound emissions. If such a reduction is  
achieved by incineration, not less than 90% of the organic carbon must be oxidized to  
carbon dioxide.  
When applying for a new permit, Michigan Rule 702(a) VOC BACT is often not as high as what  
is described above. We discussed this at one meeting, and it was our belief that this requirement  
is based on painting in a booth, which is not often the case. Typically, a spray booth with a non-  
fugitive enclosure or a PTE would get more than 90% control, and combined VOC BACT for  
spray booths is currently 95% control. As we briefly discussed, plants with flow coat lines and  
dip spin lines may have difficulty meeting 90% capture and control. This RACT requirement is  
more restrictive than BACT in many cases.  
Control equipment for VOC abatement largely or most commonly consists of oxidizing units.  
While oxidation to carbon dioxide is the target, the combustion process also produces nitrogen  
oxides (NOx, an ozone precursor) and incomplete products of combustion such as formaldehyde.  
These products are unfavorable, and the regulations would appear to replace one bad actor (or air  
pollutant) for another. We know of several companies whose thermal oxidizer is the largest  
contributor to their carbon footprint.  
Operations that are currently permitted to use solvent rags, etc., may use these wipe agents in the  
open manufacturing floor, which is not equipped with collection and ventilation systems that will  
be required as currently written. Neither this approach nor its impacts have been properly  
evaluated either for the practical or economic feasibility which should be a component of the rule  
impact and implementation process. Further and as noted above, even if such capture and control  
retrofit components can be practically implemented, the supply chain delays currently being  
experienced for equipment and electronic component delays have not been properly considered.  
Daily Emission Calculations. We are especially concerned over Rules 620a, 621a, 633a in  
which applicability is based on emissions in terms of pounds per day. These rules also require  
daily record keeping which is extremely burdensome to manufacturing facilities.  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
In our meetings we had suggested that the methodology described the U.S. EPA’s Protocol for  
Determining the Daily Volatile Organic Compound Emission Rate of Automobile and Light-Duty  
Truck Primer-Surfacer and Topcoat Operations be allowed to calculate daily emissions not only  
for Rule 610a but also for other rules that require daily record keeping. It allows daily emissions  
to be calculated as the following:  
The volume of each coating used each day can be calculated by prorating the volume of  
that coating used in a month to each day in the month. The prorating factor is the ratio of  
the total square footage coated with that coating on the day to the total square footage  
coated with that coating in the month.  
It appears that this methodology can be used for sources subject to Rule 610a. This or a similar  
methodology should be allowed for use in these other rules.  
In nearby states, it is common practice that the compliance requirement of pounds per hour can  
be based on and summarized monthly. This affords both the applicable requirement to be stated  
on a pounds of VOC per hour basis, while allowing the source to accumulate usage data and  
operational data on a monthly time period. This improves the quality of the data while reducing  
the data burden associated with short-term usage limitations. Similar to the RACT approach  
EGLE is proposing for the fiber-reinforced plastic industry, monthly data coupled with 12-month  
rolling sum compliance, provides useful and yet reasonable data collection, and processing with  
monthly compliance demonstrations.  
General Permit Changes. Rules 610a and 621a affect sources using the General Permit. It  
appears that these sources have not been notified of their need to obtain a new PTI. Permitting  
will take at least six months and if these rules go into effect in early 2022, these sources are  
already behind. Fishbeck has identified 38 sources using the General Permit (see Attachment 2)  
in southeast Michigan. The general permit is used to exempt coating lines from the content limits  
of Rules 621 and 632 by limiting each coating line to 2,000 lb/mo, 10 tons per year (tpy); and  
there is a combined coating line limit of 30 tpy. If all 38 facilities had at least three coating lines;  
the most VOC emissions that could be emitted would be 38 X 30 tpy VOC = 1,140 tons of VOC  
emissions. Of course, emissions from these 38 sources are likely much less, and some of these  
sources will have only one or two lines, and their limit would be 20 tpy not 30 tpy. The Michigan  
Air Emissions Reporting System data should be reviewed to see what these facilities actually  
emit.  
As the overall goal is to reduce VOC emissions; the General Permit should be amended rather  
than eliminated. For example, if you made the following changes use of General Permits would  
still be allowed with the following changes:  
If the source can meet already meet the annual three tpy proposed emissions, advise  
transition to this exemption (though no reductions will be achieved).  
If the source is meeting or is close to meeting the coating content limits on their lines,  
some adjustments could be made in switching some coatings, and limited to no  
reductions may be achieved. If these sources must go in for a site-specific permit, they  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
may also target an increase in emissions up to a point where controls are not cost  
effective.  
If a source must spend money to install controls to meet the new rules; most likely the  
source would go in for a permit to request as high of VOC limits as possible. As long as  
the source is meeting the 90% reduction, they would be compliant with the proposed  
rules. The source could then market and take on more work that they may not have been  
able to take before to meet current limits. For these sources, we would see an increase in  
emissions or at least PTE until they can obtain more work.  
o In addition, RTOs for these sources will require natural gas to keep the  
combustion chamber temperature at the level needed for control. This will add  
NOx emissions to the ozone nonattainment area.  
o Existing coatings require performance testing and approvals that can take years to  
complete. Shorter-term control approaches and long lead times for control  
equipment will conflict with immediate applicability and compliance requirement,  
which is unreasonable.  
If the target reduction is 15% controls, the General Permit should be amended to allow only 8.5  
tpy per line or a total of 25.5 tons VOCs for a General Permit holder. Keeping the exemption  
from RACT Rules for these General Permit sources but ratcheting down the limits to 8.5 tpy/  
line and a total of 25.5 tpy makes more sense.  
De Minimis Emission Levels: A de minimis emissions threshold should be included in Rule  
602(4) below which the RACT requirements do not apply. Otherwise, every RACT review will  
include many wasteful analyses for low emitting sources that will have no technically or  
economically feasible control options. Rule 602(4) should include categorical exemptions for  
types of equipment with inherently low VOC emissions such as natural gas fired equipment and  
other combustion sources.  
The compliance schedule for the various stages of the RACT analysis required by Rule  
602(4) should be lengthened as follows and as suggested in Attachment 1:  
o The requirement to submit the VOC PTE information to EGLE in Rule 602(4)(a)  
within one month of promulgation should be increased to at least three months  
o The requirement to provide a RACT analysis for each VOC source to EGLE in  
Rule 602(4)(b) within three months of promulgation should be increased to at  
least 12 months  
The Ohio EPA 3745-21-11 VOC RACT regulations allow 12 months to  
submit a RACT study.  
o The requirement to implement each RACT proposal within six months of  
department approval should be increased to at least two years and to at least three  
years if add-on controls are required.  
The 15 pound per calendar day exemption criteria found in Rule 610a(3)(a)(iii) should be  
changed from a daily limit to a monthly limit or a 12-month rolling average limit.  
The VOC testing requirements in Rule 610a(4)(e)(vii) should allow for alternate test  
methods to be used, especially previously approved alternate test methods, if a different  
or modified method would more accurately represent equipment operating conditions.  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
Rule 602 should include an exemption from these RACT requirements for any VOC  
source that has been subject to a Rule 702 VOC BACT analysis, PSD BACT analysis, or  
Nonattainment NSR VOC LAER analysis within the past 10 years.  
Thank you for your consideration of our comments and the extensive economic impact these  
rules would have on the largest sector of Michigan’s economy. MMA is aware of one  
representative example company that would incur a cost of at least $1 million for each piece of  
equipment required per site. An additional $100,000 per year would be necessary for operational  
costs including natural gas, which will only further increase in cost and emissions. This would  
reduce the profit/loss margin and force the company to consider relocating, and certainly  
establishing any future expansions, in other states. These regulatory changes have significant  
economic implications for Michigan, and we will continue to provide information to assist the  
department in its decision making.  
Sincerely,  
Caroline Liethen  
Director of Environmental and Regulatory Policy  
Attachments:  
620 South Capitol Avenue • Lansing, MI 48933-4247 • Phone: 517-372-5900 • www.mimfg.org  
Manufacturing Focused. Member Driven.  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
Kathryn R. Ross  
Wednesday, October 26, 2022 12:03 PM  
@cmsenergy.com>  
To:  
Cc:  
McDonald, Tracey (EGLE); Vaerten, Marissa (EGLE)  
Amy D. Kapuga; JAMES M. WALKER  
Subject:  
Attachments:  
Consumers Energy's Comments on Part 6 Rules - Proposed Revisions  
Part_6_VOC_RACT_ Proposed_Rule_CE_Comments Letter 10_26_2022 (final).pdf  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Consumers Energy Company (Consumers Energy) appreciates the opportunity to comment on the Michigan Department  
of Environment, Great Lakes, and Energy – Air Quality Division’s (AQD) Proposed Revisions to the Part 6 Volatile Organic  
Compound  
(VOC) rules. Please find our comments attached.  
Should you wish to discuss any of our comments, please feel free to contact Amy Kapuga or myself.  
Thanks,  
Kathryn Ross, Sr. Environmental Planner  
1945 W. Parnall Rd. | Jackson, MI 49201 | P22-231  
Office: 517-788-0648| Fax: 517-788-1064 |  
www.ConsumersEnergy.com  
@cmsenergy.com  
1
October 26, 2022  
Attn: Mr. Trace McDonald, Ms. Marissa Vaerten  
Michigan Department of Environment, Great Lakes, and Energy  
Air Quality Division, SIP Development Unit  
P.O. Box 30260  
Lansing, MI 48909-7760  
RE: Consumers Energy Company’s Comments on EGLE – AQD’s Proposed Revisions to  
the Part 6. Emission Limitations and Prohibitions – Existing Sources of Volatile Organic  
Compound Emissions Rules (Rule Set 2022-18 EQ)  
Consumers Energy Company (Consumers Energy) appreciates the opportunity to  
comment on the Michigan Department of Environment, Great Lakes, and Energy – Air  
Quality Division’s (AQD) Proposed Revisions to the Part 6 Volatile Organic Compound  
(VOC) rules, as posted on the Department of Licensing and Regulatory Affairs’  
Administrative Rulemaking System under the Request For Rulemaking 2022-18 EQ.  
Consumers Energy, Michigan's largest utility, provides electric and natural gas service to  
more than 6 million of the state's 10 million residents in all 68 counties in the Lower  
Peninsula. We provide natural gas service for heating and other uses to more than 1.7  
million customers. Natural gas sources used by Consumers Energy include major pipeline  
companies and producers in Michigan, Gulf Coast states and Canada. As a local  
distribution company (LDC), we distribute natural gas using compressor stations and  
thousands of miles of intrastate pipeline. Fifteen underground natural gas storage fields  
in Michigan allow our Company to economically purchase and store gas during warm  
months, for eventual use in the winter heating season.  
Consumers Energy understands that AQD has proposed these regulatory revisions in  
connection with the federal Clean Air Act (CAA) requirements for the 2015 Ozone  
National Ambient Air Quality Standards (NAAQS) non-attainment areas. The proposed  
Part 6 rules are one component of the State’s strategy to develop and submit a State  
Implementation Plan (SIP) to the U.S. Environmental Protection Agency (EPA). These  
proposed rules are to address VOC emission reductions via Reasonably Achievable  
Control Technologies (RACT). Consumers Energy also plans to review and comment on  
Consumers Energy  
1945 W. Parnall Road  
Jackson, MI 49201  
Environmental Quality & Sustainability  
www.consumersenergy.com  
the anticipated Part 8 NOx RACT proposed rules, which are the complimentary  
component of the SIP rules process, during the public comment period.  
Consumers Energy currently operates one natural gas compressor station in an area  
designated by the EPA as moderate non-attainment for the 2015 Ozone NAAQS.  
Consumers Energy also operates four (4) other compressor stations within the seven-  
county Southeast Michigan area which is currently designated as a marginal non-  
attainment area for the 2015 Ozone NAAQS, however this area is awaiting a  
redesignation determination from the EPA and could either be bumped up to moderate  
non-attainment for the 2015 Ozone NAAQS or determined to be in attainment with the  
2015 Ozone NAAQS.  
Consumers Energy strives to be compliant with all federal and state environmental  
regulations. In the development of these newly proposed rules, Consumers Energy  
requests EGLE-AQD to align the proposed regulatory definitions with other existing federal  
program definitions. This provides clarity to industry in understanding the applicability of  
similar, yet separate, regulations. This also aligns the efforts and minimizes impacts (both  
cost and schedule) to industries that must undertake equipment retrofits, replacements  
and/or operational changes to ensure compliance with all regulations. As such,  
Consumers Energy requests that the specific language for the following three definitions  
be incorporated into the proposed Part 6 rules (within R 336.1601, as appropriate), and  
provides cite to the federal regulations for reference:  
Local Distribution Company custody transfer station means a metering station where a  
Local Distribution Company (LDC) receives a natural gas supply from an upstream  
supplier, which may be an interstate transmission pipeline or a local natural gas  
producer, for delivery to customers through the LDC's intrastate transmission or  
distribution lines. (40 CFR Part 60, Subparts OOOO and OOOOa)  
Natural gas distribution means the collection of all distribution pipelines and metering-  
regulating stations that are operated by a Local Distribution Company (LDC) within a  
single state that is regulated as a separate operating company by a public utility  
commission or that are operated as an independent municipally-owned distribution  
system. (40 CFR Part 98, Subpart W)  
Natural gas transmission and storage segment means the transport or storage of natural  
gas prior to delivery to a “local distribution company custody transfer station” or to a  
final end user (if there is no local distribution company custody transfer station). For the  
purposes of this subpart, natural gas enters the natural gas transmission and storage  
segment after the natural gas processing plant, when present. (40 CFR Part 60, Subparts  
OOOO and OOOOa)  
2
Additionally, Consumers Energy urges EGLE-AQD to allow more time under the proposed  
provisions of R336.1602. Specifically, the timeframes identified in subparagraphs (4)(b)  
and (4)(b)(vi) should be extended to allow industry adequate time to develop a proposal  
for compliance as well as implement the plan. The RACT analysis required under  
subparagraphs 602(4)(b)(v) and (c) require not only a technical feasibility of the  
available control options but also economic impacts amongst other items. Given that  
industry may not even be aware that they are subject to these proposed rules, due to  
the uncertainty of the Southeast Michigan redesignation request, or for other reasons, or  
may have multiple emission sources that it has to evaluate, these timeframes are too  
restrictive to be able to provide all the necessary information required by the proposed  
rule. Should industry be required to retrofit equipment, securing this information and  
vetting the changes within the business can take substantially longer than the proposed  
3 months.  
We would suggest that the timeframe for provision (4)(b) be extended to 6 months after  
the final promulgation of the rule. In addition, we request that the language for (4)(b)(vi)  
be revised to allow for department approval of the timeframe in the RACT proposal.  
Please find attached a mark-up version (applicable pages only) showing our comments  
on for the proposed Part 6 regulations.  
Consumers Energy thanks you for your time and consideration of our request. Should you  
have any questions or concerns, please do not hesitate to contact Amy Kapuga  
Respectfully Submitted,  
Kathryn (Kate) Ross  
Sr. Environmental Analyst  
Consumers Energy Company  
1945 West Parnall Road, P22-330  
Jackson, MI 49201  
@cmsenergy.com  
3
Attachment 1  
Consumers Energy’s Mark-up Version of the Part 6 Rules  
Applicable Pages only  
Changes shown in green italic and red strike-through  
R 336.1601 Definitions (pages 3 & 4)  
R 336.1602 Existing sources of volatile organic compound emissions generally (page 7)  
Consumers Energy  
1945 W. Parnall Road  
Jackson, MI 49201  
Environmental Quality & Sustainability  
www.consumersenergy.com  
which an application for a permit to install, pursuant to the provisions of part 2 of these  
rules, was made to the department before July 1, 1987.  
(vi) Any process or process equipment which is subject to the provisions of R 336.1632  
and which either has been placed into operation before the effective date of R 336.1632  
or for which an application for a permit to install, pursuant to the provisions of part 2 of  
these rules, was made to the department before the effective date of R 336.1632.  
(vii) Any process or process equipment which is not subject to the provisions of any rule  
in this part and which either has been placed into operation before July 1, 1979, or for  
which an application for a permit to install, pursuant to the provisions of part 2 of these  
rules, was made to the department before July 1, 1979. The term does not include a  
process or process equipment operated for research, development, or pilot studies, if the  
operation is not for the purpose of producing saleable products or goods.  
(d) “Heavier vehicles” means a self-propelled vehicle designed for transporting  
persons or property on a street or highway that has a gross vehicle weight rating  
over 8,500 pounds.  
(e) “Local Distribution Company custody transfer station” means a metering station  
where a Local Distribution Company (LDC) receives a natural gas supply from an  
upstream supplier, which may be an interstate transmission pipeline or a local natural  
gas producer, for delivery to customers through the LDC’s intrastate transmission or  
distribution lines.  
(ef) “Natural gas distribution” means the collection of all distribution pipelines and  
metering-regulating stations that are operated by a Local Distribution Company (LDC)  
within a single state that is regulated as a separate operating company by a public  
utility commission or that are operated as an independent municipally-owned  
distribution system.activities in which the natural gas is provided for the end user by  
a distribution facility after that facility receives the natural gas from the natural gas  
transmission and storage segment.  
Commented [KRR1]: Reitemize definitions following the  
addition of LDC.  
(fg) “Natural gas processing” means the process of separating and recovering  
certain hydrocarbons and fluids from the raw gas to produce pipeline quality  
natural gas and natural gas products.  
(gh) Natural gas processing plant” means any processing site engaged in the  
extraction of natural gas liquids from field gas, fractionation of mixed natural gas  
liquids to natural gas products or both. Natural gas processing plant does not  
include a Joule-Thompson valve, a dew point depression valve, or an isolated or  
standalone Joule-Thompson skid.  
(hi) “Natural gas transmission and storage” means the transport or storage of  
natural gas prior to delivery to a Local Distribution Company custody transfer station  
or to a final end user (if there is no Local Distribution Company custody transfer  
station). For the purposes of this subpart, natural gas enters the natural gas  
transmission and storage segment after the natural gas processing plant, when  
present., excluding processing, sometimes long distances, and the temporary storage  
of that gas. Specific equipment used in natural gas transmission includes the land,  
mains, valves, meters, boosters, regulators, storage vessels, dehydrators,  
compressors, and their driving units and appurtenances, and equipment used for  
transporting gas from a production facility, delivery point of purchased gas,  
Commented [ADK2R1]: Natural gas transmission and  
storage  
segment means the transport or storage  
of natural gas prior to delivery to a  
‘‘local distribution company custody  
transfer station’’ (as defined in this  
section) or to a final end user (if there  
is no local distribution company  
custody transfer station). For the  
purposes of this subpart, natural gas  
enters the natural gas transmission and  
storage segment after the natural gas  
processing plant, when present. If no  
natural gas processing plant is present,  
natural gas enters the natural gas  
transmission and storage segment after  
the point of ‘‘custody transfer’’ (as  
defined in this section). A compressor  
station that transports natural gas prior  
to the point of ‘‘custody transfer’’ or to  
a natural gas processing plant (if  
present) is not considered a part of the  
natural gas transmission and storage  
segment  
3
gathering system, storage area, or other wholesale source of gas to 1 or more  
distribution areas.  
(ij) “Oil and natural gas industry” means the operations involved in the extraction  
and production of crude oil and natural gas, as well as the processing, transmission,  
storage, and distribution of natural gas. For the purposes of the rules in this part, oil  
and natural gas industry operations will be referred to in the following 4 segments:  
(i) Oil and natural gas production.  
(ii) Natural gas processing.  
(iii) Natural gas transmission and storage.  
(iv) Natural gas distribution.  
(jk) “Oil and natural gas production” means operations including the wells and all  
related processes used in the extraction, production, recovery, lifting, stabilization,  
and separation or treating of oil or natural gas, or both, including condensate.  
(kl) "Person responsible" means a person that owns, leases, controls, operates, or  
supervises a source of air contaminants.  
(lbm) “Western portion of Allegan County” means the areas in Allegan County  
described as Casco Township, Cheshire Township, city of Douglas, city of Holland,  
city of Saugatuck, Clyde Township, Fillmore Township, Ganges Township, Heath  
Township, Laketown Township, Lee Township, Manlius Township, Overisel  
Township, Saugatuck Township, and Valley Township. "Person responsible" means a  
person who owns, leases, controls, operates, or supervises  
a source of air contaminants.  
(mn) “Western portion of Muskegon County” means the areas located in  
Muskegon County described as Blue Lake Township, city of Montague, city of  
Muskegon, city of Muskegon Heights, city of North Muskegon, city of Roosevelt  
Park, city of Whitehall, Dalton Township, including the village of Lakewood Club,  
Fruitland Township, Fruitport Township, including the village of Fruitport,  
Laketon Township, Montague Township, Muskegon Township, city of Norton  
Shores, White River Township, and Whitehall Township.  
R 336.1602 Existing sources of volatile organic compound emissions generally.  
Rule 602. (1) A person shall not cause or allow the emission of volatile organic  
compounds from any existing source in excess of the provisions of any rule of this part or  
the maximum allowable emission rate specified in any of the following, whichever  
results in the lowest maximum allowable emission rate:  
(a) A permit to install.  
(b) A permit to operate.  
(bc) A renewable operating permit issued under R 336.1210.  
(cd) A voluntary agreement.  
(de) A performance contract.  
(ef) A stipulation.  
(fg) An order of the department.  
(2) Department approvals for the equivalent emission rates, alternate emission rates, or  
compliance methods that are authorized pursuant to any of the provisions listed in  
subdivision (a) of this subrule must comply shall be in compliance with all of the  
following provisions:  
4
subdivision (a) of this subrule shall be in compliance with both of the following  
provisions:  
(ai) The department approval shall becomes part of a legally enforceable order of the  
department, or permit to install, or permit to operate.  
(bii) A copy of the legally enforceable document that is identified in paragraph (i) of  
this subdivision (a) of this subrule shall is sent to the United States Environmental  
Protection Agency.  
(4) In R 336.1610, R 336.1621, and R 336.1632, where emission limits are expressed in  
pounds of volatile organic compounds per gallon of coating, minus water, as applied, the  
phrase "minus water" shall also include compounds which are used as organic solvents  
and which are excluded from the definition of volatile organic compound.  
(4) A person responsible for a facility with allowed or potential volatile organic  
compound emissions equal or greater than 100 tons per year in the 2015 ozone  
nonattainment area for which no reasonably available control technology (RACT)  
requirement has been established in R 336.1604 to R336.1644, shall meet all of the  
following requirements:  
(a) Provide the department and United States Environmental Protection Agency  
with the following information within 1 month after final promulgation of this rule  
revision:  
(i) Identification of each facility, including individual emission sources, to which  
this rule applies.  
(ii) Determination of the total potential to emit and the actual emissions of volatile  
organic compounds for the most recent calendar year from each source at the  
facility using emission testing, mass balance, or a calculation method acceptable by  
the department.  
(b) Within 34 months after final promulgation of this rule revision, provide to the  
department and United States Environmental Protection Agency, a proposal for  
RACT for each source of volatile organic compounds at the facility. The RACT  
proposal must include, at a minimum, the following information:  
(i) A list of each source subject to the RACT requirements.  
(ii) The size or capacity of each affected source and the types and quantities of  
materials processed or produced in each source.  
(iii) A physical description of each source and its operating characteristics.  
(iv) Estimates of the potential and actual volatile organic compound emissions  
from each affected source and associated supporting documentation.  
(v) A RACT analysis which meets the requirements of subdivision (c) of this  
subrule, including technical and economic support documentation for each affected  
source.  
(vi) A schedule for completing implementation of the RACT proposal as  
expeditiously as practicable but not later than 6 months after department approval  
of the proposal, including interim dates for the issuance of purchase orders, start  
and completion of process, technology and control technology changes, and the  
completion of compliance testing. The schedule will be subject to Department  
approval.  
7
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
McDonald, Tracey (EGLE)  
Wednesday, October 26, 2022 11:54 AM  
Vaerten, Marissa (EGLE)  
Subject:  
Attachments:  
FW: Comments to Rule Set 2022-18 EQ  
Comments to R. Set 2022-18(27343345.3).pdf  
Categories:  
2022-018EQ COMMENTS  
FYI  
From: Cumings, Troy <  
@wnj.com>  
Sent: Wednesday, October 26, 2022 11:52 AM  
To: McDonald, Tracey (EGLE) <MCDONALDT@michigan.gov>  
Subject: Comments to Rule Set 2022-18 EQ  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Trace,  
Attached are comments to Rule Set 2022-18 EQ submitted on behalf of Willert Home Products, Inc. I look forward to  
working with you on finalizing the rule set. Thanks.  
Troy M. Cumings | Partner  
Warner Norcross + Judd LLP  
One Michigan Avenue Building, 120 North Washington Square, Suite 410, Lansing, MI 48933  
d 517.679.7411 |  
@wnj.com | profile | V-Card  
This email and any attachments are solely for the confidential use of the intended recipient. If you are not the intended recipient, please do not  
read, distribute or act in reliance on it or any attachments. If you received this email by mistake, please notify us immediately by email, and  
promptly delete this email and any attachments.  
The attorney-client and work product privileges are not waived by the transmission of this email.  
1
October 26, 2022  
Via Email  
Mr. Trace McDonald  
EGLE  
Air Quality Division  
525 West Allegan Street  
Lansing, Michigan 48933  
Re:  
Dear Mr. McDonald:  
We represent Willert Home Products, Inc. On behalf of Willert, I submit the following  
Comments to Rule Set 2022-18 EQ Rule 660  
comments to Rule Set 2022-18 EQ. My comments relate to the proposed amendments to Rule  
660, which adopt by reference certain versions of the OTC Model Rule for Consumer Products.  
My comments focus specifically on the regulation of para-dichlorobenzene (“PDCB”) in air  
fresheners and toilet/urinal care products.  
Proposed Rule 660 attempts to exempt products containing 98% PDCB. As drafted,  
however, the proposed changes to Rule 660 would not fully exempt those products. As explained  
in more detail below, there are three issues with the current draft language. First, the draft rule  
applies the exemption only to one version of the OTC Consumer Product Rules that Rule 660  
adopts. Second, the draft rule exempts only certain PDCB-containing “solid toilet/urinal care”  
productsit does not exempt air fresheners that contain PDCB. Finally, both versions of the OTC  
Consumer Product Rule that Rule 660 adopts contain a freestanding prohibition for PDCB-  
containing products, which the current draft rule does not account for.  
1. The exemption applies to only one version of the OTC Consumer Products Rules and  
therefore will not be effective until April 30, 2023.  
The draft Rule 600 incorporates two separate versions of the OTC Model Rule for  
Consumer Products: The 2006 version (referred to in the draft rule as “ver2006”) and the 2012  
version (referred to in the draft rule as “ver2012”). The draft Rule 660 incorporates ver2006 before  
January 1, 2023; it incorporates ver2012 after April 30, 2023. This would create a roughly four-  
month gap where neither ver2006 nor ver2012 applies. In section (2)(f), the draft Rule 660  
contains the following exemption for products containing not less than 98% PDCB:  
Troy M. Cumings | Partner  
D 616.752.2731  
E
@wnj.com  
150 Ottawa Avenue, N.W., Suite 1500  
Grand Rapids, MI 49503  
Mr. Trace McDonald  
October 26, 2022  
Page 2  
In ver2012, the volatile organic compound limit in section (3) table of standards for  
solid toilet/urinal care as it applies to products containing not less than 98% para-  
dichlorobenzene.  
Because this language exempts toilet/urinal care products containing not less than 98%  
PDCB only from ver2012, the exemption would not apply until after April 30, 2023. An effective  
exemption must apply to both ver2006 and ver2012.  
2. The exemption exempts only “solid toilet/urinal care” products, leaving the  
prohibition on solid air fresheners containing not less than 98% PDCB in place.  
Both ver2006 and ver2012 of the OTC Consumer Products Rules regulate toilet/urinal care  
products and solid air fresheners containing PDCB. However, the exemption found in section  
(2)(f) of the draft Rule 660 refers only to toilet/urinal care products. The omission of “solid air  
fresheners” from that section means the manufacture and sale of those products would be  
prohibited in Michigan. The logic behind the exemption of toilet/urinal care products containing  
not less than 98% PDCB, however, applies with equal force to solid air fresheners containing not  
less than 98% PDCB. Indeed, since ver2006 was released, EPA has determined that PDCB is “not  
likely to be carcinogenic to humans.”1 Accordingly, solid air fresheners should be included in  
section (2)(f).  
3. The exemption in draft Rule 660 does not account for a freestanding prohibition on  
PDCB-containing products found in the OTC Consumer Product Rules.  
Both ver2006 and ver2012 of the OTC Consumer Product Rules regulate PDCB-containing  
solid air fresheners and toilet/urinal care products through the section 3 table of standards.  
However, both ver2006 and ver2012 contain a separate, freestanding prohibition on PDCB-  
containing products in section (3)(n): Requirements for Solid Air Fresheners and Toilet/Urinal  
Care Products. That section prohibits outright the sale, supply, offer for sale, or manufacture of  
any solid air fresheners or toilet/urinal care products that contain PDCB. Section (3)(n) is noted  
as an optional provision, which each state should decide whether to incorporate on a case-by-case  
basis.2 As written, Michigan’s incorporation of ver2006 and ver2012 is silent as to whether that  
provision is incorporated.  
Unless the final Rule 660 expressly disclaims the adoption or application of the  
freestanding prohibition on PDCB-containing solid air fresheners and toilet/urinal care products  
1 Revised Reregistration Eligibility Decision (RED) Para-dichlorobenzene, EPA 738-R-07-010; U.S. Environmental  
Protection Agency, Office of Prevention, Pesticides, and Toxic Substances, Office of Pesticide Programs, U.S.  
Government Printing Office: Washington, DC, 2008.  
2 The ver2012 rules explain that provisions noted with a double asterisk, as section (3)(n) is, are left “up to each state  
to decide whether it wishes to include regulation of said compounds in its state-specific rulemaking. OTC takes no  
position on whether to include these compounds in such a rulemaking.” (Ver2012, at 1.) The same note is made in  
the ver2006 rules (Ver2006, at 1.)  
Mr. Trace McDonald  
October 26, 2022  
Page 3  
found in section 3(n) of ver2006 and ver2012, the existing exemption found in section (2)(f) of the  
draft rule will be ineffective.  
4. All of these issues can be resolved by minor changes to sections (1)(b) and (2)(f) of the  
draft Rule 660.  
The three issues I note above can be resolved with minor changes to sections (1)(b) and  
(2)(f) of the draft Rule 660. I propose the following changes to the current draft Rule 660 language:  
(1) Except as provided in subrule (2) of this rule, the following provisions are adopted by  
reference in R 336.1902:  
. . .  
(b) After December 31, 2022 April 30, 2023, the ozone transport commission’s “OTC  
Model Rule for Consumer Products, “ Dated May 10, 2012, (ver2012).  
. . .  
(2) In ver2006 and ver2012, as they apply to products containing not less than 98%  
para-dichlorobenzene, the volatile organic compound limit in section (3) table of  
standards for air fresheners and solid toilet/urinal care, and the prohibitions in  
Section 3(n) requirements for solid air fresheners and toilet/urinal care products,  
as it applies to products containing not less than 98% para-dichlorobenzene.  
Please do not hesitate to reach out to me with any questions you have.  
Very truly yours,  
Troy M. Cumings  
27343345-3  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
McDonald, Tracey (EGLE)  
Wednesday, October 26, 2022 2:30 PM  
Vaerten, Marissa (EGLE)  
Subject:  
Attachments:  
FW: Public Comments EGLE changes to R 336.1601-R 336.1662 & RACT  
Letter Public Comments EGLE 102622.pdf  
Categories:  
2022-018EQ COMMENTS  
From: Rita Loof <rml93@verizon.net>  
Sent: Wednesday, October 26, 2022 2:23 PM  
To: McDonald, Tracey (EGLE) <MCDONALDT@michigan.gov>  
Cc: Dolehanty, Mary Ann (EGLE) <DOLEHANTYM@michigan.gov>  
Subject: Public Comments EGLE changes to R 336.1601-R 336.1662 & RACT  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Dear Mr. McDonald, please see attached. Regards,  
Rita  
Rita M. Loof  
Director, Environmental Affairs  
RadTech International  
@radtech.org  
@verizon.net  
909-981-5974  
cell/text  
www.radtech.org  
1
October 26th, 2022  
Mr. Trace McDonald  
Department of Environment, Great Lakes and Energy  
Air Quality Division  
Re: Public Comments on the Michigan’s Department of Environment, Great Lakes and Energy  
(EGLE)Changes to R 336.1601 – R 336.1662 and “Reasonably Available Control  
Technologies” (RACT).  
Dear Mr. McDonald:  
RadTech International is the trade association for the Ultraviolet/ Electron Beam/Light Emitting  
Diode (UV/EB/LED) industry. The organization represents over 800 members nationwide  
involved in a myriad of markets ranging from solar panel manufacturing to finger nail polish.  
We are pleased to comment on EGLE’s proposed changes to Rules 336.1601 – R 336.1662  
which, according to your agency, are necessary to satisfy requirements of the federal Clean Air  
Act (CAA) 42 USC 7401 et seq., requirements referred to as “Reasonably Available Control  
Technologies” (RACT).  
Unlike conventional inks and coatings, UV/EB/LED products do not evaporate. Instead, they are  
specifically formulated to react to an energy source. The nature of the process is such that  
virtually no Volatile Organic Compounds (VOCs) are generated. Additionally, UV/EB/LED  
processes are electric and thus do not produce combustion contaminants such as Nitrogen Oxides  
(NOx), Sulfur Oxides (Sox) and Greenhouse Gases. With UV/EB/LED technology, facilities can  
achieve emission reductions above and beyond those required by even the most stringent of  
regulations. Thus, our technology can help EGLE achieve requirements of the “Reasonable  
Available Control Technology” (RACT) provisions in the Clean Air Act.  
The South Coast Air Quality Management District (SCAQMD) has some of the most stringent  
air quality regulations in the nation. In many of its rulemakings, the agency has recognized the  
sustainability advantages, including energy efficiency, of energy curable technology. SCAQMD  
provides incentives to companies who convert to UV/EB/LED through exemptions from  
permitting and recordkeeping. The agency recognized UV/EB/LED as Best Available Control  
Technology (BACT) for many industry sectors and the technology has recently been included in  
the Statewide BACT Clearinghouse for the California Air Resources Board.  
UV/EB/LED technology is considered “super-compliant” in the SCAQMD which applies to  
coatings with a Volatile Organic Compound (VOC) content of less than 50 grams per liter.  
RadTech holds a seat on the South Coast Air Quality Management Plan Advisory Committee.  
Our Association provides input to the agency on how to achieve clean air goals and  
implementation of UV/EB/LED is one strategy which has been included in the most recent  
documents of the Air Quality Management Plan (AQMP). According to SCAQMD findings:  
“These programs may also provide manufacturers with incentives to accelerate the  
deployment of cleaner technologies. Such an example is the use of energy-curing  
technologies which includes ultraviolet light (UV), electron beam (EB), heat and light  
emitting diode (LED) cured coatings.  
The California State Senate has adopted a resolution recognizing the many benefits of ultraviolet  
(UV) and electron beam (EB) technologies and the contributions of RadTech. The proclamation  
acknowledges the “invaluable” contributions made by RadTech to the State of California and  
beyond, and cites the Association’s ideals of community service. It commends RadTech for its  
“outstanding commitment to improving the environment and economy through its programs.”  
The Environmental Protection Agency (EPA) has classified UV/EB technology as Lowest  
Achievable Emission Rate. The EPA Control Techniques Guidelines documents state: “This  
technology is gaining greater acceptance and, where applicable, achieves a near 100 percent  
reduction of VOC emissions”.  
According to the public notice, the state must revise existing RACT rules to align with the most  
recent recommendations contained in the United States Environmental Protection Agency’s  
(USEPA) Control Technique Guidelines (CTGs) and promulgate new more stringent rules  
setting or revising emission standards and operational requirements for certain types of existing  
emission sources.  
UV/EB/LED can play a role in the following EGLE rules:  
Rule 336.1610-- Emission of volatile organic compounds from existing automobile, light-  
duty truck, and other product and material coating lines.  
Rule 336.1620-- Emission of volatile organic compounds from existing flat wood  
paneling coating lines.  
Rule 336.1621-- Emission of volatile organic compounds from existing metallic surface  
coating lines.  
Rule 336.1632-- Emission of volatile organic compounds from existing automobile,  
truck, and business machine plastic part coating lines.  
We are concerned that some of the Environmental Protection Agency’s (EPA) Control  
Technique Guidelines (CTG) have not been updated since 1978 and thus the information is not  
accurate by current application methods and standards in 2020. Basing the RACT demonstration  
on the EPA CTGs may not capture the current state of our technology which has greatly  
advanced since the promulgation of the CTGs. As an example, the CTG for Wood Furniture  
Manufacturing Operations, promulgated in 1996, assumes that energy curable materials have a  
Volatile Organic Compound (VOC) content of 458 grams per liter but, currently our materials  
are typically less than 50 grams per liter in VOC content and in many cases exceed current  
EGLE rule limits. Throughout the years, ink and coating makers have continued work to  
formulate alternative materials which, may not have been readily available when the CTGs were  
promulgated. In many cases, there is no consideration of energy curable inks which can be  
equivalent to control devices and analogous to other low VOC ink systems.  
We note that competing technologies such as conventional solvent systems with add-on controls  
and waterborne coating processes, have been included in most of the relevant EPA CTGs. One  
of EPA’s recommendations is that “inks which contain 60 percent or more non-volatile material  
be exempt from emission limitations in order to encourage development of high solids inks.”  
We very much support this incentive type approach and urge EGLE to implement it.  
We request that UV/EB/LED processes be considered as an alternative equivalent option in the  
RACT Demonstration. UV/EB/LED technology is available in the following CTG categories:  
Offset Lithographic Printing and Letterpress Printing  
Graphic Arts-Rotogravure and Flexography  
Flexible Package Printing  
Wood Furniture Manufacturing Operations  
Factory Surface Coating of Flat Wood Paneling  
Flat Wood Paneling Coatings  
Flat Wood, Interior Paneling  
Large Appliance Coatings  
Metal Furniture Coatings  
Surface Coating of Miscellaneous Metal Parts and Plastics Products  
Paper, Film and Coil Coatings  
Miscellaneous Industrial Adhesives  
Automobile and Light-Duty Truck Assembly Coatings  
Surface Coating of Cans  
The following are examples (not an exhaustive list) of permitted operations in the SCAQMD  
using UV/EB/LED technology:  
Spray Booth, Wood  
Company Name  
Application # Date Issued  
Excel Cabinets, Inc.  
Head West Inc.  
450588  
F80114  
11/26/05  
01/12/06  
Lithographic Printing  
Company Name  
AQMD  
Permit #  
F32751  
F15320  
F24307  
D53533  
F15651  
F15651  
D92649  
F31957  
Date Issued  
Holiday Printing & Lithograph Inc.  
Westminster Press  
07/25/00  
08/11/98  
02/09/00  
05/21/92  
11/24/98  
11/24/98  
08/10/95  
06/21/00  
K & D Graphics, A California Corp.  
Jaco Printing Corp, Business Forms Press  
Jaco Printing Corp, Business Forms Press  
Jaco Printing Corp, Business Forms Press  
Royal Paper Box Co.  
Creative Mailings Inc.  
Request to Include Incentives in Rulemaking  
Our materials are typically well below 50 grams/liter in VOC content which is minimal  
compared to existing and proposed limits. We respectfully request that UV/EB/LED materials  
be exempted from the rule requirements. An exemption would be an incentive for businesses to  
voluntarily choose UV/EB/LED technology resulting in additional emission reductions for the  
South Coast Basin.  
Recordkeeping requirements are burdensome on businesses and in the case of UV/EB/LED  
operations, are not crucial because the materials are well below the rule limits. Exempting  
energy curable materials from overly prescriptive recordkeeping requirements will alleviate  
regulatory burdens on EGLE’s business community and benefit air quality.  
Definition  
We would very much appreciate the inclusion of a definition for energy curable materials in the  
rule. We propose a definition like the one in other SCAQMD rules (R1130, R1168):  
ENERGY CURABLE MATERIALS are single component reactive products that cure upon  
exposure to visible-light, ultraviolet light, or to an electron beam.  
Test Method  
The Environmental Protection Agency and the SCAQMD have long recognized that EPA  
Method 24 is not suitable for thin film UV/EB/LED Materials. RadTech urges the inclusion of  
ASTM D7767-11 as suitable test method for thin film UV/EB/LED products. We propose the  
following language:  
The VOC content of thin film Energy Curable Adhesives and Sealants may be determined by  
manufacturers using ASTM Test Method 7767 Standard Test Method to Measure Volatiles from  
Radiation Curable Acrylate Monomers, Oligomers, and Blends and Thin Coatings Made from  
Them.  
Request for Additional Time to Submit Comments  
As requested via the Q & A box in the meeting today, we request a one week extension to the  
public comment period to allow our members to submit comments on this rulemaking.  
We look forward to a continued collaboration with EGLE. Please let me know of any additional  
assistance our association can provide.  
Sincerely,  
Rita M. Loof  
Director, Environmental Affairs  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
McDonald, Tracey (EGLE)  
Thursday, October 27, 2022 7:53 AM  
Vaerten, Marissa (EGLE)  
FW: Public Comments on the Michigan’s Department of Environment, Great Lakes and  
Energy (EGLE) Changes to R 336.1601 – R 336.1662 and “Reasonably Available Control  
Technologies” (RACT)  
Subject:  
Attachments:  
Categories:  
10-26-22 EGLE Public Comments Letter.pdf  
2022-018EQ COMMENTS  
FYI. I’ve replied and a copy has already been added to the comment folder  
From: Mike Bonner < @viscosity.com>  
Sent: Wednesday, October 26, 2022 4:00 PM  
To: McDonald, Tracey (EGLE) <MCDONALDT@michigan.gov>  
Subject: Public Comments on the Michigan’s Department of Environment, Great Lakes and Energy (EGLE) Changes to R  
336.1601 – R 336.1662 and “Reasonably Available Control Technologies” (RACT)  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Dear Mr. McDonald,  
Attached please find our comments on the abovementioned rule changes being contemplated by EGLE.  
Please feel free to reach out to me if I can be of any assistance whatsoever.  
Best Regards,  
Michael R. Bonner | Vice President – Engineering & Technology  
@viscosity.com  
www.viscosity.com  
12427 31 Mile Road | Washington, MI 48095 USA  
Visit our Blog @ The Business of Viscosity  
CLICK FOR FREE CUSTOMIZED REPORT  
CLICK TO REVIEW EVALUATION TOOLS  
1
October 26th, 2022  
Mr. Trace McDonald  
Department of Environment, Great Lakes and Energy  
Air Quality Division  
Re: Public Comments on the Michigan’s Department of Environment, Great Lakes and Energy  
(EGLE) Changes to R 336.1601 – R 336.1662 and “Reasonably Available Control  
Technologies” (RACT).  
Dear Mr. McDonald:  
Saint Clair Systems, Inc. is a Michigan based company, involved in the design manufacture of  
temperature and viscosity control equipment for fluid dispensing systems. This includes both  
solvent based and UV/EB cure applications for various customers, many of whom are located in  
Michigan. We are involved in industrial/automotive finishing, adhesives and sealants, coil  
coatings, food packaging, and printing sectors. Our company is a member of the RadTech  
International association.  
We echo RadTech’s requests to provide incentives for facilities in Michigan who have converted  
or are considering conversion to UV/EB/LED. The technology can help EGLE achieve  
requirements of the “Reasonable Available Control Technology” (RACT) provisions in the  
Clean Air Act. UV/EB/LED can play a role in the following EGLE rules:  
Rule 336.1610-- Emission of volatile organic compounds from existing automobile, light-  
duty truck, and other product and material coating lines.  
Rule 336.1620-- Emission of volatile organic compounds from existing flat wood  
paneling coating lines.  
Rule 336.1621-- Emission of volatile organic compounds from existing metallic surface  
coating lines.  
Rule 336.1632-- Emission of volatile organic compounds from existing automobile,  
truck, and business machine plastic part coating lines.  
We are concerned that some of the Environmental Protection Agency’s (EPA) Control  
Technique Guidelines (CTG) have not been updated since 1978 and thus the information is not  
accurate by current application methods and standards in 2020. Basing the RACT demonstration  
on the EPA CTGs may not capture the current state of our technology which has greatly  
advanced since the promulgation of the CTGs. As an example, the CTG for Wood Furniture  
12427 31 Mile Road • Washington Township, Michigan • 48095  
Manufacturing Operations, promulgated in 1996, assumes that energy curable materials have a  
Volatile Organic Compound (VOC) content of 458 grams per liter but, currently UV/EB/LED  
materials are typically less than 50 grams per liter in VOC content and in many cases exceed  
current EGLE rule limits. Throughout the years, ink and coating makers have continued work to  
formulate alternative materials which may not have been readily available when the CTGs were  
promulgated. In many cases, there is no consideration of energy curable inks which can be  
equivalent to control devices and analogous to other low VOC ink systems.  
We request that UV/EB/LED processes be considered as an alternative equivalent option in the  
RACT Demonstration. UV/EB/LED technology is available in the following CTG categories:  
Offset Lithographic Printing and Letterpress Printing  
Graphic Arts-Rotogravure and Flexography  
Flexible Package Printing  
Wood Furniture Manufacturing Operations  
Factory Surface Coating of Flat Wood Paneling  
Flat Wood Paneling Coatings  
Flat Wood, Interior Paneling  
Large Appliance Coatings  
Metal Furniture Coatings  
Surface Coating of Miscellaneous Metal Parts and Plastics Products  
Paper, Film and Coil Coatings  
Miscellaneous Industrial Adhesives  
Automobile and Light-Duty Truck Assembly Coatings  
Surface Coating of Cans  
We wholeheartedly support RadTech’s requests for regulatory flexibility in the form of permit  
exemptions in EGLE’s rules. Energy curable materials are typically well below 50 grams/liter in  
VOC content which is minimal compared to existing and proposed limits. We respectfully  
request that UV/EB/LED materials be exempted from the rule requirements. An exemption  
would be an incentive for businesses to voluntarily choose UV/EB/LED technology resulting in  
additional emission reductions for Michigan.  
Recordkeeping requirements are burdensome on businesses and in the case of UV/EB/LED  
operations, are not crucial because the materials are well below the rule limits. Exempting  
energy curable materials from overly prescriptive recordkeeping requirements will alleviate  
regulatory burdens on EGLE’s business community and benefit air quality.  
We would very much appreciate the inclusion of a definition for energy curable materials in the  
rule. We propose a definition like the one in SCAQMD rules (R1130, R1168):  
ENERGY CURABLE MATERIALS are single component reactive products that cure upon  
exposure to visible-light, ultraviolet light, or to an electron beam.  
12427 31 Mile Road • Washington Township, Michigan • 48095  
The Environmental Protection Agency and the SCAQMD have long recognized that EPA  
Method 24 is not suitable for thin film UV/EB/LED Materials. We urge the inclusion of ASTM  
D7767-11 as suitable test method for thin film UV/EB/LED products. We support RadTech’s  
proposed language as follows:  
The VOC content of thin film Energy Curable Adhesives and Sealants may be determined by  
manufacturers using ASTM Test Method 7767 Standard Test Method to Measure Volatiles from  
Radiation Curable Acrylate Monomers, Oligomers, and Blends and Thin Coatings Made from  
Them.  
We look forward to a continued collaboration with EGLE. Please let me know of any additional  
assistance we can provide.  
Sincerely,  
Michael R. Bonner  
Vice President Engineering & Technology  
12427 31 Mile Road • Washington Township, Michigan • 48095  
Vaerten, Marissa (EGLE)  
From:  
Sent:  
To:  
Gary Jones  
Tuesday, October 25, 2022 2:58 PM  
Vaerten, Marissa (EGLE)  
@printing.org>  
Cc:  
McDonald, Tracey (EGLE)  
RE: Info From Joshua Flood at Kay Automotive Graphics  
AdhesivesRACTRuleApplicabilityScreenPrinting.docx  
Subject:  
Attachments:  
Categories:  
2022-018EQ COMMENTS  
CAUTION: This is an External email. Please send suspicious emails to abuse@michigan.gov  
Hi Marissa,  
Thanks for the feedback on the information from Kay Automotive Graphics.  
As I went back and looked at the CTG that EPA issued on adhesives, it became apparent that screen printing was also not  
to be included as it was not specifically identified as a covered source category, so I am submitting the attached memo  
that includes the reasoning as a supplement to my previous comments.  
Please let me know if you have any question or need additional information.  
Gary Jones  
Director, Environmental, Health, and Safety Affairs  
PRINTING United Alliance  
10015 Main St., Fairfax, VA 22031  
|
@printing.org  
1
MICHIGAN DEPARTMENT OF ENVIRONMENT, GREAT LAKES, AND  
ENERGY ENVIRONMENTAL QUALITY  
AIR QUALITY DIVISION  
AIR POLLUTION CONTROL  
Filed with the secretary of state on  
These rules take effect immediately upon filing with the secretary of state unless adopted  
under section 33, 44, or 45a(9) of the administrative procedures act of 1969, 1969 PA  
306, MCL 24.233, 24.244, or 24.245a. Rules adopted under these sections become  
effective 7 days after filing with the secretary of state.  
(By authority conferred on the director of the department of environment, Great Lakes,  
and energy environmental quality by sections 5503 and 5512 of the natural resources  
and environmental protection act, 1994 PA 451, MCL 324.5503 and 324.5512, and  
Executive Reorganization Order Nos.umbers 1995-16, 2009-31, and 2011-1, MCL  
324.99903, 324.99919, and 324. 99921)  
R 336.1601, R 336.1602, R 336.1606, R 336.1607, R 336.1608, R 336.1609, R 336.1610,  
R 336.1611, R 336.1618, R 336.1620, R 336.1621, R 336.1622, R 336.1623, R 336.1624,  
R 336.1625, R 336.1627, R 336.1628, R 336.1629, R 336.1630, R 336.1631, R 336.1632,  
and R 336.1660 of the Michigan Administrative Code are is amended, R 336.1610a, R  
336.1620a, R 336.1621a, R 336.1624a, R 336.1633, R 336.1634, R 336.1635, R  
336.1636, R 336.1637, R 336.1638, R 336.1639, R 336.1640, R 336.1641, R 336.1642, R  
336.1643, R 336.1644, and R 336.1662 are added, and R 336.1661 is rescinded, as  
follows:  
PART 6. EMISSION LIMITATIONS AND PROHIBITIONS--  
EXISTING SOURCES OF VOLATILE ORGANIC COMPOUND EMISSIONS  
R 336.1601 Definitions.  
Rule 601. As used in this part:  
(a) “2015 ozone nonattainment area” means Berrien, Livingston, Macomb,  
Monroe, Oakland, St. Clair, Washtenaw, Wayne, the western portion of Allegan,  
and the western portion of Muskegon Counties.  
(b) “Eastern portion of Muskegon County” means the areas located in Muskegon  
County described as Casnovia Township, Cedar Creek Township, Egelston  
Township, Holton Township, Moorland Township, Ravenna Township, and  
Sullivan Township.  
(a)(c) "Existing source" means any of the following: (i) Any process or process  
equipment which that is subject to the provisions rules listed in table 60 of R 336.1604  
to R 336.1618 and which has either has been placed into operation before the  
corresponding date listed in table 60 July 1, 1979, or for which an application for a  
September 7, 2022  
permit to install, pursuant to the provisions of part 2 of these rules, was made to the  
department before July 1, 1979 the corresponding date listed in table 60. The term  
does not include a process or process equipment operated for research, development, or  
pilot studies, if the operation is not for the purpose of producing saleable products or  
goods.  
TABLE 60  
Rules  
Date  
R 336.1604 to R 336.1605  
R 336.1606 to R 336.1609  
R 336.1610  
R 336.1610a  
R 336.1611 to R 336.1617  
R 336.1618  
R 336.1620  
R 336.1620a  
R 336.1621  
R 336.1621a  
R 336.1622 to R 336.1624  
R 336.1624a  
R 336.1625  
R 336.1628  
R 336.1629  
R 336.1630 and R 336.1631  
R 336.1632 to R 336.1644  
Any process or process equipment not  
subject to the provisions of any rule in this  
part.  
July 1, 1979  
March 1, 2023  
July 1, 1979  
March 1, 2023  
July 1, 1979  
March 1, 2023  
July 1, 1980  
March 1, 2023  
July 1, 1980  
March 1, 2023  
July 1, 1980  
March 1, 2023  
July 1, 1980  
January 5, 1981  
January 20, 1984  
July 1, 1987  
March 1, 2023  
July 1, 1979  
(ii) Any process or process equipment which is subject to the provisions of R 336.1619  
to R 336.1625 and which either has been placed into operation before July 1, 1980, or for  
which an application for a permit to install, pursuant to the provisions of part 2 of these  
rules, was made to the department before July 1, 1980.  
(iii) Any process or process equipment which is subject to the provisions of R 336.1628  
and which either has been placed into operation before January 5, 1981, or for which an  
application for a permit to install, pursuant to the provisions of part 2 of these rules, was  
made to the department before January 5, 1981.  
(iv) Any process or process equipment which is subject to the provisions of R 336.1629  
and which either has been placed into operation before January 20, 1984, or for which an  
application for a permit to install, pursuant to the provisions of part 2 of these rules, was  
made to the department before January 20, 1984.  
(v) Any process or process equipment which is subject to the provisions of R 336.1630  
or R 336.1631 and which either has been placed into operation before July 1, 1987, or for  
2
which an application for a permit to install, pursuant to the provisions of part 2 of these  
rules, was made to the department before July 1, 1987.  
(vi) Any process or process equipment which is subject to the provisions of R 336.1632  
and which either has been placed into operation before the effective date of R 336.1632  
or for which an application for a permit to install, pursuant to the provisions of part 2 of  
these rules, was made to the department before the effective date of R 336.1632.  
(vii) Any process or process equipment which is not subject to the provisions of any rule  
in this part and which either has been placed into operation before July 1, 1979, or for  
which an application for a permit to install, pursuant to the provisions of part 2 of these  
rules, was made to the department before July 1, 1979. The term does not include a  
process or process equipment operated for research, development, or pilot studies, if the  
operation is not for the purpose of producing saleable products or goods.  
(d) “Heavier vehicles” means a self-propelled vehicle designed for transporting  
persons or property on a street or highway that has a gross vehicle weight rating  
over 8,500 pounds.  
(e) “Natural gas distribution” means activities in which the natural gas is provided  
for the end user by a distribution facility after that facility receives the natural gas  
from the natural gas transmission and storage segment.  
(f) “Natural gas processing” means the process of separating and recovering  
certain hydrocarbons and fluids from the raw gas to produce pipeline quality  
natural gas and natural gas products.  
(g) Natural gas processing plant” means any processing site engaged in the  
extraction of natural gas liquids from field gas, fractionation of mixed natural gas  
liquids to natural gas products or both. Natural gas processing plant does not  
include a Joule-Thompson valve, a dew point depression valve, or an isolated or  
standalone Joule-Thompson skid.  
(h) “Natural gas transmission and storage” means the transport of natural gas,  
excluding processing, sometimes long distances, and the temporary storage of that  
gas. Specific equipment used in natural gas transmission includes the land, mains,  
valves, meters, boosters, regulators, storage vessels, dehydrators, compressors, and  
their driving units and appurtenances, and equipment used for transporting gas  
from a production facility, delivery point of purchased gas, gathering system,  
storage area, or other wholesale source of gas to 1 or more distribution areas.  
(i) “Oil and natural gas industry” means the operations involved in the extraction  
and production of crude oil and natural gas, as well as the processing, transmission,  
storage, and distribution of natural gas. For the purposes of the rules in this part, oil  
and natural gas industry operations will be referred to in the following 4 segments:  
(i) Oil and natural gas production.  
(ii) Natural gas processing.  
(iii) Natural gas transmission and storage.  
(iv) Natural gas distribution.  
(j) “Oil and natural gas production” means operations including the wells and all  
related processes used in the extraction, production, recovery, lifting, stabilization,  
and separation or treating of oil or natural gas, or both, including condensate.  
(k) "Person responsible" means a person that owns, leases, controls, operates, or  
supervises a source of air contaminants.  
3
(lb) “Western portion of Allegan County” means the areas in Allegan County  
described as Casco Township, Cheshire Township, city of Douglas, city of Holland,  
city of Saugatuck, Clyde Township, Fillmore Township, Ganges Township, Heath  
Township, Laketown Township, Lee Township, Manlius Township, Overisel  
Township, Saugatuck Township, and Valley Township. "Person responsible" means a  
person who owns, leases, controls, operates, or supervises  
a source of air contaminants.  
(m) “Western portion of Muskegon County” means the areas located in Muskegon  
County described as Blue Lake Township, city of Montague, city of Muskegon, city  
of Muskegon Heights, city of North Muskegon, city of Roosevelt Park, city of  
Whitehall, Dalton Township, including the village of Lakewood Club, Fruitland  
Township, Fruitport Township, including the village of Fruitport, Laketon  
Township, Montague Township, Muskegon Township, city of Norton Shores, White  
River Township, and Whitehall Township.  
R 336.1602 Existing sources of volatile organic compound emissions generally.  
Rule 602. (1) A person shall not cause or allow the emission of volatile organic  
compounds from any existing source in excess of the provisions of any rule of this part or  
the maximum allowable emission rate specified in any of the following, whichever  
results in the lowest maximum allowable emission rate:  
(a) A permit to install.  
(b) A permit to operate.  
(bc) A renewable operating permit issued under R 336.1210.  
(cd) A voluntary agreement.  
(de) A performance contract.  
(ef) A stipulation.  
(fg) An order of the department.  
(2) Department approvals for the equivalent emission rates, alternate emission rates, or  
compliance methods that are authorized pursuant to any of the provisions listed in  
subdivision (a) of this subrule must comply shall be in compliance with all of the  
following provisions:  
(a) The provisions of this subrule apply to approvals by the department pursuant to any  
of the following provisions:  
(i) R 336.1610(5)(a) (More than 24-hour but less than 1-month averaging period).  
(ii) R 336.1610(11) table 63 (Column B - transfer efficiency).  
(iii) R 336. 1610a(4)(d)(i) (More than 24-hour but less than 1-month averaging  
period).  
(iv) R 336.1610a(4) table 64-b and table 64-d (Column B transfer efficiency).  
(viii) R 336.1611(1) (Equivalent control method).  
(ivi) R 336.1620(34)(a) (More than 24-hour but less than 1-month averaging period).  
(vii) R 336.1621(34) (Transfer efficiency).  
(viii) R 336.1621(4) (Baseline transfer efficiency less than 60%).  
(viix) R 336.1621(6)(a) (More than 24-hour but less than 1-month averaging period).  
(viiix) R 336.1621(9)(e) (Metallic-nonmetallic part).  
(xi) R 336.1621a(2)(b)(ii) (Metallic-nonmetallic part).  
4
(xii) R 336.1621a(3)(c) (Alternate emission limits).  
(xiii) R 336.1621a(3)(h)(i) (More than 24-hour but less than 1-month averaging  
period).  
(ixiv) R 336.1622(1) (Equivalent control method).  
(xv) R 336.1623(1) (Equivalent control method).  
(xvi) R 336.1623(8)(d) (Equivalent compliance provisions).  
(xvii) R 336.1624(1) (Equivalent emission rate).  
(xviii) R 336.1624(5)(d) (More than 24-hour but less than 1-month averaging period).  
(xivx) R 336.1625(1) (Equivalent control method, except alternative to condenser in  
R 336.1625(2)(b)).  
(xvx) R 336.1625(2)(b) (Alternative control method).  
(xvxi) R 336.1625(8) (Alternative control system).  
(xvxii) R 336.1628(1) (Equivalent control method).  
(xvxiii) R 336.1629(1) (Equivalent control method).  
(xixiv) R 336.1630(1) (Equivalent control method).  
(xxv) R 336.1631(1) (Equivalent control method).  
(xxvi) R 336.1631(5) (Alternate compliance method).  
(xxvii) R 336.1632(86)(a) (More than 24-hour but less than 1-month averaging  
period).  
(xxiii) R 336.1632(13) (Alternate compliance provisions).  
(xxiv) R 336.1632(14) (Cross-line averaging).  
(xxviii) R336.1633(3)(f)(i) (More than 24-hour but less than 1-month averaging  
period).  
(xxix) R 336.1636(4)(a) (Alternate emission limits).  
(xxx) R 336.1636(6)(b)(i) (More than 24-hour but less than 1-month averaging  
period).  
(xxvxi) R 336.2004(4) (Alternate test method).  
(xxvxii) R 336.2040(5)(a)(i)(A) (Alternate test method).  
(xxvxiii) R 336.2040(5)(a)(iv) (Alternate test method).  
(xxviixiv) R 336.2040(9) (Transfer efficiency test method).  
(xxixv) R 336.2040(9)(j)(ii) (Alternate measurement procedure).  
(xxxvi) R 336.2040(10) (Modified capture efficiency test method).  
(xxxvii) R 336.2040(11)(a)(iv) (Alternate test method).  
(xxxviii) R 336.2040(11)(b)(ii) (Alternate test method).  
(b) Upon application for a new permit or order, or revision to an existing permit  
or order, to request the approval of the provisions outlined in subdivision (a) of this  
subrule, the source shall submit a demonstration containing the following, as  
applicable:  
(i) Reasons why the applicant is requesting an alternative.  
(ii) Information demonstrating why the limitation or requirement as described in  
the applicable part 6 rule is not possible to attain.  
(iii) Explanation of why alternative options, such as implementation of add-on  
controls or modifying coating formulations would not be sufficient to meet other  
part 6 rules.  
5
(iv) A demonstration showing why the ozone National Ambient Air Quality  
Standard will not be affected.  
(v) Additional pertinent information, as needed.  
(b) Department approvals for the equivalent emission rates, alternate emission rates, or  
compliance methods that are authorized by any of the provisions identified in subdivision  
(a) of  
this subrule shall be in compliance with all of the following provisions:  
(ci) At a minimum, Tthe portion of or the whole proposed draft permit or order  
approval related to this rule shall be is subject to a 30-day public comment period. (ii)  
When the proposed approval is noticed for a 30-day public comment period, a copy of the  
notice shall must also be sent to the United States Environmental Protection Agency.  
(diii) The proposed draft permit or order approval must shall offer is subject to a  
public hearing upon request immediately after the 30-day public comment period that is  
required in paragraph subdivision (ic) of this subdivision rule.  
(eiv) The department approval shall becomes part of a legally enforceable order of the  
department, or permit to install, or permit to operate.  
(fv) Upon department issuance of Tthe legally enforceable document identified in  
paragraph subdivision (ive) of this subdivision rule, it must shall be sent to the United  
States Environmental Protection Agency as a request for a revision of the Michigan state  
implementation plan, together with all of the other information that is required for the  
submittal of a complete state implementation plan revision request. Department approval  
and the legally enforceable document does not shall have no effect on the federally  
approved state implementation plan until and unless the submitted state implementation  
plan revision request is formally approved by the United States Environmental Protection  
Agency.  
(3) Department approvals of a derivative authorized by the for the equivalent emission  
rates, alternate emission rates, or compliance methods that are authorized by the  
provisions identified in subdivision (a) of this subrule shall be in compliance with both of  
in R 336.1625(4) include the following provisions actions:  
(a) The provisions of this subrule apply to approvals by the department pursuant to R  
336.1625(4) (Alternate condenser temperature).  
(b) Department approvals for the equivalent emission rates, alternate emission rates, or  
compliance methods that are authorized pursuant to the provisions identified in  
subdivision (a) of this subrule shall be in compliance with both of the following  
provisions:  
(ai) The department approval shall becomes part of a legally enforceable order of the  
department, or permit to install, or permit to operate.  
(bii) A copy of the legally enforceable document that is identified in paragraph (i) of  
this subdivision (a) of this subrule shall is sent to the United States Environmental  
Protection Agency.  
(4) In R 336.1610, R 336.1621, and R 336.1632, where emission limits are expressed in  
pounds of volatile organic compounds per gallon of coating, minus water, as applied, the  
phrase "minus water" shall also include compounds which are used as organic solvents  
and which are excluded from the definition of volatile organic compound.  
(4) A person responsible for a facility with allowed or potential volatile organic  
compound emissions equal or greater than 100 tons per year in the 2015 ozone  
6
nonattainment area for which no reasonably available control technology (RACT)  
requirement has been established in R 336.1604 to R336.1644, shall meet all of the  
following requirements:  
(a) Provide the department and United States Environmental Protection Agency  
with the following information within 1 month after final promulgation of this rule  
revision:  
(i) Identification of each facility, including individual emission sources, to which  
this rule applies.  
(ii) Determination of the total potential to emit and the actual emissions of volatile  
organic compounds for the most recent calendar year from each source at the  
facility using emission testing, mass balance, or a calculation method acceptable by  
the department.  
(b) Within 3 months after final promulgation of this rule revision, provide to the  
department and United States Environmental Protection Agency, a proposal for  
RACT for each source of volatile organic compounds at the facility. The RACT  
proposal must include, at a minimum, the following information:  
(i) A list of each source subject to the RACT requirements.  
(ii) The size or capacity of each affected source and the types and quantities of  
materials processed or produced in each source.  
(iii) A physical description of each source and its operating characteristics.  
(iv) Estimates of the potential and actual volatile organic compound emissions  
from each affected source and associated supporting documentation.  
(v) A RACT analysis which meets the requirements of subdivision (c) of this  
subrule, including technical and economic support documentation for each affected  
source.  
(vi) A schedule for completing implementation of the RACT proposal as  
expeditiously as practicable but not later than 6 months after department approval  
of the proposal, including interim dates for the issuance of purchase orders, start  
and completion of process, technology and control technology changes, and the  
completion of compliance testing.  
(vii) The testing, monitoring, recordkeeping, and reporting procedures proposed  
to demonstrate compliance with RACT.  
(viii) Any additional information requested by the department necessary for the  
evaluation of the RACT proposal.  
(c) The RACT analysis required under subdivision (b)(v) of this subrule must  
include:  
(i) A ranking of the available control options for the affected source in descending  
order of control effectiveness. Available control options are air pollution control  
technologies or techniques with a reasonable potential for application to the source.  
Air pollution control technologies and techniques include the application of  
production process or control methods that reduce volatile organic compound  
emissions. The control technologies and techniques must include existing controls  
for the source category and technology transfer controls applied to similar source  
categories.  
7
(ii) An evaluation of the technical feasibility of the available control options  
identified in paragraph (i) of this subdivision. The evaluation of technical feasibility  
must be based on physical, chemical, and engineering principles. A determination of  
technical infeasibility must identify technical difficulties that would preclude the  
successful use of the control option on the affected source.  
(iii) A ranking of the technically feasible control options in descending order of  
overall control effectiveness for volatile organic compound emissions. The list must  
present the array of control options and include, at a minimum, the following  
information:  
(A) The baseline emissions of volatile organic compounds before implementation  
of each control option.  
(B) The estimated emission reduction potential or the estimated control efficiency  
of each control option.  
(C) The estimated emissions after the application of each control option.  
(D) The economic impacts and cost effectiveness of each control option.  
(iv) An evaluation of cost effectiveness of each control option consistent with the  
“EPA Air Pollution Control Cost Manual (Sixth Edition),EPA-452/B-02-001,  
adopted by reference in R 336.1902. The evaluation must be conducted in  
accordance with the following requirements:  
(A) The cost effectiveness must be evaluated in terms of dollars per ton of  
volatile organic compound emissions reduction.  
(B) The cost effectiveness must be calculated as the annualized cost of the  
control option, divided by the baseline emission rate, minus the control option  
emission rate, as shown by the following equation:  
Average cost effectiveness  
($/ton removed)  
=
Control option total annualized cost ($/yr)  
-------------------------------------------------------  
Baseline emission rate Control option rate (tons/yr)  
(C) For purposes of this subparagraph, baseline emission rate represents the  
maximum emissions before the implementation of the control option. The baseline  
emission rate is established using either test results or approved emission factors  
and historic operating data.  
(d) The department shall approve, deny, or modify each RACT proposal.  
(e) Upon receipt of notice of the department's approval of the RACT proposal, the  
facility shall begin implementation of the measures necessary to comply with the  
approved or modified RACT proposal. Implementation of the RACT program must  
be completed according to the schedule established in the approved RACT proposal  
and be as expeditious as practicable, but no later than 6 months after department  
approval of the RACT proposal.  
(f) The department shall submit each approved RACT program to the United  
States Environmental Protection Agency for approval as a revision to the state  
implementation plan.  
R 336.1606 Loading gasoline into existing stationary vessels of more than 2,000-gallon  
capacity at dispensing facilities handling 250,000 or more gallons per year.  
8
Rule 606. (1) After June 30, 1980, iIt is unlawful for a person to load or allow the  
loading of gasoline from a delivery vessel into any existing stationary vessel of more than  
2,000-gallon capacity located at a gasoline dispensing facility which is in any county  
listed in table 61-a and which has a throughput of 250,000 or more gallons per year,  
unless the such stationary vessel is equipped with a permanent submerged fill pipe for  
either of the following:.  
(a) A facility with a throughput of 250,000 or more gallons per year, and the  
stationary vessel was installed before July 1, 1979.  
(b) The stationary vessel was installed after July 1, 1979, and before March 1,  
2023.  
(2) After June 30, 1981, it is unlawful for a person to load or allow the loading of  
gasoline from a delivery vessel into any existing stationary vessel of more than 2,000-  
gallon capacity located at a gasoline dispensing facility which is outside of any county  
listed in table 61-a and which has a throughput of 250,000 or more gallons per year,  
unless such stationary vessel is equipped with a permanent submerged fill pipe.  
(23) After December 31, 1982, iIt is unlawful for a person to load or allow the loading  
of gasoline from a delivery vessel into any existing stationary vessel of more than 2,000-  
gallon capacity located at a gasoline-dispensing facility which is in any area listed in  
table 61 and which has a throughput of 250,000 or more gallons per year, unless the such  
stationary vessel is controlled by a vapor balance system or an equivalent control system  
approved by the department for the following:  
(a) Any stationary vessel installed before July 1, 1979, located in the area listed in  
table 61 and which has a throughput of 250,000 or more gallons per year, except  
those served exclusively by gasoline loading facilities that have a throughput of less  
than 1,000,000 gallons of gasoline per year.  
(b) Any stationary vessel installed or modified after July 1, 1979, and before  
March 1, 2023, and located in an area listed in table 61 or in the 2015 ozone  
nonattainment area.  
(3) Proper operation of tThe vapor balance system as required in subrule (2) of this  
rule is when shall capture displaced gasoline vapor and air are captured by means of a  
vaportight vapor tight collection line and shall be is designed to return not less than  
90%, by weight, of the displaced gasoline vapor from the stationary vessel to the delivery  
vessel.  
(4) Any stationary vessel that is subject to the provisions of subrule (32) of this rule  
shall must be equipped, maintained, or controlled with both of the following:  
(a) An interlocking system or procedure to ensure that the vaportight vapor tight  
collection line is connected before any gasoline can be loaded.  
(b) A device to ensure that the vaportight vapor tight collection line is shall close  
closed upon disconnection so as to prevent the release of gasoline vapor.  
(5) Any delivery vessel that is subject to the provisions of subrule (32) of this rule must  
shall be vaportight vapor tight and shall be filled only at a loading facility that is  
equipped with a system as required by R 336.1608(32) and (45), and R 336.1609(2) and  
(34). R 336.1705(2) and (3), or R 336.1706(2) and (3).  
(6) The provisions of subrules (3) and (4) of this rule shall not apply to a stationary  
vessel at a gasoline-dispensing facility that is served exclusively by gasoline-loading  
facilities exempted by the department under R 336.1608(7) An existing stationary  
9
vessel installed or modified after July 1, 1979, and before March 1, 2023, at a  
gasoline dispensing facility that is not subject to the provisions of subrule (2) of this  
rule must be constructed in a manner that allows the vessel to be retrofitted  
according to subrules (2) and (4) of this rule.  
(7) Tables 61 and 61-a read as follows:  
TABLE 61  
List of major metropolitan areas.  
(Subject to R 336.1606, R 336.1607, and R 336.1608) R 336.1703, R 336.1704, and R  
336.1705)  
Metropolitan  
Area  
County  
Affected area (1)  
1) Detroit  
Macomb  
T3N, R12E, Sections 3-10, 15-22, & 27-34  
T3N, R13E, Sections 25, 35, & 36  
T3N, R14E, Sections 11-14 & 19-32  
T3N, R15E, Sections 7 and 18  
T4N, R12E, Sections 27-34  
Macomb County south of the T2N north  
township line  
Oakland  
T1N, R8E, Sections 1-36  
T1N, R9E, Sections 1-36  
T1N, R1OE, Sections 1-36  
T1N, R11E, Sections 1-36  
T2N, R8E, Sections 1-3, 10-16, & 19-36  
T2N, R9E, Sections 1-36  
T2N, R1OE, Sections 1-36  
T2N, R11E, Sections 1-36  
T3N, R8E, Sections 13-15, 20-29, & 33-36  
T3N, R9E, Sections 1-36  
T3N, R1OE, Sections 2-36  
T3N, R11E, Sections 1-5 & 7-36  
T4N, R9E, Sections 17, 19-22, & 26-36  
T4N, R1OE, Sections 1-3, 10-12, 14-16, 20-  
23, 25-29, & 31-35  
T5N, R1OE, Sections 22, 26-29, 34, & 35  
Washtenaw  
T2S, R5E, Sections 12-27 & 36 T2S,  
R6E, Sections 7-11 & 13-36 T2S,  
R7E, Sections 18, 19, & 29-36 T3S,  
R6E, Sections 1-6, 8-17, 23, & 24  
T3S, R7E, Sections 1-26  
10  
All areas except the following:  
T1S, R8E, Sections 5-8, 17-20, 30, & 31  
T2S, R8E, Sections 5-9, 16-21, & 28-30  
T3S, R8E, Sections 31-35  
Wayne  
T4S, R8E, Sections 2-36  
T4S, R9E, Sections 1-5 & 9-36  
T4S, R1OE, Sections 7, 8, 17, & 18  
2)Flint  
Genesee  
T6N, R5E, Sections 1-3  
T6N, R6E, Sections 1-6, 11-14, 24, & 25  
T6N, R7E, Sections 1-30  
T7N, R5E, Sections 34-36  
T7N, R6E, Sections 1-36  
T7N, R7E, Sections 1-36  
T7N, R8E, Sections 3-11, 14-19, 21, 22, and 30  
T8N, R5E, Sections 13-15, 22-27, & 34-36  
T8N, R6E, Sections 1, 2, 11-14, & 19-36  
T8N, R7E, Sections 5-11 & 13-36  
T9N, R6E, Sections 11, 14, 15, 22-27, 35, and  
36  
T9N, R7E, Sections 31 & 32  
3)Grand Rapids  
Kent  
T5N, R11W, Sections 4-8, 17, & 18  
T5N, R12W, Sections 1, 12, & 13  
T6N, R1OW, Sections 3-10, 15-21, & 28-33  
T6N, R11W, Sections 1-36  
T6N, R12W, Sections 1-36  
T7N, R1OW, Sections 28-35  
T7N, R11W, Sections 3-10, 15-23, & 25-36  
T7N, R12W, Sections 1-36  
T8N, R11W, Sections 13-16, 19-23, & 26-34  
T5N, R13W, Sections 4 & 5  
T6N, R13W, Sections 9-16, 21-29, 32, & 33  
Ottawa  
T5N, R2W, Sections 4, 5, 7-9, 15-18, 20-23,  
4)Lansing  
Clinton  
Eaton  
26-29, & 31-  
35  
T3N, R3W, Sections 1-3 & 9-12  
T4N, R3W, Sections 1-4, 9-16, 20-26, 35, and  
36  
T3N, R2W, Sections 1-12 14-16, 22, & 23  
T4N, R1W, Sections 2-11, 14-23, 26-29, & 33  
Ingham  
T4N, R2W, Sections 1-36  
(8) (1) Maps of affected areas may be reviewed and inspected at the Lansing office of the  
Air Quality Division of the department of environmental quality described in table 61 are  
available upon request.  
11  
TABLE 61-a  
List of counties referenced in R 336.1606 through R 336.1609  
Allegan  
Barry  
Bay  
Berrien  
Branch  
Calhoun  
Cass  
Clinton  
Eaton  
Genesee  
Gratiot  
Hillsdale  
Huron  
Ingham  
Ionia  
Jackson  
Kalamazoo  
Kent  
Muskegon  
Oakland  
Ottawa  
Saginaw  
St. Clair  
St. Joseph  
Sanilac  
Shiawassee  
Tuscola  
Van Buren  
Washtenaw  
Wayne  
Lapeer  
Lenawee  
Livingston  
Macomb  
Marquette  
Midland  
Monroe  
Montcalm  
R 336.1607 Loading gasoline into existing stationary vessels of more than 2,000-gallon  
capacity at loading facilities.  
Rule 607. (1) After June 30, 1980, iIt is unlawful for a person to load, or allow the  
loading of, gasoline from a delivery vessel into any existing stationary vessel of more  
than 2,000-gallon capacity located at a gasoline-loading facility, in any county listed in  
table 61-a, unless the stationary vessel is equipped with a permanent submerged fill pipe.  
(2) After June 30, 1981, it is unlawful for a person to load, or allow the loading of  
gasoline from a delivery vessel into any existing stationary vessel of more than 2,000-  
gallon capacity located at a gasoline-loading facility outside of any county listed in table  
61-a, unless the stationary vessel is equipped with a permanent submerged fill pipe.  
(23) After December 31, 1982, iIt is unlawful for a person to load, or allow the loading  
of, gasoline from a delivery vessel into any existing stationary vessel of more than  
2,000-gallon capacity located at either of the following loading facilities, unless the  
stationary vessel is controlled by a vapor balance system, or an equivalent control  
system approved by the department:  
(a) A loading facility located in any area listed in table 61.  
(b) A loading facility located in the 2015 ozone nonattainment area.  
(c)A loading facility which is located outside both the 2015 ozone nonattainment  
area and in any area that is not listed in table 61 and which that delivers gasoline to a  
gasoline-dispensing facility subject to R 336.1606(32) and (4) or R 336.1703(2) and (3).  
(3) Proper operation of tThe vapor balance system as required in subrule (2) of this  
rule is when shall capture displaced gasoline vapors and air are captured by means of a  
vaportight vapor tight collection line and shall be that is designed to return not less than  
90%, by weight, of the displaced gasoline vapor from the stationary vessel to the delivery  
vessel.  
(4) Any stationary vessel that is subject to the provisions of subrule (32) of this rule  
shall must be equipped, maintained, or controlled with all of the following:  
12  
(a) An interlocking system or procedure to ensure that the vaportight vapor tight  
collection line is connected before any gasoline can be loaded.  
(b) A device to ensure that the vaportight vapor tight collection line must shall close  
upon disconnection so as to prevent the release of gasoline vapor.  
(c) Pressure-vacuum relief valves on above ground stationary vessels with a minimum  
pressure valve setting of 8 ounces, if that setting does not exceed the container's  
maximum pressure rating.  
(5) Any delivery vessel subject to subrule (32) of this rule must shall be vaportight  
vapor tight.  
(6) A person who is responsible for the operation of all control measures required by  
this rule shall develop written procedures for the operation of all such control measures.  
The procedures shall must be posted in an accessible, conspicuous location near the  
stationary vessel.  
(7) An existing stationary vessel installed or modified after July 1, 1979, and before  
March 1, 2023, at a gasoline loading facility that is not subject to the provisions of  
subrule (2) of this rule, must be constructed in a manner that allows the vessel to be  
retrofitted, according to subrules (2) and (4) of this rule.  
R 336.1608 Loading gasoline into delivery vessels at existing loading facilities handling  
less than 5,000,000 gallons per year.  
Rule 608. (1) After June 30, 1980, iIt is unlawful for a person to load, or allow the  
loading of, gasoline from a stationary vessel into any delivery vessel located at an  
existing gasoline-loading facility, which is located in any county listed in table 61-a and  
which has a throughput of less than 5,000,000 gallons of gasoline per year, unless the  
delivery vessel is filled by a submerged fill pipe.  
(2) After June 30, 1981, it is unlawful for a person to load, or allow the loading of,  
gasoline from a stationary vessel into any delivery vessel located at an existing  
gasoline-loading facility which is located outside of any county listed in table 61-a and  
which has a throughput of less than 5,000,000 gallons of gasoline per year, unless the  
delivery vessel is filled by a submerged fill pipe.  
(23) After December 31, 1982, iIt is unlawful for a person to load, or allow the loading  
of, gasoline from a stationary vessel into any delivery vessel located at either any of the  
following loading facilities having a throughput of less than 5,000,000 gallons per year,  
unless the delivery vessel is controlled by a vapor balance system, or an equivalent  
control system approved by the department:  
(a) An existing loading facility located in any area listed in table 61.  
(b) An existing loading facility located in the 2015 ozone nonattainment area.  
(c) An existing loading facility which is located outside both the 2015 ozone  
nonattainment area and in any area that is not listed in table 61 and which that delivers  
gasoline to a gasoline-dispensing facility subject to R 336.1606(32) and (4) or R  
336.1703(2) and (3).  
(3) The provisions of subrule (2) of this rule do not apply to the following gasoline-  
loading facilities, provided the facility was installed before July 1, 1979, and has a  
throughput of less than 1,000,000 gallons of gasoline per year:  
(a) An existing loading facility located in any area listed in table 61.  
13  
(b) An existing loading facility located outside any area listed in table 61 which  
delivers gasoline to a gasoline-dispensing facility subject to R 336.1606(2).  
(4) Proper operation of tThe vapor balance system as required in subrule (2) of this  
rule is when shall capture displaced gasoline vapor and air are captured by means of a  
vaportight vapor tight collection line and shall be that is designed to return not less than  
90%, by weight, of the displaced gasoline vapor from the delivery vessel to the stationary  
vessel.  
(54) Any delivery vessel that is loaded at a facility subject to subrule (32) of this rule  
shall must be equipped, maintained, or controlled with all of the following:  
(a) An interlocking system or procedure to ensure that the vaportight vapor tight  
collection line is connected before any gasoline can be loaded.  
(b) A device to ensure that the vaportight vapor tight collection line will closes upon  
disconnection so as to prevent the release of gasoline vapor.  
(c) A device or procedure to accomplish complete drainage before the loading device is  
disconnected or to prevent liquid drainage from the loading device when not in use.  
(d) Pressure-vacuum relief valves that are vaportight vapor tight and set to prevent the  
emission of displaced gasoline vapor during the loading of the delivery vessel, except  
under emergency conditions.  
(e) Hatch openings that are kept closed and vaportight vapor tight during the loading  
of the delivery vessel.  
(65) Any stationary vessel at a facility subject to subrule (32) of this rule shall must be  
vaportight vapor tight.  
(76) A person who is responsible for the operation of all control measures required by  
this rule shall develop written procedures for the operation of all such control measures.  
The procedures shall must be posted in an accessible, conspicuous location near the  
loading device.  
(7) The provisions of subrule (3) of this rule shall not apply to any gasoline-loading  
facility that has a throughput of less than 1,000,000 gallons of gasoline per year.  
R 336.1609 Loading delivery vessels with organic compounds having true vapor  
pressure of more than 1.5 psia at existing loading facilities handling 5,000,000 or more  
gallons of such the compounds per year.  
Rule 609. (1) After June 30, 1981, it is unlawful for a person to load, or allow the  
loading of, any organic compound that has a true vapor pressure of more than 1.5  
psia at actual conditions from any stationary vessel into any delivery vessel located  
at the following existing loading facilities that are outside any county listed in table  
61-a and have a throughput of 5,000,000 or more gallons of the compounds per year,  
unless the delivery vessel is filled by a submerged fill pipe:  
(a) An existing facility installed outside the counties listed in table 61-a before July  
1, 1979.  
(b) An existing facility installed or modified in this state after July 1, 1979, and  
before March 1, 2023.  
(12) After December 31, 1982, Iit is unlawful for a person to load, or allow the loading  
of, any organic compound that has a true vapor pressure of more than 1.5 psia at actual  
conditions from any stationary vessel into any delivery vessel located at the following an  
existing loading facilityies which is in any county listed in table 61-a and which hasve a  
14  
throughput of 5,000,000 or more gallons of such the compounds per year, unless the  
such delivery vessel is controlled by a vapor recovery system as described in subrule (3)  
of this rule:  
(a) An existing facility installed in counties listed in table 61-a before July 1, 1979.  
(b) An existing facility installed or modified in this state after July 1, 1979, and  
before March 1, 2023.  
(3) Proper operation of the vapor recovery system as required by subrule (2) of this  
rule is when that captures all displaced organic vapor and air are captured by means of  
a vapor-tight vapor tight collection line and the system recovers the organic vapor such  
that emissions to the atmosphere do not exceed 0.7 pounds of organic vapor per 1,000  
gallons of organic compounds loaded.  
(43) Any delivery vessel located at a facility that is subject to the provisions of subrule  
(2) of this rule must shall be equipped, maintained, or controlled with all of the  
following:  
(a) An interlocking system or procedure to ensure that the vapor-tight vapor tight  
collection line is connected before any organic compound can be loaded.  
(b) A device to ensure that the vapor-tight vapor tight collection line shall closes upon  
disconnection so as to prevent the release of organic vapor.  
(c) A device to accomplish complete drainage before the loading device is  
disconnected, or a device to prevent liquid drainage from the loading device when not in  
use.  
(d) Pressure-vacuum relief valves that are vapor-tight vapor tight and set to prevent the  
emission of displaced organic vapor during the loading of the delivery vessel, except  
under emergency conditions.  
(e) Hatch openings that are kept closed and vapor-tight vapor tight during the loading  
of the delivery vessel.  
(54) A person who is responsible for the operation of all control measures required by  
this rule shall develop written procedures for the operation of all such control measures.  
Such The procedures shall must be posted in an accessible, conspicuous location near the  
loading device.  
(65) The provisions of subrule (2) of this rule do shall not apply to the loading of the  
following:  
(a) Ccrude oil or condensate into delivery vessels at production facilities if such  
loading is accomplished with a submerged fill pipe after June 30, 1981.  
(b) Butane, isobutane, propane, propylene, butylene, C3-C4 mixtures, and  
mixtures of these organic compounds that comply with the following specified  
requirements:  
(i) Utilizes a pressurized loading system that does not allow organic vapor to be  
discharged from the delivery vessel during loading.  
(ii) Utilizes a device to ensure the loading line closes upon disconnection to  
prevent release of organic vapor.  
(iii) Ensures that all pressure-vacuum relief valves are vapor-tight and set to  
prevent the emission of organic vapor during the loading of the delivery vessel,  
except under emergency conditions.  
(iv) All hatch openings are kept closed and vapor-tight during the loading of the  
delivery vessel.  
15  
(v) Written procedures for the operation of the loading device are posted in an  
accessible, conspicuous location near the loading device.  
R 336.1610 Existing coating lines; emission of volatile organic compounds from existing  
automobile, light-duty truck, and other product and material coating lines.  
Rule 610. (1) A person shall not cause or allow the emission of volatile organic  
compounds from the coating of automobiles and light-duty trucks, from any existing  
coating line, in excess of the applicable emission rates shown in table 62.  
(2) A person shall not cause or allow the emission of volatile organic compounds from  
the coating of any of the following, from an existing coating line, in excess of the  
applicable emission rates shown in column A of table 63 or the equivalent emission rates  
in column B of table 63:  
(a) Cans.  
(b) Coils.  
(c) Large appliances.  
(d) Metal furniture.  
(e) Magnet wire.  
(f) The nonmetallic surfaces of fabrics, vinyl, or paper.  
(3) Subrule (2) of this rule notwithstanding, and as an alternative to the allowable  
emission rate established by table 63, the existing paper coating lines at Fletcher pPaper  
cCompany of Alpena may comply with subrule (2) of this rule by not exceeding a  
volatile organic compound emission rate of 180 tons per calendar year and 30 tons per  
calendar month.  
(4) A person who is responsible for the operation of a coating line that is subject to this  
rule shall obtain current information and keep records necessary for the determination of  
compliance with this rule, as required in R 336.2041.  
(5) For each coating line, compliance with the emission limits specified in table 62 and  
table 63 shall must be based upon all of the following provisions:  
(a) For prime coat operations that utilize an electrodeposition process in automobile and  
light-duty truck coating lines that are regulated under table 62, compliance must shall be  
based upon all coatings that belong to the same coating category that is used during each  
calendar month averaging period. For all other coatings, compliance must shall be based  
upon the volume-weighted average of all coatings which that belong to the same coating  
category and which are used during each calendar day averaging period. The department  
may specifically authorize compliance to be based upon a longer averaging period, which  
shall must not be more than 1 calendar month.  
(b) If coatings that belong to more than 1 coating category are used on the same coating  
line during the specified averaging period, then compliance must shall be determined  
separately for each coating category.  
(c) The information and records as required by subrule (4) of this rule.  
(6) Compliance with the emission limits specified in this rule must shall be determined  
using the applicable method described in the following subdivisions:1 of the following  
methods, as applicable:  
(a) For the prime-electrodeposition process and for the final repair emission limits  
specified in table 62, the method described in either R 336.2040(12)(a) if the coating line  
16  
does not have an add-on emissions control device or R 336.2040(12)(b) if the coating line  
has 1 or more add-on emissions control devices.  
(b) For the primer surfacer and topcoat emission limits specified in table 62,  
compliance must shall be determined by the methodology described in the publication  
entitled "Protocol for Determining the Daily Volatile Organic Compound Emission Rate  
of Automobile and Light-duty Truck Topcoat Operations,", EPA-450/3-88-018 EPA-  
453/R-08-002, adopted by reference in R 336.1902. References to topcoat operations in  
this publication shall also apply to primer surfacer lines, with the following added  
provisions:  
(i) Unless specifically included in the adopted publication, if an anti-chip, color-in-  
prime, blackout, or spot primer coating is applied as part of either a primer surfacer or  
topcoat coating operation, then the anti-chip, color-in-prime, blackout, or spot primer  
coating must shall be included in the transfer efficiency tests for that coating operation,  
conducted according to section 18 or 19 of the adopted publication, and the transfer  
efficiency values in section 20 of the adopted publication shall must not be used.  
(ii) If spot primer is applied as part of a primer surfacer coating operation, then the  
daily usage of spot primer, as calculated in section 8 of the adopted publication, may be  
derived from monthly usage of spot primer based upon the number of vehicles processed  
in the primer surfacer operation each day. If an add-on emissions control device is used  
on the coating line application area to achieve compliance with the primer surfacer or  
topcoat emission limits specified in table 62, then the capture efficiency must shall be  
determined in accordance with R 336.2040(10).  
(c) For the emission limits specified in column B of table 63, the method described in  
either R 336.2040(12)(e) if the coating line does not have an add-on emissions control  
device or R 336.2040(12)(f) if the coating line has 1 or more add-on emissions control  
devices.  
(d) For the emission limits specified in column A of table 63, the method described in  
either R 336.2040(12)(a) if the coating line does not have an add-on emissions control  
device or R 336.2040(12)(b) if the coating line has 1 or more add-on emissions control  
devices.  
(7) The provisions of this rule, with the exception of except for the provisions in  
subrule (4) of this rule, do not apply to coating lines that are within a stationary source  
and that have a combined actual emission rate of volatile organic compounds of less than  
100 pounds per day or 2,000 pounds per month as of November 4, 1999. If the combined  
actual emission rate equals or is more than 100 pounds per day for a subsequent day or  
2,000 pounds per month for a subsequent month, then this rule shall permanently apply  
applies to the coating lines.  
(8) A person may exclude low-use coatings that total 55 gallons or less per rolling 12-  
month period at a stationary source from the provisions of this rule, except for subrule (4)  
of this rule.  
(9) Between November 1 and March 31, a person may discontinue the operation of a  
natural gas-fired afterburner that is used to achieve compliance with the emission limits  
in this rule, unless the afterburner is used to achieve compliance with, or is required by,  
any of the following:  
(a) Any other Another provision of these rules.  
(b) A permit to install.  
17  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department.  
(10) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 under subrule (9) of this rule, then both of the following  
provisions shall apply between November 1 and March 31:  
(a) All other provisions of this rule, except for the emission limits, shall remain in  
effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
(11) Tables 62 and 63 read as follows:  
18  
Table TABLE 62  
Volatile organic compound emission limits for existing automobile and light-duty truck  
coating lines  
Coating Category  
Prime-electrodeposition process  
Primer surfacer3  
Topcoat  
Emission Limit  
1.21  
14.92  
14.92  
Final repair  
4.821  
1Pounds of volatile organic compounds per gallon of coating, minus water, as applied.  
2Pounds of volatile organic compounds per gallon of applied coating solids.  
3The primer surfacer or topcoat coating category would include an anti-chip, blackout, or spot primer  
coating if this coating is applied as part of the primer surfacer or topcoat coating operation.  
Table TABLE 63  
Volatile organic compound emission limits for existing coating lines  
Coating Category  
Metallic surfaces  
Coating of cans  
Column A1  
Column B2  
Sheet basecoat (exterior and interior and overvarnish; 2.8  
2-piece  
Can exterior (basecoat and overvarnish)  
2- and 3-piece can interior body spray; 2-piece can  
interior end (spray or roll coat)  
3-piece can side-seam  
4.2  
5.5  
3.7  
2.6  
2.8  
3.0  
1.7  
End sealing compound  
Coating of coils  
Coating of large appliances3  
Coating of metal furniture3  
Insulation of magnet wire  
Nonmetallic surfaces  
7.5  
8.4  
Coating of fabric  
Coating of vinyl  
Coating of paper  
2.9  
3.8  
2.9  
1Pounds of volatile organic compounds emitted per gallon of coating, minus water, as applied.  
2Pounds of volatile organic compounds emitted per gallon of applied coating solids. The purpose of  
column B emission limits is to allow credit for transfer efficiencies greater than the baseline transfer  
efficiency. Note: department approval of the transfer efficiency test method is required.  
3The allowable emission rate does not apply to coatings that are used for the repair of scratches and nicks.  
(12) A coating line subject to R 336.1610a does not need to meet the provisions of R  
336.1610.  
Commented [GJ1]: Does this mean sources that are  
excluded from 610a are also excluded from 610? If so, can  
this be revised to say it also includes those that are exempt  
from 610a are also exempt from 610?  
R 336.1610a Existing coating lines; emission of volatile organic compounds from  
existing automobile, light-duty truck; and paper, film, and foil; cans, coils, and  
19  
fabrics; insulation of magnet wire; metal furniture coating lines in 2015 ozone  
nonattainment areas.  
Rule 610a. (1) As used in this rule:  
(a) “Automobile” means a motor vehicle designed to carry up to 8 passengers.  
Automobile does not include vans, sport utility vehicles, or motor vehicles designed  
primarily to transport light loads of property.  
(b) “Coatings of paper, film, and foil” means materials applied onto or  
impregnated into a substrate for decorative, protective, or functional purposes,  
including, but not limited to, solvent-borne coatings, water-borne coatings,  
adhesives, wax coatings, wax laminations, extrusion laminations, 100% solid  
adhesives, UV cured coatings, electron beam cured coatings, hot melt coatings, and  
cold seal coatings.  
(c) Occurrence” means the application of the combination of coatings that  
constitute a final repair coat for a single automobile or light-duty truck.  
(2) Except as provided in subrule (3) of this rule, the provisions of this rule apply to  
a person causing or allowing the emission of any volatile organic compound from  
the following existing coating lines at a facility located in the 2015 ozone  
nonattainment areas:  
(a) Automobile and light-duty truck assembly coatings product category, as  
defined in R 336.1103.  
(b) The coating of bodies or body parts, or both, for new heavier vehicles at an  
automobile and light-duty truck assembly facility or a heavier vehicle assembly  
facility, that meets the applicability requirements of R 336.1621a and has elected to  
comply with the requirements of this rule instead of the requirements of R  
336.1621a.  
(c) Metal furniture coating operations.  
(d) Paper, film, and foil surface coating operations.  
(3) The provisions of this rule, as specified, do not apply to the following:  
(a) With the exception of the requirements in subrule (6) of this rule, the following  
coating lines at a stationary source that have a combined actual emission rate of  
volatile organic compounds, including related cleaning activities, of less than 15  
pounds per calendar day before consideration of controls. If the combined actual  
emission rate equals or is more than 15 pounds per calendar day for a subsequent  
day, then this rule permanently applies to these coating lines:  
(i) Automobile and light-duty truck assembly coating lines that are within an  
automobile and light-duty truck assembly facility.  
(ii) Metal furniture coating lines at a stationary source.  
(iii) Cans, coils, fabrics, and insulation of magnet wire coating lines at a stationary  
source.  
(b) With the exception of the requirements in subrule (6) of this rule, low-use  
coatings that have a combined total of less than 55 gallons per rolling 12-month  
period at a stationary source.  
(c) Automobile and light-duty truck coatings used at plastic or composites molding  
facilities.  
20  
(d) The limits in table 64-a of this rule do not apply to automobile and light-duty  
truck coating materials that are supplied in containers with a net volume of 16  
ounces or less, or a net weight of 1 pound or less.  
(e) The coating of metallic surfaces that are subject to R 336.1621 or R 336.1621a.  
(f) With the exception of the requirements in subrules (5) and (6) of this rule,  
paper, film, and foil surface coating lines within a stationary source that have a  
potential to emit less than 25 tons per year of volatile organic compounds before  
controls. If the potential to emit equals or is more than 25 tons per year of volatile  
organic compounds from paper, film, and foil coatings for a subsequent year, then  
this rule permanently applies to the paper, film, and foil surface coating lines.  
(g) Facilities subject to R 336.1624 or R 336.1635.  
(h) Coatings performed on, in, or off-line with any screen or digital printing press.  
(i) Size presses and on-machine coaters on paper making machines applying sizing  
or water-based clays.  
(j) Paper, film, or foil materials used to form unsupported substrates, such as  
calendaring of vinyl, blown film, cast film, extruded film, and co-extruded film.  
(k) Coatings performed at research and development or prototype facilities.  
(4) A person subject to this rule shall not cause or allow the emission of any volatile  
organic compound, unless the following provisions are met:  
(a) An automobile and light-duty truck coating facility must not cause or allow the  
emission of volatile organic compounds from the coating of automobiles and light-  
duty trucks or miscellaneous materials, as outlined within table 64-a, from any  
existing coating line as defined in R 336.1103, in excess of the applicable emission  
rates shown in table 64-a.  
(b) A person subject to this rule shall not cause or allow the emission of volatile  
organic compounds from the coating of metal furniture, from an existing coating  
line, in excess of the applicable emission rate as shown in column A of table 64-b or  
the equivalent emission rates in column B of table 64-b.  
(c) A person subject to this rule shall meet an overall volatile organic compound  
control efficiency of 90% for each existing coating line at a paper, film, and foil  
stationary source. Alternatively, a person shall not cause or allow the emission of  
volatile organic compounds from the coating of paper, film, and foil, from an  
existing coating line, in excess of the applicable emission rate as shown in column A  
of table 64-d or the equivalent emission rates in column B of table 64-d.  
(d) For each coating line, compliance with the emission limits specified in table 64-  
a, table 64-b, and table 64-d is based upon all of the following provisions:  
(i) For prime coat operations that utilize an electrodeposition process in  
automobile and light-duty truck coating lines that are regulated under table 64-a,  
compliance is based on all coatings that belong to the same coating category that is  
used during each calendar month averaging period. For all other coatings,  
compliance is based on the volume-weighted average of all coatings that belong to  
the same coating category and are used during each calendar day averaging period.  
Under R 336.1602(2), the department may specifically authorize compliance to be  
based on a longer averaging period, not to exceed more than 1 calendar month.  
21  
(ii) If coatings that belong to more than 1 coating category are used on the same  
coating line during the specified averaging period, then compliance is determined  
separately for each coating category.  
(iii) The information and records as required by subrule (5) of this rule.  
(e) Compliance with the emission limits specified in this rule must be determined  
using the applicable method described in the following paragraphs:  
(i) For the prime-electrodeposition process emission limit specified in table 64-a,  
the method described in either R 336.2040(12)(a) if the coating line does not have an  
add-on emissions control device or R 336.2040(12)(b) if the coating line has 1 or  
more add-on emissions control devices.  
(ii) For the primer surfacer, topcoat, and combined primer surfacer and topcoat  
coating category emission limits specified in table 64-a, compliance must be  
determined by the methodology described in the publication entitled “Protocol for  
Determining the Daily Volatile Organic Compound Emission Rate of Automobile  
and Light-duty Truck Topcoat Operations,EPA-453/R-08-002, adopted by  
reference in R 336.1902. References to topcoat operations in this publication also  
apply to primer surfacer lines, with the following added provisions:  
(A) Unless specifically included in the adopted publication, if an anti-chip, color-  
in-prime, blackout, or spot primer coating is applied as part of either a primer  
surfacer or topcoat coating operation, then the anti-chip, color-in-prime, blackout,  
or spot primer coating is included in the transfer efficiency tests for that coating  
operation, conducted according to section 18 or 19 of the adopted publication, and  
the transfer efficiency values in section 20 of the adopted publication must not be  
used.  
(B) When spot primer is applied as part of a primer surfacer coating operation,  
then the daily usage of spot primer, as calculated in section 8 of the adopted  
publication, may be derived from monthly usage of spot primer based upon the  
number of vehicles processed in the primer surfacer operation each day. If an add-  
on emissions control device is used on the coating line application area to achieve  
compliance with the primer surfacer or topcoat emission limits specified in table 64-  
a, then the capture efficiency must be determined in accordance with R  
336.2040(10).  
(iii) For the final repair coating category emission limit specified in table 64-a,  
compliance must be on an occurrence weighted average basis, calculated in  
accordance with the following equation, in which clear coatings have a weighting  
factor of 2 and all other coatings have a weighting factor of 1:  
풊=ퟏ  
ퟐ푽푶푪  
푽푶푪  
풄풄  
VOCtot  
=
풏+ퟐ  
Where:  
VOCtot = Total volatile organic compound content of all coating, as applied, on an  
occurrence weighted average basis, and used to determine compliance with this  
paragraph.  
i = subscript denoting a specific coating applied.  
22  
n = Total number of coatings applied in the final repair operation, other than clear  
coatings  
VOCcc = The volatile organic compound content, as applied, of the clear coat used  
in the final repair operation.  
VOCi = The volatile organic compound content of each coating used in the final  
repair operation, as applied, other than clear coatings.  
(iv) For determining the volatile organic compounds content of coatings, other  
than reactive adhesives, used at automobile and light-duty truck coating assembly  
facilities specified in table 64-a, compliance must be determined in accordance with  
R 336.2040(5).  
(v) For determining the volatile organic compounds content of reactive adhesives  
used at automobile and light-duty truck coating assembly facilities, specified in table  
64-a, compliance must be determined by the procedure described in appendix A of  
40 CFR part 63, subpart PPPP, adopted by reference in R 336.1902.  
(vi) As an alternative for the compliance methods in subrules (4)(iv) and (4)(v) of  
this rule, automobile and light-duty truck coating assembly facilities may use the  
manufacturer’s formulation data. If there is a disagreement between the  
manufacturer’s formulation data and the results of a subsequent test, the  
department shall use the test method results unless the facility can make a  
determination approved by the department that the manufacturer’s formulation  
data are correct.  
(vii) For the emission limits specified in column A of table 64-b, table 64-c, and  
table 64-d, the method described in either R 336.2040(12)(a) if the coating line does  
not have an add-on emissions control device or R 336.2040(12)(b) if the coating line  
has 1 or more add-on emissions control devices.  
(viii) For the emission limits specified in column B of table 64-b and table 64-d,  
the method described in either R 336.2040(12)(e) if the coating line does not have an  
add-on emissions control device or R 336.2040(12)(f) if the coating line has 1 or  
more add-on emissions control devices.  
(f) A person responsible for the following coating lines shall make a determination  
of compliance with these emission limits using the method specified in subrule (3)(e)  
of this rule and submit a copy of this determination and supporting data to the  
department by the following specified date, as applicable:  
(i) For primer surfacer and topcoat coating lines, no later than 6 months after the  
effective date of this rule.  
(ii) Metal furniture coating lines that are subject to the equivalent emission rates  
in column B of table 64-b, no later than 6 months after the effective date of this rule.  
TABLE 64-a  
Volatile organic compound emission limits for existing automobile and light-duty  
truck coating lines and miscellaneous materials used at automobile and light-duty  
truck assembly coating facilities.  
23  
Coating Category  
VOC Emission Limit  
Prime-electrodeposition process  
(EDP) (including application area,  
spray/rinse stations, and curing  
oven)  
When solids  
When 0.040≤  
When  
RT≤0.040:  
turnover ratio RT≤0.160:  
(RT)≥0.16:  
0.71  
(0.084 x 3500.160-R  
No VOC  
emission  
limit.  
T
x 8.34)1  
Primer surfacer4 (including  
application area, flash-off area, and  
oven)  
Topcoat (including application area, 12.02  
flash-off area, and oven)  
Final repair operations  
Combined primer-surfacer and  
topcoat  
12.02  
4.83  
12.02  
Miscellaneous Materials Used at Automobile and Light-Duty Truck Assembly Coating  
Facilities  
Coating Category  
lb VOC/gal coating  
(minus water, as  
applied)  
g VOC/L of coating  
(minus water and  
exempt compounds,  
as applied)  
900  
250  
650  
650  
650  
200  
650  
650  
200  
750  
700  
Glass Bonding Primer5  
Adhesive5  
7.53  
2.13  
5.43  
5.43  
5.43  
1.73  
5.43  
5.43  
1.73  
6.33  
5.83  
Cavity Wax5  
Sealer5  
Deadener5  
Gasket/Gasket sealing material5  
Underbody Coating5  
Trunk interior coating5  
Bedliner5  
Weatherstrip adhesive5  
Lubricating wax/compound5  
1 Pounds of volatile organic compounds per gallon of applied coating solids.  
2 Pounds of volatile organic compounds per gallon of applied coating solids on a daily weighted  
average basis as determined by following the procedures in the “Protocol for determining the Daily  
Volatile Organic Compound Emission Rate of Automobile and Light-Duty Truck Topcoat  
Operations” (EPA-453/R-08-002).  
3 Pounds of volatile organic compounds per gallon of coating, minus water, as applied.  
4 The primer surfacer or topcoat coating category would include an anti-chip, blackout, or spot  
primer coating if this coating is applied as part of the primer surfacer or topcoat coating operation.  
5 VOC emission limits must not be applied to materials supplied in containers with a net volume of  
16 ounces or less, or a net weight of 1 pound or less.  
24  
TABLE 64-b  
Volatile organic compound emission limits for existing metal furniture coating lines.  
Coating Type  
Column A1  
Baked Air Dried Baked  
Column B2  
Air Dried  
General, 1 Component  
General, Multi-Component  
Extreme High Gloss  
Extreme Performance  
Heat Resistant  
Metallic  
Pretreatment Coatings  
Solar Absorbent  
2.3  
2.3  
3.0  
3.0  
3.0  
3.5  
3.5  
3.0  
2.3  
2.8  
2.8  
3.5  
3.5  
3.5  
3.5  
3.5  
3.3  
3.3.  
5.1  
5.1  
5.1  
6.7  
6.7  
5.1  
3.3  
4.5  
4.5  
6.7  
6.7  
6.7  
6.7  
6.7  
1 Pounds of volatile organic compounds emitted per gallon of coating, minus water, as applied.  
2 Pounds of volatile organic compounds emitted per gallon of applied coating solids. The purpose of  
column B emission limits is to allow credit for transfer efficiencies greater than the baseline transfer  
efficiency. Note: department approval under R 336.1602(2) of the transfer efficiency test method is  
required.  
TABLE 64-c  
Volatile organic compound emission limits for existing cans, coils, fabrics, and  
insulation of magnet wire coating lines.  
Coating Category  
Column A1  
Coating of cans  
Sheet basecoat (exterior and interior) and overvarnish; 2-piece  
Can exterior (basecoat and overvarnish)  
2- and 3-piece can interior body spray; 2-piece can interior end (spray  
or roll coat)  
2.8  
4.2  
3-piece can side-seam  
End sealing compound  
Coating of coils  
Coating of fabric  
Insulation of magnet wire  
1 Pounds of volatile organic compounds emitted per gallon of coating, minus water, as applied.  
5.5  
3.7  
2.6  
2.9  
1.7  
TABLE 64-d  
Volatile organic compound emission limits for paper, film, and foil surface coating  
and pressure sensitive tape and label surface coating.  
Coating Category  
Column A1  
Column B2  
Paper, Film, and Foils Surface Coating  
(not including pressure sensitive type and  
label)  
0.08  
0.40  
25  
Pressure Sensitive Tape and Label Surface 0.067  
Coating  
0.20  
1 Pounds of volatile organic compounds emitted per gallon of coating, minus water, as applied.  
2 Pounds of volatile organic compounds emitted per gallon of applied coating solids. The purpose of  
column B emission limits is to allow credit for transfer efficiencies greater than the baseline transfer  
efficiency. Note: department approval of the transfer efficiency test method is required.  
(5) A person subject to this rule shall comply with the following work practices for  
each coating line subject to this rule, unless the source has an equivalent work  
practice plan established for coatings in a post-1990 federal standard found in 40  
CFR part 63 with an equivalent subpart approved by the department. The person  
responsible for a surface coating operation subject to this rule shall develop written  
procedures for compliance with the following provisions:  
(a) Store all volatile organic compound-containing coatings, thinners, and cleaning  
materials, including used shop towels, in closed containers.  
(b) Minimize spills of volatile organic compound-containing coatings, thinners,  
and cleaning materials.  
(c) Clean up spills immediately.  
(d) Convey any coatings, thinners, and cleaning materials in closed containers or  
pipes.  
(e) Close mixing vessels that contain volatile organic compound coatings and other  
materials except when specifically in use.  
(f) Minimize usage of solvents during cleaning of storage, mixing, and conveying of  
equipment.  
(6) A person responsible for the operation of a coating line that is subject to this  
rule shall obtain current information and keep records that are necessary for the  
determination of compliance with the provisions of this rule, as required in R  
336.2041.  
R 336.1611 Existing cold cleaners.  
Rule 611. (1) A person shall not operate an existing cold cleaner unless all of the  
provisions of subrules (2) to (4) of this rule are met or unless an equivalent control  
method is approved by the department under R 336.1602(2).  
(2) A person shall not operate an existing cold cleaner unless all of the following  
conditions are met:  
(a) A cover shall must be installed and shall must be closed when parts are not being  
handled in the cleaner.  
(b) A device shall must be available for draining cleaned parts, and the parts shall must  
be drained for not less than 15 seconds or until dripping ceases.  
(c) Waste organic solvent shall must be stored only in closed containers, unless the  
stored solvent is demonstrated to be a safety hazard and is disposed of so that not more  
than 20%, by weight, is allowed to evaporate into the atmosphere.  
(3) A person who is responsible for the operation of a cold cleaner shall develop written  
procedures for compliance with the provisions of this rule. The procedures shall must be  
posted in an accessible, conspicuous location near the cold cleaner.  
26  
(4) The provisions of this rule do not apply to cold cleaners that are subject to the  
provisions of 40 C.F.R. Part 63, Subpart T, “National Emission Standards for  
Halogenated Solvent Cleaning,40 CFR part 63, subpart T, adopted by reference in R  
336.1902.  
R 336.1618 Use of cutback or emulsified paving asphalt.  
Rule 618. (1) After May 1, 2012, aA person shall not manufacture, mix, store, use, or  
apply cutback or emulsified paving asphalt, from May 1 to September 30 March 1 to  
October 31, unless the cutback or emulsified paving asphalt contains no greater than 3%  
volatile organic compounds by volume, which is equivalent to 6.0 milliliters of oil  
distillate, from a 200 milliliters sample, at 500 degrees Fahrenheit as determined by a test  
method in subrule (2) of this rule. This rule applies is applicable to both existing and new  
sources as defined by the dates in R 336.1601(ca)(i) and R 336.1701.  
(2) Compliance with subrule (1) of this rule shall must be determined by 1 of the  
following test methods:  
(a) ASTM Method D6997, Standard Test Methods and Practice for Distillation of  
Emulsified Asphalts, adopted by reference in R 336.1902.  
(b) AASHTO T59 Standard Method of Test for Emulsified Asphalts, adopted by  
reference in R 336.1902.  
(c) ASTM Method D402, Standard Test Method Ffor Distillation of Cutback Asphaltic  
(Bituminous) Products, adopted by reference in R 336.1902.  
(d) AASHTO T78, Standard Method of Test for Cutback Asphaltic Products, adopted  
by reference in R 336.1902.  
(3) Any person subject to this rule shall maintain records of the manufacture, mixing,  
storage, use, or application of any cutback or emulsified paving asphalt containing  
volatile organic compounds during the period May 1 to September 30 March 1 to  
October 31. The records shall must include information on the volatile organic  
compound content documented in the product data sheets or material safety data sheets.  
The records must shall be available to any representative of the department during  
normal business hours, and copies must shall be provided to the department upon  
request.  
(4) The following definitions apply to this rule and supersede any similar definitions in  
R 336.1103:.As used in this rule:  
(a) “Asphalt” means a dark-brown to black solid, liquid, or semisolid cementitious  
material composed primarily of bitumens that occur naturally or are obtained as a residue  
of petroleum refining.  
(b) “Cutback paving asphalt” means asphalt that has been liquefied by blending with an  
organic solvent and that is used for the purpose of paving or repairing, or paving and  
repairing, a road surface.  
(c) “Emulsified paving asphalt” means asphalt that has been liquefied by mixing with  
water and an emulsifying agent and that is used for the purpose of paving or repairing, or  
paving and repairing, a road surface.  
R 336.1620 Emission of volatile organic compounds from existing interior flat wood  
paneling coating lines.  
27  
Rule 620. (1) As used in this rule, coating of interior flat wood panelingmeans  
the factory-finished coating of flat products that are constructed of wood, and are  
intended for use as interior paneling. Coating of interior flat wood paneling does not  
include the coating of flat wood products intended for use as exterior siding,  
tileboard, cabinets, or furniture components.  
(21) A person shall not cause or allow the emission of volatile organic compounds from  
the coating of interior flat wood paneling from any existing coating line in excess of the  
applicable emission rates as follows:  
(a) Six pounds per 1,000 square feet of coated finished product from printed interior  
panels made of hardwood, plywood, or thin particle board, regardless of the number of  
coats applied.  
(b) Twelve pounds per 1,000 square feet of coated finished product from natural finish  
hardwood plywood panels, regardless of the number of coats applied.  
(c) Ten pounds per 1,000 square feet of coated finished product from class II finishes  
on hardboard panels, regardless of the number of coats applied.  
(32) A person who is responsible for the operation of a coating line that is subject to this  
rule shall obtain current information, and keep daily records necessary, for the  
determination of compliance with this rule, as required in R 336.2041.  
(43) For each coating line, compliance with the emission limits specified in this rule  
shall must be based upon all of the following:  
(a) The volume-weighted average of all coatings which that belong to the same coating  
category and which are used during each calendar day averaging period. The department  
may specifically authorize compliance to be based upon a longer averaging period, which  
shall not be not to exceed more than 1 calendar month.  
(b) If coatings that belong to more than 1 coating category are used on the same coating  
line during the specified averaging period, then compliance shall must be determined  
separately for each coating category.  
(c) The information and records as required by the provisions of subrule (2) of this rule.  
(54) Compliance with the limits specified in subrule (1) of this rule must shall be  
determined using the method described in either R 336.2040(12)(i) if the coating line  
does not have an add-on emissions control device or R 336.2040(12)(j) if the coating line  
has 1 or more add-on emissions control devices.  
(65) This rule, with the exception of subrule (2) of this rule, does not apply to flat wood  
paneling coating lines which that are within a stationary source and which have a  
combined actual emission rate of volatile organic compounds of less than 100 pounds per  
day or 2,000 pounds per month as of the effective date of this amendatory rule. If the  
combined actual emission rate equals or exceeds 100 pounds per day for a subsequent  
day or 2,000 pounds per month for a subsequent month, then this rule shall permanently  
apply applies to the coating lines.  
(76) A person may exclude low-use coatings that total 55 gallons or less per rolling 12-  
month period at a stationary source from the provisions of this rule, except for subrule (2)  
of this rule.  
(87) A person may discontinue the operation of a natural gas-fired afterburner, which is  
used to achieve compliance with the emission limits in this rule, between November 1  
and March 31, unless the afterburner is used to achieve compliance with, or is required  
by, any of the following:  
28  
(a) Any other Another provision of these rules.  
(b) A permit to install.  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department.  
(98) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 under subrule (7) (8) of this rule, then both of the following  
provisions shall apply between November 1 and March 31:  
(a) All other provisions of this rule, except the emission limits, shall remain in effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
(10) A flat wood paneling coating line subject to R 336.1620a does not need to meet  
the provisions of R 336.1620.  
R 336.1620a Emission of volatile organic compounds from existing flat wood  
paneling coating lines in 2015 ozone nonattainment areas.  
Rule 620a. (1) As used in this rule, coating of flat wood panelingmeans the  
factory-finished coating of flat products that are constructed of wood and intended  
for use as interior paneling, exterior siding, tileboard, cabinets, or furniture  
components.  
(2) Unless all of the applicable provisions this rule are met, a person shall not  
cause or allow the emission of any volatile organic compound from the coating of  
flat wood paneling on existing lines located in the 2015 ozone nonattainment area  
for the following materials:  
(a) Printed interior panels made of hardwood, plywood, or thin particleboard.  
(b) Natural finish hardwood plywood panels.  
(c) Class 2 finishes on hardboard panels.  
(d) Tileboard.  
(e) Exterior siding.  
(3) Except as provided in subrule (7), the provisions of this rule do not apply to the  
following:  
(a) Flat wood paneling coating lines that are within a stationary source and have a  
combined actual emission rate of volatile organic compounds, including related  
cleaning activities, of less than 15 pounds per day before consideration of controls. If  
the combined actual emission rate equals or is more than 15 pounds per day for a  
subsequent day, then this rule permanently applies to these coating lines.  
(b) Low-use coatings that total 55 gallons or less per rolling 12-month period at a  
stationary source.  
(4) A person subject to subrule (2) of this rule shall not cause or allow the emission  
of any volatile organic compound from flat wood paneling coating, unless 1 of the  
following provisions are met:  
(a) Surface coatings, inks, or adhesives are less than 2.1 pounds per gallon  
coating, excluding water and exempt solvents.  
(b) Surface coatings, inks, or adhesives are less than 2.9 pounds per gallon solids.  
29  
(c) Add-on control is operated and maintained and has an overall control  
efficiency of volatile organic compounds of 90% or more.  
(5) For each coating line, compliance with the emission limits specified in this rule  
must be based upon all of the following:  
(a) The volume-weighted average of all coatings that belong to the same coating  
category and are used during each calendar day averaging period.  
(b) If coatings that belong to more than 1 coating category are used on the same  
coating line during the specified averaging period, then compliance must be  
determined separately for each coating category.  
(c) The information and records as required by the provisions of subrule (7) of  
this rule.  
(6) Compliance with the limits specified in subrule (4) of this rule, as appropriate,  
must be determined using the methods described in R 336.2040(12), as applicable.  
(7) A person who is responsible for the operation of a coating line that is subject  
to this rule shall obtain current information and keep daily records necessary for  
the determination of compliance with this rule, as required in R 336.2041.  
R 336.1621 Emission of volatile organic compounds from existing metallic surface  
coating lines.  
Rule 621. (1) A person shall not cause or allow the emission of volatile organic  
compounds from the coating of metallic surfaces from any existing coating line in excess  
of the applicable emission rates as follows:  
(a) Four and three-tenths pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for clear coatings.  
(b) Three and one-half pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for air-dried coatings.  
(c) Three and one-half pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for extreme performance coatings.  
(d) Four and eight-tenths pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for truck final repair coatings.  
(e) Four and nine-tenths pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for glass adhesion body primer. For the purpose of As  
used in this subdivision, "glass adhesion body primer" means the prime coating that is  
applied to automobile or truck bodies as part of the glass bonding system.  
(f) Four and three-tenths pounds of volatile organic compounds emitted per gallon of  
coating, minus water, as applied for steel pail and drum interior coatings.  
(g) Three pounds of volatile organic compounds emitted per gallon of coating, minus  
water, as applied for all other coatings.  
(2) If the provisions of more than 1 subdivision of subrule (1) of this rule are applicable  
for a specific coating, then the least stringent provision shall apply applies.  
(3) To take credit for improved transfer efficiency, upon written request and approval by  
the department, a person may achieve the emission limits specified in subrule (1) of this  
rule by an equivalent emission limit expressed in pounds of volatile organic compounds  
emitted per gallon of applied coating solids. The equivalent emission limit is shall be  
established by the following equation:  
30  
(푇)  
A =  
100  
Where:  
A = Allowable equivalent emission limit, pounds of volatile organic compounds per  
gallon of applied coating solids.  
E = Applicable emission limit as specified in subrule (1) of this rule, pounds of volatile  
organic compounds per gallon of coating, minus water, as applied.  
S = Solids volume fraction representative of a compliance coating, gallon of solids per  
gallon of coating, minus water, as applied.  
The value of "S" shall must be determined by using the following equation:  
S = 1 -  
7.36  
(TE)b = Overall baseline transfer efficiency of the coating line as specified in subrule  
(4) of this rule, percent. Where If multiple application methods are used on the coating  
line, the overall baseline transfer efficiency shall must be determined using the method  
described in R 336.2040(9). Department approval of the transfer efficiency test method is  
required.  
(4) For the purpose of establishing an equivalent emission limit under subrule (3) of this  
rule, the value of (TE)b, the overall baseline transfer efficiency of the coating line, must  
shall be 60%. Notwithstanding this provision, a person may request, in writing to the  
department, and the department may approve, a value for (TE)b that is less than 60%, but  
not less than 40%. A request for a value for (TE)b of less than 60% shall must include a  
demonstration that the lower requested value is representative of the overall transfer  
efficiency achieved by similar coating lines which use the most efficient type of  
application equipment that is reasonably available for the similar coating lines.  
(5) A person who that is responsible for the operation of a coating line that is subject to  
this rule shall obtain current information, and keep daily records necessary, for the  
determination of compliance with the provisions of this rule, as required in R 336.2041.  
(6) For each coating line, compliance with the emission limits specified in this rule  
must shall be based upon all of the following:  
(a) The volume-weighted average of all coatings which that belong to the same coating  
category, and which are used during each calendar day averaging period. The department  
may specifically authorize compliance to be based upon a longer averaging period, which  
shall not be not to exceed more than 1 calendar month.  
(b) If coatings that belong to more than 1 coating category are used on the same coating  
line during the specified averaging period, then compliance must shall be determined  
separately for each coating category.  
(c) The information and records required by subrule (5) of this rule.  
(7) Compliance with the emission limits specified in this rule must shall be determined  
using the applicable method described in 1 of the following: subdivisions:  
(a) For coating lines that are subject to the emission limits specified in subrule (1) of  
this rule, the method described in either R 336.2040(12)(a) if the coating line has no add-  
31  
on emissions control device or R 336.2040(12)(b) if the coating line has 1 or more add-on  
emissions control devices.  
(b) For coating lines subject to the equivalent emission limits specified in subrule (3) of  
this rule, the method described in either R 336.2040(12)(e) if the coating line has no add-  
on emissions control device or R 336.2040(12)(f) if the coating line has 1 or more add-on  
emissions control device.  
(8) This rule does not apply to the coating of metallic surfaces that are subject to R  
336.1610.  
(9) This rule does not apply to any of the following:  
(a) Automobile refinishing.  
(b) Customized topcoating of less than 35 automobiles or trucks, or both, per day.  
(c) Coating of the exterior of airplanes when the part to be coated has already been  
assembled on the airplane.  
(d) Coating of the exterior of marine vessels when the part to be coated has already  
been assembled on the marine vessel.  
(e) Coating of a part consisting of both metallic and nonmetallic components if a  
demonstration is made, to the satisfaction of the department, that the limits of this rule  
cannot be met due to the presence of the nonmetallic component. In this case, and if the  
nonmetallic component of the part is plastic and used as an automobile, truck, or business  
machine plastic part, R 336.1632 shall apply applies to the coating of the part.  
(10) This rule, except for subrule (5) of this rule, does not apply to a metallic surface  
coating line that complies with both of the following provisions:  
(a) The coating line has an actual emission rate of volatile organic compounds equal to  
or less than 2,000 pounds per month and 10.0 tons per year as of November 4, 1999. If  
the actual rate of emissions from an exempted metallic surface coating line exceeds 2,000  
pounds per month for a subsequent month or 10.0 tons per year for a subsequent year,  
then the provisions of this rule shall thereafter permanently applyies to the metallic  
surface coating line for as long as the applicable equipment is in operation.  
(b) Volatile organic compound emissions from the coating line, when combined with  
the total emissions of volatile organic compounds from all other metallic surface coating  
lines at the stationary source that are exempted by this subrule, do not exceed 30.0 tons  
per year.  
(11) A person may exclude low-use coatings that total 55 gallons or less per rolling 12-  
month period at a stationary source from the provisions of this rule, except for subrule (5)  
of this rule.  
(12) A person may discontinue the operation of a natural gas-fired afterburner, which is  
used to achieve compliance with the emission limits in this rule, between November 1  
and March 31, unless the afterburner is used to achieve compliance with, or is required  
by, any of the following:  
(a) Any other Another provisions of these rules.  
(b) A permit to install.  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department.  
32  
(13) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 under subrule (12) of this rule, then both of the following  
provisions shall apply between November 1 and March 31:  
(a) All other provisions of this rule, except the emission limits, shall remain in effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
(14) A metallic surface coating line subject to R 336.1621a does not need to meet  
the provisions of this rule.  
R 336.1621a Emission of volatile organic compounds from existing metal parts,  
metal products, and motor vehicle material surface coating lines in 2015 ozone  
nonattainment areas.  
Rule 621a. (1) A person shall not cause or allow the emission of any volatile  
organic compound from an existing metallic surface coating line at a facility located  
in the 2015 ozone nonattainment areas in excess of the applicable emission rates  
provided in subrule (3) of this rule.  
(2) This rule does not apply to the following:  
(a) Except as provided in subrule (5) of this rule, metallic surface coating lines  
that are within a stationary source and have a combined actual emission rate of  
volatile organic compounds, including related cleaning activities, of less than 15  
pounds per calendar day before consideration of controls. If the combined actual  
emission rate equals or is more than 15 pounds per calendar day for a subsequent  
day, then this rule permanently applies to these coating lines.  
(b) Metallic surface coating lines that meet any of the following processes:  
(i) The portion of a metallic surface coating process that is addressed in  
R 336.1610, R 336.1610a, R 336.1620, R 336.1620a, R 336.1635, R 336.1636,  
R 336.1637, R 336.1638, and R 336.1639.  
(ii) Coating of a part consisting of both metallic and nonmetallic components if a  
demonstration is made to the satisfaction of the department, under  
R 336.1602(2), that the limits of this rule cannot be met due to the presence of the  
nonmetallic component. In this case, and if the nonmetallic component of the part is  
plastic and used as an automobile, truck, or business machine plastic part,  
R 336.1632 applies to the coating of the part, as applicable.  
(iii) Aerosol coatings.  
(iv) Architectural coatings, and automobile refinish coatings that are used for  
architectural coating or automobile refinish coating purposes as defined by their  
respective national volatile organic compound rules.  
(v) Coatings that are applied to test panels and coupons as part of research and  
development, quality control, or performance testing activities at paint research or  
manufacturing facilities.  
(vi) Customized top coating of less than 35 automobiles or trucks, or both, per  
calendar day.  
(vii) Coating of the exterior of airplanes when the part to be coated has already  
been assembled on the airplane.  
33  
(viii) Coating of the exterior of marine vessels when the part to be coated has  
already been assembled on the marine vessel.  
(ix) Coatings used on a non-production basis.  
(x) Rubber to metal bonding.  
(c) The following metal parts coating processes are exempt from subrule (3) of this  
rule:  
(i) Stencil coatings.  
(ii) Safety-indicating coatings.  
(iii) Solid-film lubricants.  
(iv) Electric-insulating and thermal-conducting coatings.  
(v) Magnetic data storage disk coatings.  
(vi) Plastic extruded onto metal parts to form a coating.  
(d) The coating of bodies or body parts for new heavier vehicles at an automobile  
and light-duty truck assembly facility or a heavier vehicle assembly facility where  
the person responsible elects to comply with the provisions of R 336.1610a under the  
classification of automobile and light-duty truck coating lines.  
(e) The application methods required by subrule (3)(b) of this rule do not apply to  
airbrush operations using 5 gallons or less per year of coating.  
(f) A person subject to this rule may exclude low-use coatings that have a  
combined total less than 55 gallons per rolling 12-month period at a stationary  
source from the provisions of this rule, except for subrule (5) of this rule.  
(3) A person shall not cause or allow the emission of volatile organic compounds  
from metallic surface coating operations, unless the following provisions are met:  
(a) A person responsible for a coating line engaged in the surface coating of  
metallic surfaces, with the exception of motor vehicle materials as listed in table 64-  
g, shall limit volatile organic compounds emissions from all volatile organic  
compound-containing materials, such as coatings, thinners, and other additives,  
used by each metallic surface coating line by complying with either subdivision (c),  
(d), or (e) of this subrule, as applicable.  
(b) A person subject to this rule shall not apply volatile organic compound-  
containing coatings to metal parts and products subject to the provisions of this  
rule, unless the coating is applied with properly operating equipment according to  
an operating procedure specified by the equipment manufacturer or the executive  
officer, or designee, and by the use of 1 of the following methods:  
(i) Electrostatic application.  
(ii) Flow coat.  
(iii) Dip coat (including electrodeposition).  
(iv) Roll coater.  
(v) High-volume, low-pressure (HVLP) spray.  
(vi) Airless spray.  
(vii) Air-assisted airless spray.  
(viii) Alternative coating application methods that demonstrate equal or better  
transfer efficiency capability than HVLP spraying. Written departmental approval  
is required for alternative coating application methods.  
34  
(c) A metallic surface coating operation must not cause or allow the emission of  
volatile organic compounds from the coating of metallic surfaces from any existing  
metal parts coating line in any of the 2015 ozone nonattainment areas, in excess of  
the applicable content limits expressed in terms of mass of volatile organic  
compounds per volume of coating excluding water and exempt compounds, as  
applied, as specified in table 64-e, or emission rates expressed in terms of mass of  
volatile organic compounds per volume of solids as applied, as specified in table 64-  
f, unless a demonstration is made to the satisfaction of the department, under R  
336.1602(2).  
TABLE 64-e  
Metal Parts and Products low-VOC Coating Content Limits  
Air Dried  
lb VOC/gal  
coating  
Baked  
Coating Category  
lb VOC/gal  
coating  
(excluding  
water), as  
applied  
2.3  
(excluding water),  
as applied  
General 1 Component  
2.8  
2.8  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
2.8  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
3.5  
2.8  
3.5  
3.5  
4.2  
General Multi Component  
Camouflage  
Electric-Insulating Varnish  
Etching Filler  
Extreme High-Gloss  
Extreme Performance  
Heat-Resistant  
High Performance Architectural  
High Temperature  
Metallic  
Military Specification  
Mold-Seal  
Pan Backing  
Prefabricated Architectural Multi-Component  
Prefabricated Architectural One-Component  
Pretreatment Coatings  
Repair and Touch Up  
Silicone Release  
Solar-Absorbent  
Vacuum-Metalizing  
Drum Coating, New, Exterior  
Drum Coating, New, Interior  
Drum Coating, Reconditioned, Exterior  
Drum Coating, Reconditioned, Interior  
2.3  
3.5  
3.5  
3.5  
3.0  
3.0  
3.0  
3.5  
3.5  
3.0  
2.3  
3.0  
3.5  
2.3  
2.3  
3.5  
3.0  
3.5  
3.0  
3.0  
2.8  
3.5  
3.5  
4.2  
35  
TABLE 64-f  
Metal Parts and Products VOC Emission Rate Limits (VOC per Volume Solids)  
Air Dried  
Baked  
Coating Category  
lb VOC/gal  
lb VOC/gal  
solids, as applied solids, as applied  
General 1 Component  
General Multi Component  
Camouflage  
Electric-Insulating Varnish  
Etching Filler  
Extreme High-Gloss  
Extreme Performance  
Heat-Resistant  
High Performance Architectural  
High Temperature  
Metallic  
Military Specification  
Mold-Seal  
4.52  
4.52  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
4.52  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
6.67  
4.52  
6.67  
6.67  
9.78  
3.35  
3.35  
6.67  
6.67  
6.67  
5.06  
5.06  
5.06  
6.67  
6.67  
5.06  
3.35  
5.06  
6.67  
3.35  
3.35  
6.67  
6.67  
5.06  
5.06  
4.52  
6.67  
6.67  
9.78  
Pan Backing  
Prefabricated Architectural Multi-Component  
Prefabricated Architectural One-Component  
Pretreatment Coatings  
Silicone Release  
Solar-Absorbent  
Vacuum-Metalizing  
Drum Coating, New, Exterior  
Drum Coating, New, Interior  
Drum Coating, Reconditioned, Exterior  
Drum Coating, Reconditioned, Interior  
(d) A metallic surface coating operation applicable to this rule, except for motor  
vehicle materials, may choose to use an equivalent volatile organic compound  
emission rate limit based on the use of a combination of low-volatile organic  
compound coatings specified in tables 64-e and table 64-f, specified methods of  
application specified under subdivision (b) of this subrule, and add-on controls. The  
overall emission reduction efficiency needed to demonstrate compliance is  
determined each day as follows:  
(i) Obtain the emission limitation from table 64-e or table 64-f. If using the lb  
volatile organic compounds/gal coating, excluding water, as applied limit from table  
64-e, then calculate the emission limitation in a solids basis according to the  
following equation:  
S = C / 1 (C/7.36 lb/gal)  
36  
Where:  
S = The volatile organic compound emission limitation in terms of lb volatile  
organic compounds/gal of coating solids.  
C = The volatile organic compound emission limitation in terms of lb volatile  
organic compounds/gal of coating, excluding water, as applied.  
(ii) Calculate the required overall emission reduction efficiency of the control  
system for the day according to the following equation:  
E = [(VOCa S)/VOCa] x 100  
Where:  
E = The required overall emission reduction efficiency of the control system for  
the day.  
VOCa = The maximum volatile organic compound content of the coatings, as  
applied, used each day on the subject coating line, in units of lb volatile organic  
compounds/gal of coating solids, as determined by the applicable test methods and  
procedures specified in subdivision (h) of this subrule.  
S = The volatile organic compound emission limitation in terms of lb volatile  
organic compounds/gal of coating solids.  
(e) A metallic surface coating operation applicable to this rule, with the exception  
of motor vehicle materials, can choose to use add-on control equipment that must  
have an overall control efficiency of 90% or higher. The coating operation would  
not have to limit the volatile organic compound content of the coating materials and  
would not need to use any particular coating application method.  
(f) A person subject to this rule shall not cause or allow the emissions of volatile  
organic compounds from existing motor vehicle material coating operations in any  
of the 2015 ozone nonattainment areas in excess of the emission rates as specified in  
table 64-g, as applicable.  
TABLE 64-g  
Volatile organic compound emission limitation for existing motor vehicle materials  
Coating category  
lb VOC/gal coating  
(excluding water), as applied  
Motor vehicle cavity wax  
Motor vehicle sealer  
Motor vehicle deadener  
Motor vehicle gasket/gasket sealing material  
Motor vehicle underbody coating  
Motor vehicle trunk interior coating  
Motor vehicle bedliner  
3.5  
3.0  
3.0  
1.7  
3.5  
3.0  
1.7  
3.5  
Motor vehicle lubricating wax/compound  
37  
(g) If the provisions of more than 1 coating category of this subrule are applicable  
for a specific coating, then the least stringent provision may be applied.  
(h) For each coating line, compliance with the emission limits specified in this rule  
must be based upon all of the following:  
(i) The volume-weighted average of all coatings that belong to the same coating  
category, and are used during each calendar day averaging period. Under R  
336.1602(2), the department may specifically authorize compliance to be based upon  
a longer averaging period, not to exceed more than 1 calendar month.  
(ii) If coatings that belong to more than 1 coating category are used on the same  
coating line during the specified averaging period, then compliance must be  
determined separately for each coating category.  
(iii) The information and records required by subrule (5) of this rule.  
(i) Compliance with the emission limits specified in this rule must be determined  
using the applicable method described in the following subdivisions:  
(i) For coating lines that are subject to the emission limits specified in subdivision  
(c) of this subrule, the method described in either R 336.2040(12)(a) if the coating  
line has no add-on emissions control device or R 336.2040(12)(b) if the coating line  
has 1 or more add-on emissions control devices.  
(ii) For coating lines that are subject to the emission limits specified in subrule  
(3)(d) of this rule, the method described in either R 336.2040(12)(c) if the coating  
line has no add-on emissions control device or R 336.2040(12)(d) if the coating line  
has 1 or more add-on emissions control devices.  
(4) The following work practices are required for storage, mixing operations, and  
handling operations for coatings, thinners, cleaning, and coating-related waste  
materials. The person responsible for a metallic parts surface coating operation  
shall develop written procedures to comply with the following provisions:  
(a) Store all volatile organic compound-containing coatings, thinners, coating-  
related waste, and cleaning materials in closed containers.  
(b) Ensure that mixing and storage containers used for volatile organic compound-  
containing coatings, thinners, coating-related waste, and cleaning materials are kept  
closed at all times, except when depositing or removing these materials.  
(c) Minimize spills of volatile organic compound-containing coatings, thinners,  
coating-related waste, and cleaning materials.  
(d) Convey volatile organic compound-containing coatings, thinners, coating-  
related waste, and cleaning materials from 1 location to another in closed containers  
or pipes.  
(e) Minimize volatile organic compound emission from cleaning of application,  
storage, mixing, and conveying equipment by ensuring that equipment cleaning is  
performed without atomizing the cleaning solvent and all spent solvent is captured  
in closed containers.  
(5) A person who is responsible for the operation of a coating line that is subject to  
this rule shall obtain current information, and keep daily records necessary for the  
determination of compliance with the provisions of this rule, and as required in  
R 336.2041.  
R 336.1622 Emission of volatile organic compounds from existing components of  
38  
petroleum refineries; refinery monitoring program.  
Rule 622. (1) A person shall not cause or allow the emission of any volatile organic  
compound from any existing component, as listed in subrule (2) of this rule, of a  
petroleum refinery, including topping plants, unless all of the provisions of this rule are  
satisfied or unless an equivalent control method, as approved by the department under R  
336.1602(2), is implemented. An alternate acceptable control method is described in  
“Standards of Performance for Equipment Leaks of VOC in Petroleum Refineries for  
which Construction, Reconstruction, or Modification Commenced After January 4, 1983,  
and on or Before November 7, 2006,40 CFR C.F.R., Ppart 60, Ssubpart GGG adopted  
by reference in R 336.1902.  
(2) A person shall not operate an existing petroleum refinery unless a monitoring  
program and schedule approved by the department is implemented. This monitoring  
program and schedule shall must provide for, and identify by type and refinery unit, by  
quarter, all of the following:  
(a) An annual inspection of all of the following components:  
(i) Pump seals.  
(ii) Process valves in liquid volatile organic compound service.  
(iii) Process drains.  
(iv) Components that are difficult to monitor.  
(b) A quarterly inspection of all of the following components:  
(i) Compressor seals.  
(ii) Process valves in gaseous volatile organic compound service.  
(iii) Pressure-relief valves in gaseous volatile organic compound service.  
(c) A weekly visual inspection of all pump seals from which volatile organic  
compounds could leak.  
(d) An immediate inspection of any pump seal from which a liquid, including which  
includes a volatile organic compound, is observed dripping.  
(e) An inspection of any relief valve from which a volatile organic compound could  
discharge within 2 normal business days after of its begins venting to the atmosphere.  
(f) An inspection as soon as is practical, but not later than 2 normal business days, after  
the repair of any component that was found leaking.  
(3) Except for the visual inspections required by subrule (2)(c) of this rule, all  
inspections shall must be performed using equipment and procedures as specified in 40  
CFR C.F.R. Ppart 60, Aappendix A, Mmethod 21, adopted by reference in R 336.1902.  
A component is leaking when a concentration of more than 10,000 ppm, by volume, as  
methane or hexane, is measured by Mmethod 21.  
(4) If implementation of the quarterly leak detection program as specified in subrule  
(2)(b) of this rule shows that 2% or less of the process valves in a given refinery unit are  
leaking for 2 consecutive quarters, then the inspections of process valves in that refinery  
unit may be skipped for 1 quarter. If 2% or less of the process valves in a given refinery  
unit are leaking for 5 consecutive quarters, then the inspections may be done annually. If  
a subsequent inspection shows that if more than 2% of the process valves are leaking,  
then quarterly inspections of valves shall again be required.  
(5) The percent of valves leaking on a refinery unit, as referenced in subrule (4) of this  
rule, shall must be determined by dividing the total number of valves found to be leaking  
39  
on the refinery unit during the specified monitoring period by the total number of valves  
on the refinery unit that are required to be monitored by this rule.  
(6) The provisions of this This rule do does not apply to any of the following:  
(a) Pressure-relief valves that vent to an operating flare header, fuel gas system, or  
vapor control device.  
(b) Components that are unsafe to monitor, until monitoring personnel would no longer  
be exposed to immediate danger.  
(c) Storage tank valves.  
(d) Valves that are not externally regulated.  
(e) Components that process, transfer, or contain 1 or more volatile organic compounds  
in the liquid phase under actual conditions, all of which have a true vapor pressure of less  
than 1.55 psia.  
(7) Notwithstanding the provisions of subrule (2) of this rule, the monitoring of  
components, such as process drains and valves, that are used solely in effecting a refinery  
unit turnaround, is required only within the quarter following the turnaround.  
(8) A leak that is detected pursuant to the monitoring program provisions of subrule (2)  
of this rule or for any other another reason must shall be repaired. Except as provided in  
subrule (10) of this rule, this leak shall must be repaired as soon as possible, but not more  
than 15 days after the leak is detected. Until the time that the leak is repaired and retested  
verifying a successful repair, the component causing the leak must shall bear a weather-  
resistant, numbered, identifying tag that indicates the date the leak was discovered.  
(9) A log of all leaks detected pursuant to the provisions of subrules (2), (3), (5), and (6)  
of this rule or by another any other method shall must be maintained by the operator of  
the petroleum refinery. This log shall must identify all of the following:  
(a) The leaking component by type and location.  
(b) The number of the identifying tag.  
(c) The date the leak was discovered.  
(d) The date the leak was repaired.  
(e) The date the component was retested after the repair with an indication of the testing  
results.  
(f) The person or persons who performed the inspections. The log must shall be made  
available to any representative of the department during normal business hours of the  
refinery and shall be kept maintained for a minimum of 2 years.  
(10) If a leak cannot be repaired within 15 days due to circumstances beyond the control  
of the operator of the petroleum refinery or because the leaking component cannot be  
repaired unless a significant portion of the refinery unit is shut down for turnaround, then  
the operator shall maintain a separate log of the non-repair. The log shall must identify  
all of the following:  
(a) The leaking component by type, location, and refinery unit.  
(b) The date on which the leak was discovered.  
(c) The reason why the leak cannot be repaired within 15 days.  
(d) The estimated date of repair.  
(11) Within 25 days after of the end of the previous quarter, the operator shall submit to  
the department a report that contains all of the following information for that quarter:  
(a) The total number of components tested, by type.  
(b) The total number of components found leaking and repaired, by type.  
40  
(c) The accumulative total number of components, by refinery unit and type, found to  
be leaking and not repaired within the required time period and the reason for non-repair.  
(d) The type or types of monitoring equipment utilized during the quarter. The report  
required by this subrule shall must be made on a form approved by the department.  
(12) The department may require the early shutdown for turnaround of a refinery unit if  
the department feels that there are a significant number of leaks that would justify this  
action.  
(13) Except for safety pressure-relief valves, a person shall not operate existing  
petroleum refinery equipment that has a valve at the end of a pipe or line that contains a  
volatile organic compound, unless the pipe or line is sealed with a second valve, blind  
flange, plug, or cap. The sealing device may be removed only when a sample is being  
taken or during maintenance operations. A current, written description detailing routine  
sampling procedures and listing the sealing devices involved must shall be maintained  
and , upon request by the department, shall be submitted to the department in an  
acceptable format upon request.  
R 336.1623 Storage of petroleum liquids having a true vapor pressure of more than 1.0  
psia, but less than 11.0 psia, in existing external floating roof stationary vessels of more  
than 40,000-gallon capacity.  
Rule 623. (1) A person shall not store any petroleum liquid having a true vapor pressure  
of more than 1.0 psia, but less than 11 psia, at actual storage conditions in any existing  
external floating roof stationary vessel of more than 40,000-gallon capacity, unless the  
provisions of subrules (2) to (11) of this rule are met or unless an equivalent control  
method, as approved by the department under R 336.1602(2), is implemented.  
(2) Any stationary vessel subject to the provisions of this rule must shall be equipped  
with a floating roof to which a continuous rim-mounted secondary seal has been attached.  
(3) The secondary seal, as required by subrule (2) of this rule, must shall meet all of the  
following requirements:  
(a) There shall must be no visible holes, tears, or other nonfunctional openings in the  
seal or seal fabric.  
(b) The seal shall must be intact and uniformly in place around the circumference of  
the floating roof between the floating roof and the vessel wall.  
(c) For vessels equipped with vapor-mounted primary seals, the accumulated area of  
gaps exceeding 1/8 of an inch in width between the secondary seal and the vessel wall  
shall not exceed 1.0 square inch per foot of tank diameter.  
(4) All openings in the external floating roof in any stationary vessel subject to the  
provisions of this rule, except for automatic bleeder vents, rim space vents, and leg  
sleeves, shall must be equipped with both of the following:  
(a) Covers, seals, or lids that must shall remain in the closed position, except when the  
openings are in actual use.  
(b) Projections into the vessel that remain below the liquid surface at all times.  
(5) All automatic bleeder vents in any stationary vessel subject to the provisions of this  
rule shall must be closed at all times, except when the floating roof is floated off or  
landed on the roof leg supports.  
41  
(6) All rim vents in any stationary vessel subject to the provisions of this rule shall must  
be set to open only when the floating roof is being floated off the leg supports or at the  
manufacturer's recommended setting.  
(7) All emergency floating roof drains in any stationary vessel subject to the provisions  
of this rule shall must be provided with slotted membrane fabric covers, or equivalent  
covers, that cover not less than 90% of the area of the opening.  
(8) A person who is responsible for the operation of a stationary vessel subject to the  
provisions of this rule shall comply with all of the following requirements:  
(a) Perform a semiannual routine inspection to ensure compliance with all provisions of  
subrules (2) to (7) of this rule, with the exception of subrule (3)(c) of this rule.  
(b) For vessels equipped with a vapor-mounted primary seal, perform an annual  
inspection to document compliance with the provisions of subrule (3)(c) of this rule.  
(c) Maintain a record of the results of the inspections performed as required by this  
subrule. This record must shall be made available to any representative of the department  
and shall be maintained kept for a minimum of 2 years.  
(d) The provisions of this subrule may, upon written notice, be modified by the  
department under R 336.1602(2), if considered necessary to accomplish the purpose of  
this rule.  
(9) The provisions of subrules (2) and (3) of this rule do not apply to any of the  
following external floating roof stationary vessels:  
(a) Vessels that are used to store waxy, heavy-pour crude oil.  
(b) Vessels of less than 420,000-gallon capacity that are used to store produced crude  
oil and condensate before lease custody transfer.  
(c) Vessels of welded construction which that are equipped with a primary seal  
consisting of a metallic-type shoe seal, a liquid-mounted foam seal, or a liquid-mounted,  
liquid-filled-type seal and which contain a petroleum liquid that has a true vapor pressure  
of less than 4.0 psia.  
(d) Vessels that are used to store jet naphtha (jet b or jp-4).  
(10) A person who that is responsible for the operation of a stationary vessel that meets  
1 of the exemption provisions of subrule (9) of this rule shall maintain records that  
include all of the following information:  
(a) The type of vessel and, for a stationary vessel that meets the exemption provisions  
of subrule (9)(c) of this rule, the type of primary seal.  
(b) The capacity of the stationary vessel.  
(c) The contents of the stationary vessel.  
(d) For a stationary vessel that meets the exemption provisions of subrule (9)(c) of this  
rule, the true vapor pressure of the petroleum liquid in the stationary vessel.  
(11) The provisions of subrules (2) to (8) of this rule do not apply to any existing  
floating roof stationary vessel that contains a petroleum liquid which that has a true  
vapor pressure of less than 1.5 psia. A person who that is responsible for such stationary  
vessel shall maintain a record that includes all of the following information:  
(a) Average monthly stored liquid temperature.  
(b) Type of petroleum liquid.  
(c) Reid vapor pressure of the petroleum liquid. The record that is required by this  
subrule must shall be made available to any representative of the department and shall be  
maintained kept for a minimum of 2 years.  
42  
R 336.1624 Emission of volatile organic compounds from existing graphic arts lines.  
Rule 624. (1) A person shall not cause or allow the emission of any volatile organic  
compound from an existing graphic arts line, unless all of the provisions of the following  
subrules this rule are met or unless an equivalent emission rate, as approved by the  
department, is achieved. For the purpose of this rule, the term As used in this rule,  
"graphic arts" applies to rotogravure and flexographic operations only.  
(2) For the purpose of this rule, both of the following provisions apply:  
(a) In calculating the calendar day averaging period percent reduction of volatile  
organic compound emissions from a graphic arts line that is subject to the emission limits  
specified in subrule (3)(c) of this rule, the starting level shall must be the total amount of  
volatile organic compounds used on the graphic arts line during the calendar day  
averaging period. This level must shall be expressed as pounds of volatile organic  
compounds.  
(b) It will be is assumed that all volatile organic compounds applied to the substrate are  
emitted, unless captured and controlled by control equipment.  
(3) A person shall not cause or allow the emission of any volatile organic compound  
from an existing graphic arts line, unless the provisions of 1 or more of the following  
subdivisions are met:  
(a) The volatile fraction of all inks and coatings used on a graphic arts line as applied to  
the substrate must shall contain a maximum of 25%, by volume, of volatile organic  
compounds, based upon a calendar day averaging period.  
(b) The nonvolatile fraction of all inks and coatings used on a graphic arts line as  
applied to the substrate, minus water, shall must be a minimum of 60%, by volume,  
based upon a calendar day averaging period.  
(c) The overall reduction in volatile organic compound emissions, based on pounds of  
volatile organic compounds from a graphic arts line for which compliance is to be  
achieved through the use of 1 or more add-on emissions control devices must shall be 1  
of the following, based upon a calendar day averaging period:  
(i) For publication rotogravure printing, a minimum of 75%.  
(ii) For packaging rotogravure printing, a minimum of 65%.  
(iii) For flexographic printing, a minimum of 60%.  
(4) A person who that is responsible for the operation of a graphic arts line that is  
subject to this rule shall obtain current information, and keep records necessary, for a  
determination of compliance with this rule, as follows:  
(a) As required in subrule (12) of this rule for sources subject to subrule (3)(a) or (b) of  
this rule.  
(b) As required in R 336.2041(10)(d) and (e) for sources subject to subrule (3)(c) of this  
rule.  
(5) Compliance with the emission limits specified in this rule must shall be based upon  
all of the following provisions, as applicable:  
(a) Compliance with the emission limit specified in subrule (3)(a) or (b) of this rule  
shall must be based upon all inks and coatings that are used during each calendar day  
averaging period.  
43  
(b) Compliance with the applicable calendar day averaging period overall reduction  
provision specified in subrule (3)(c) of this rule shall must be based upon all inks and  
coatings that are used during each calendar day averaging period.  
(c) If more than 1 compliance option listed in subrule (3) of this rule is used on a  
graphic arts line during a calendar day averaging period, then compliance must shall be  
determined separately for each option used and shall be based upon all inks and coatings  
used for each option during each calendar day averaging period.  
(d) The department may specifically authorize compliance to be based upon a longer  
averaging period than the calendar day averaging period specified in subdivision (a), (b),  
or (c) of this subrule, not to exceed but the period shall not be more than 1 calendar  
month.  
(e) The information and records as required by subrule (4) of this rule.  
(6) Compliance with subrule (3)(a) and (b) of this rule must shall be determined using  
the method described in subrule (11) of this rule. Compliance with subrule (3)(c) of this  
rule shall must be determined using the method described in R 336.2040(11).  
(7) This rule, except for subrule (4) of this rule, does not apply to graphic arts lines  
which that are within a stationary source and which have a total combined actual  
emission rate of volatile organic compounds of less than 100 pounds per day or 2,000  
pounds per month as of November 4, 1999. If the combined actual emission rate equals  
or is more than 100 pounds per day for a subsequent day or 2,000 pounds per month for a  
subsequent month, then this rule shall permanently apply applies to the graphic arts lines.  
(8) A person may exclude low-use inks or coatings that total 55 gallons or less per  
rolling 12-month period at a stationary source from the provisions of this rule, except for  
subrule (4) of this rule.  
(9) A person may discontinue the operation of a natural gas-fired afterburner , which  
that is used to achieve compliance with the emission limits in this rule , between  
November 1 and March 31, unless the afterburner is used to achieve compliance with, or  
is required by, any of the following:  
(a) Any other Another provisions of these rules.  
(b) A permit to install.  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department.  
(10) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 under subrule (9) of this rule, then both of the following  
provisions shall apply between November 1 and March 31:  
(a) All other provisions of this rule, except the emission limits, shall remain in effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
(11) Compliance with subrule (3)(a) and (b) of this rule must shall be determined as  
follows:  
(a) The following equation must shall be used to determine if the volatile fraction of all  
inks and coatings used on a graphic arts line, as applied, meets the volatile organic  
compound limitation specified in subrule (3)(a) of this rule:  
44  
VOC = ∑  
푂퐶퐼 x 100  
퐼=1  
퐶퐼  
퐼=1  
Where:  
VOC = Volatile organic compound fraction of the volatile fraction of all inks and  
coatings used on a graphic arts line, as applied, each calendar day averaging period,  
percent.  
I = Individual ink or coating, as applied.  
N = Number of different inks and coatings used on a graphic arts line, as applied, each  
calendar day averaging period.  
LI = Volume of each ink or coating, as applied, used on the calendar day averaging  
period, gallons.  
VVOCI = Volume fraction of volatile organic compounds in each ink or coating, as  
applied, percent.  
VVCI = Volume fraction of volatiles in each ink or coating, as applied, percent. The  
provisions of subrule (3)(a) of this rule must shall be met if the value for "VOC" in the  
equation is less than or equal to 25%percent.  
(b) The following equation must shall be used to determine if the nonvolatile fraction  
of all inks and coatings used on a graphic arts line, as applied, meets the limitation  
specified in subrule (3)(b) of this rule:  
NV = ∑  
푂퐶퐼 x 100  
퐼=1  
퐶퐼  
퐼=1  
Where:  
NV = Nonvolatile fraction of all inks and coatings used on a graphic arts line, as  
applied, minus water and exempt compounds, by volume, on a calendar day averaging  
period, percent.  
I = Individual ink or coating, as applied.  
N = Number of different coatings and inks used on a graphic arts line, as applied, each  
calendar day averaging period.  
LI = Volume of each ink or coating, as applied, used on the calendar day averaging  
period, gallons.  
VI = Volume fraction of non-volatiles in each ink or coating, as applied, percent.  
VVOCI = Volume fraction of volatile organic compounds in each ink or coating, as  
applied, percent.  
The provisions of subrule (3)(b) of this rule must shall be met if the value for "NV" in  
the equation is equal to or greater than 60%percent.  
(12) A person subject to subrule (3)(a) or (b) of this rule shall keep the following  
records:  
(a) For graphic arts lines subject to subrule (3)(a) of this rule:  
(i) The name, identification number, and volume "LI", of each ink or coating used each  
calendar day averaging period.  
45  
(ii) The volume fraction of volatile organic compounds in each ink or coating, as  
applied, each calendar day averaging period.  
(iii) The volume fraction of volatiles in each ink or coating, as applied, during each  
calendar day averaging period.  
(iv) The volatile organic compound fraction of the volatile fraction of all inks and  
coatings used on a graphic arts line, as applied, each calendar day averaging period.  
(b) For graphic arts lines subject to subrule (3)(b) of this rule:  
(i) The name, identification number, and volume "LI", of each ink or coating used each  
calendar day averaging period.  
(ii) The volume fraction of non-volatiles in each ink or coating, as applied, each  
calendar day averaging period.  
(iii) The volume fraction of non-volatiles in all inks and coatings used each calendar  
day averaging period.  
(13) Sources demonstrating compliance with a control efficiency as required in subrule  
(3)(c) of this rule shall submit a stack testing protocol based on the conditions in  
(Reference the appropriate section in 1040 or 1041 for approval by the department.  
(14) A graphic art line subject to R 336.1624a does not need to meet the  
provisions of this rule accept as specified in R 336.1624a.  
R 336.1624a Emission of volatile organic compounds from existing flexographic  
printing lines located in the 2015 ozone nonattainment areas.  
Rule 624a. (1) As used in this rule:  
(a) “Flexible packaging” means packaging that is not rigid and whose shapes can  
be readily changed. Flexible packaging includes, but is not limited to, bags,  
pouches, liners, and wraps utilizing paper, plastic, film, aluminum foil, metalized  
or coated paper or film, or any combination of these materials.  
(b) “Flexible packaging printing” means the subset of graphic arts lines used in  
the printing of packages or parts of packages.  
(c) “Graphic arts” means rotogravure and flexographic printing operations only.  
(2) A person shall not cause or allow the emission of any volatile organic  
compound from inks, coatings, adhesives, and cleaning material from an existing  
flexible package printing line located in the 2015 ozone nonattainment areas, unless  
all of the applicable provisions of this rule are met.  
(3) Except as provided in subrule (8) of this rule, the provisions of this rule do not  
apply to flexible package printing lines that are within a stationary source and have  
a combined actual emission rate of volatile organic compounds, including related  
cleaning activities, of less than 3 tons per year on a 12-month rolling basis before  
consideration of controls  
Commented [GJ2]: This is confusing as subrule 8 contains  
recordkeeping requirements for sources that are subject to  
the rule and need to demonstrate compliance. You may  
want to add a provision to subrule 8 that says to track  
emissions on a 12 month rolling basis and then reference  
that specific provision.  
Commented [GJ3]: Please delete this once in always in  
provision as it is not supported by current EPA  
requirements. It is not in the CTG for offset lithographic  
printing or letterpress printing.  
(a) In lieu of calculating emissions to establishing that the facility's total  
actual VOC emissions are less than 3 tons per year on a 12-month  
rolling basis before consideration of controls, the owner or operator  
may maintain monthly records of material usage demonstrating the  
following thresholds have not been exceeded:  
Commented [GJ4]: This allows smaller facilities to  
determine if the rule is applicable to them without having to  
perform complex emission calculations.  
46  
Type of Printing Operation  
12-Month Rolling Threshold  
Flexographic and Rotogravure solvent  
based materials  
6,000 pounds of solvent  
from inks, dilution solvents, coatings,  
clean-up solutions and  
adhesives, combined  
Flexographic and Rotogravure water  
based materials  
24,000 pounds of water-based inks,  
coatings, and adhesives, combined;  
(4) Each printing press line with a potential to emit less than 25 tons per year of  
volatile organic compounds must meet the overall reduction of volatile organic  
compound emissions in R 336.1624(3), if they exceed the applicability threshold in  
the applicability threshold in 336.1624(7)as applicable.  
Commented [GJ5]: Having to meet this requirement  
needs to be contingent upon meeting the applicability  
threshold in 336.1624(7). This also needs to be stated and a  
condition of applicability before the requirements of  
336.1624(3) apply. Otherwise any flexible source that is not  
subject to 336.1624a would have to meet the requirements  
of 336.1624(3) even if they would be exempt per  
336.1624(7).  
(5) Each printing press line with a potential to emit of 25 tons per year or more of  
volatile organic compounds must meet the overall reduction of volatile organic  
compound emissions in subdivisions (a), (b) or (c) of this subrule, as applicable:  
(a) The volatile fraction of all inks, coatings, and adhesives used on a flexible  
package printing line as applied to the substrate must contain a maximum of 0.8 kg  
volatile organic compounds per kilogram solids applied. 0.8 pounds volatile organic  
compounds per pound of solids applied.  
(b) The volatile fraction of all inks, coatings, and adhesives used on a flexible  
package printing line as applied to the substrate must contain a maximum of , or  
0.16 kilogram volatile organic compounds per kilogram materials 0.16 pounds  
volatile organic compounds per pound of materials applied per line.  
(c) The overall reduction in volatile organic compound emissions, based on pounds  
of volatile organic compounds from a flexible package printing line for which  
compliance is to be achieved through the use of 1 or more add-on emissions control  
devices, must be 1 of the following, based upon a monthly averaging period:  
(i) A minimum of 65% control efficiency if the press was first installed before  
March 14, 1995, and control installed before March 1, 2023.  
Commented [GJ6]: The CTG does not use pounds, but  
kilograms and has a second limit based on materials  
applied. Also rule 1040 and 1041 need to be revised as they  
do not have kilograms as one of the compliance methods.  
See Page 14 at  
(ii) A minimum of 70% control efficiency if the press was first installed before  
March 14, 1995, and control installed on or after March 1, 2023.  
(iii) A minimum of 75% control if the press was installed on or after March 14,  
1995, and control installed before March 1, 2023.  
(iv) A minimum of 80% control if the press was installed on or after March 14,  
1995, and control installed on or after March 1, 2023.  
(d) An overall reduction in volatile organic compound emissions equivalent to  
the reductions in subdivision (c) of this subrule, using a combination of control  
efficiency and low volatile organic compound content materials.  
47  
(e) In lieu of calculating emissions to establish that the flexographic or  
rotogravure press line potential VOC emissions are less than twenty-five tons per  
year the owner or operator may maintain monthly records of material usage as  
follows:  
Commented [GJ7]: This allows smaller facilities to  
determine if the rule is applicable to them without having to  
perform complex emission calculations.  
Type of Printing Operation  
12-Month Rolling Threshold  
Flexographic and Rotogravure solvent 50,000 pounds of solvent  
from inks, dilution solvents, coatings,  
based materials  
clean-up solutions and  
adhesives, combined  
(6) Facilities must conduct the following work practice standards for cleaning  
materials:  
(a) Keep cleaning materials and used shop towels in closed containers.  
(b) Convey cleaning materials from 1 location to another in closed containers or  
pipes.  
(7) Compliance with the emission limits specified in this rule must be based upon  
all of the following provisions, as applicable:  
(a) Compliance with the emission limit specified in subrule (5)(a) or (b) of this rule  
must be based upon all inks, coatings, and adhesives that are used during each  
calendar month by using manufactures formulation data for pounds of material,  
pounds of solids, and volatile organic compounds in each product.  
(b) Compliance with the overall reduction specified in subrule (5)(c) of this rule  
must be based upon all inks, coatings, and adhesives that are used during each  
month, calculated using methods described in R 336.2040(11).  
(c) Compliance with the emission limit specified in subrule (4) of this rule must be  
determined as described in R 336.1624(5), (6) and (11).  
(d) Sources demonstrating compliance with a control efficiency as required in  
subrule (5)(c) of this rule shall submit a stack testing protocol based on the  
conditions in (Reference the appropriate section in 1040 or 1041 for approval by the  
department.  
(e) If more than 1 control option or limit listed in subrule (5) of this rule is used on  
a graphic arts line during a monthly averaging period, compliance must be  
determined separately for each option used and be based upon all inks, coatings,  
and adhesives used for each option during each monthly averaging period.  
(8) A person that is responsible for the operation of a graphic arts line that is  
subject to this rule shall obtain current information, and keep records necessary, for  
a determination of compliance with this rule, as follows:  
(a) For lines subject to subrule (5)(a) of this rule:  
(i) The volume fraction of volatile organic compounds in each ink, coating, and  
adhesive as applied, each month.  
(ii) The pounds of solids as applied, each month.  
48  
(b) For lines subject to subrule (5)(b) of this rule:  
(i) The volume fraction of volatile organic compounds in each ink, coating, or  
adhesive, as applied, each month.  
(ii) The pounds of materials as applied, each month.  
(c) For lines subject to subrule (5)(c) of this rule, follow requirements as  
described in R 336.2041(10)(d) and (e).  
(d) For lines subject to subrule (4) of this rule, follow requirements as  
described in R 336.1624(4) and (12).  
(e)  
When shop towels are properly stored and conveyed as required by subrule (6)  
When shop towels are properly stored and conveyed as required by  
subrule (6) of this rule, the affected source may use a retention factor from  
cleaning solutions of up to 50% for VOCs with a composite vapor pressure of  
no more than 10 mmHg at 20 degrees Celsius.  
Commented [GJ8]: There is no requirement in the CTG to  
track cleaning solution use or VOC content.  
R 336.1625 Emission of volatile organic compound from existing equipment utilized in  
manufacturing synthesized pharmaceutical products.  
Rule 625. (1) A person shall not cause or allow the emission of any volatile organic  
compound from existing equipment utilized in the manufacturing of synthesized  
pharmaceutical products, unless all of the provisions of the following subrules this rule  
are met or unless an equivalent control method, as approved by the department under  
R 336.1602(2), is implemented.  
(2) A person shall not operate an existing reactor, distillation operation, crystallizer,  
centrifuge, or vacuum dryer, unless the emissions from this equipment are controlled by  
either of the following:  
(a) A condenser, such that the outlet gas temperature does not exceed the following  
levels:  
(i) Minus 25 degrees Celsius (minus 13 degrees Fahrenheit) when the sum of the  
partial pressure or pressures of the volatile organic compound or compounds in the gas  
stream, as measured at 20 degrees Celsius (68 degrees Fahrenheit), is greater than 300  
millimeters of mercury (5.8 pounds per square inch).  
(ii) Minus 15 degrees Celsius (5 degrees Fahrenheit) when the sum of the partial  
pressure or pressures of the volatile organic compound or compounds in the gas stream,  
as measured at 20 degrees Celsius (68 degrees Fahrenheit), is greater than 150  
millimeters of mercury (2.9 pounds per square inch).  
(iii) Zero degrees Celsius (32 degrees Fahrenheit) when the sum of the partial pressure  
or pressures of the volatile organic compound or compounds in the gas stream, as  
measured at 20 degrees Celsius (68degrees Fahrenheit), is greater than 75 millimeters of  
mercury (1.5 pounds per square inch).  
(iv) Ten degrees Celsius (50 degrees Fahrenheit) when the sum of the partial pressure  
or pressures of the volatile organic compound or compounds in the gas stream, as  
measured at 20 degrees Celsius (68 degrees Fahrenheit), is greater than 52.5 millimeters  
of mercury (1.0 pounds per square inch).  
(v) Twenty-five degrees Celsius (77 degrees Fahrenheit) when the sum of the partial  
pressure or pressures of the volatile organic compound or compounds in the gas stream,  
49  
as measured at 20 degrees Celsius (68 degrees Fahrenheit), is greater than 26.2  
millimeters of mercury (0.5 pounds per square inch).  
(b) An alternative control technology approved by the department under R  
336.1602(2), the use of which results in an emission level no greater than would occur by  
meeting the provisions of subdivision (a) of this subrule. For purposes of comparing the  
actual emission level from an alternative control technology to the allowable emission  
level resulting from meeting the provisions of subdivision (a) of this subrule, the actual  
emission level must shall be determined using the methods described in 40 CFR C.F.R.  
Ppart 60, Aappendix A and the allowable emission level shall must be determined using  
the calculation methods described in appendix B of "Control of Volatile Organic  
Emissions From Manufacture of Synthesized Pharmaceutical Products," EPA-450/2-78-  
029, both adopted by reference in R 336.1902.  
(3) For the purpose of this rule, the sum of the partial pressure or pressures of the  
volatile organic compound or compounds in the gas stream is to be determined as  
follows:  
Where:  
Pt = 푖=1(푃푖)(푋푖)  
Pt = Sum of the partial pressures of all volatile organic compounds.  
Pi = Vapor pressure of volatile organic compounds at 20 degrees Celsius (68 degrees  
Fahrenheit).  
Xi = Mole fraction of volatile organic compounds in liquid mixture.  
n = Number of different volatile organic compounds in liquid mixture.  
i = Individual volatile organic compound.  
The mole fraction, Xi, is determined as follows:  
Xi = moles of "i" in liquid mixture total moles of liquid mixture  
The total moles of liquid mixture must shall include both the moles of volatile organic  
compounds and volatile inorganic compounds, (such as water) such as water, in the  
liquid mixture.  
(4) Notwithstanding the provisions of subrule (2)(a) of this rule, a person shall not be  
required to reduce the temperature of a gas stream below the freezing point of a  
condensable component in that gas stream if it can be demonstrated, using intrinsic  
chemical data, to the satisfaction of the department under R 336.1602(3), that in doing  
so, the condenser would be rendered ineffective. In this case, the temperature of the gas  
stream must shall be reduced as low as can be achieved without freezing of the  
condenser occurring.  
(5) The provisions of this rule do not apply to any single existing reactor, distillation  
operation, crystallizer, centrifuge, or vacuum dryer that has a maximum uncontrolled  
volatile organic compound emission rate of less than 15 pounds per day.  
(6) A person shall not operate an existing air dryer or production equipment exhaust  
system unless the volatile organic compound emissions from this equipment are reduced  
by not less than 90% if the uncontrolled volatile organic compound emissions are 330  
50  
pounds per day or more or are reduced to less than or equal to 33 pounds per day if the  
uncontrolled volatile organic compound emissions are less than 330 pounds per day.  
(7) A person shall not load or allow the loading of a volatile organic compound that has  
a vapor pressure of more than 210 millimeters of mercury (4.1 pounds per square inch),  
as measured at 20 degrees Celsius (68 degrees Fahrenheit), from a truck or railcar into an  
existing stationary vessel of more than a 2,000-gallon capacity, unless a vapor balance  
system or an alternate control system that provides not less than 90% control of loading  
emissions is utilized.  
(8) A person shall not store a volatile organic compound that has a vapor pressure of  
more than 75 millimeters of mercury (1.5 pounds per square inch), as measured at 20  
degrees Celsius (68 degrees Fahrenheit), in an existing above ground stationary vessel,  
unless the stationary vessel is equipped with a pressure/vacuum conservation vent set at  
plus or minus 1.5 millimeters of mercury (0.03 pounds per square inch) or an alternate  
control system at least as effective, under R 336.1602(2). For purposes of comparing the  
actual emission level from an alternative control technology to the allowable emission  
level resulting from the use of a pressure/vacuum conservation vent meeting this  
requirement, the actual emission level must shall be determined using the methods  
described in 40 CFR C.F.R. Ppart 60, Aappendix A, and the allowable emission level  
shall must be determined using the calculation methods described in appendix B of  
"Control of Volatile Organic Emissions From Manufacture of Synthesized  
Pharmaceutical Products,", EPA-450/2-78-029, both adopted by reference in R 336.1902.  
(9) A person shall not operate an existing centrifuge, rotary vacuum filter, or other filter  
that has an exposed liquid surface, where if the liquid contains a volatile organic  
compound or compounds and the sum of the partial pressure or pressures of volatile  
organic compound or compounds is 26.2 millimeters of mercury (0.5 pounds per square  
inch) or more, as measured at 20 degrees Celsius (68 degrees Fahrenheit), unless the  
equipment is enclosed.  
(10) A person shall not operate an existing in-process tank that may contain a volatile  
organic compound at any time, unless the tank is equipped with a cover and the cover  
remains closed, except when production, sampling, maintenance, or inspection  
procedures require operator access.  
(11) A person shall not operate any existing equipment utilized in the manufacturing of  
synthesized pharmaceutical products from which a liquid containing a volatile organic  
compound or compounds can be observed dripping or running, unless the leak is repaired  
immediately, if possible, but not later than the first time the equipment is off-line for a  
period of time that is long enough to complete the repair.  
(12) A person who is responsible for the operation of a synthesized pharmaceutical  
process subject to the provisions of this rule shall obtain current information and maintain  
records that are necessary for a determination of compliance with the provisions of this  
rule. The information shall must include all of the following:  
(a) For operations subject to the provisions of subrule (2) of this rule, all of the  
following information:  
(i) A list of all volatile organic compounds in each gas stream.  
(ii) The vapor pressure, as measured at 20 degrees Celsius (68 degrees Fahrenheit), of  
each volatile organic compound.  
(iii) The mole fraction of each volatile organic compound in the liquid mixture.  
51  
(iv) Continuous records of the gas outlet temperature of each condenser or of a  
parameter that insures ensures proper operation of an equivalent control device used  
pursuant to subrule (2)(b) of this rule.  
(b) For operations that are in compliance comply with the exemption provisions of  
subrule (5) of this rule, the amount of material entering and exiting each reactor,  
distillation operation, crystallizer, centrifuge, and vacuum dryer.  
(c) For air dryers subject to the provisions of subrule (6) of this rule, the amount of  
material entering and exiting each air dryer.  
(d) For operations subject to the provisions of subrule (7) of this rule, the following  
information:  
(i) The date when each stationary vessel is loaded.  
(ii) The type and vapor pressure, as measured at 20 degrees Celsius (68 degrees  
Fahrenheit), of each volatile organic compound loaded into each stationary vessel.  
(e) For operations subject to the provisions of subrule (9) of this rule, all of the  
following information:  
(i) A list of all volatile organic compounds in the liquid.  
(ii) The vapor pressure, as measured at 20 degrees Celsius (68 degrees Fahrenheit), of  
each volatile organic compound.  
(iii) The mole fraction of each volatile organic compound in the liquid mixture.  
(f) For operations subject to the provisions of subrule (11) of this rule, the following  
information:  
(i) The date each leak was detected.  
(ii) The date each leak was repaired.  
R 336.1627 Delivery vessels; vapor collection systems.  
Rule 627. (1) A person shall not operate any delivery vessel that is subject to control by  
a vapor collection system, either vapor balance or recovery system, required by R  
336.1606, R 336.1607, R 336.1608, or R 336.1609, R 336.1703, R 336.1704, R  
336.1705, or R 336.1706, unless all of the provisions of this rule are met.  
(2) Delivery vessels shall must comply with all requirements described in the 40 CFR  
C.F.R. Ppart 60, Aappendix A, Mmethod 27, adopted by reference in R 336.1902.  
(3) The owner of any delivery vessel that is subject to subrule (1) of this rule shall test  
the delivery vessel in accordance with 40 CFR C.F.R. Ppart 60, Aappendix A, Mmethod  
27, within 1 year after of the date of the previous test. Notification of the exact time and  
location of the test shall must be given to the department, in writing, not less than 7 days  
before the actual test. If the time or location of the test changes for any reason, then the  
owner or operator shall notify the department as soon as practical.  
(4) The test shall must comply with documentation requirements described in 40 CFR  
C.F.R. Ppart 60, Aappendix A, Mmethod 27 and shall be submitted to the department  
within 30 days of after the test completion and in a form acceptable to the department.  
Upon successful completion of the required testing, the vessel is shall be deemed  
provisionally certified providing the department does not invalidate the certification by  
issuing disapproval within 45 days after of receipt of the results.  
(5) There shall must be no visible liquid leaks from the vessel or collection system,  
except when the disconnection of dry breaks in liquid lines produces a few drops of  
liquid.  
52  
(6) A person shall not operate any vapor collection system, either vapor balance or  
recovery system, required by R 336.1606, R 336.1607, R 336.1608, and R 336.1609, R  
336.1703, R 336.1704, R 336.1705, or R 336.1706, unless all of the provisions of  
subrules (7) to (11) of this rule are met.  
(7) There shall must be no gas detector reading greater than or equal to 100% of the  
lower explosive limit at a distance of 1 inch from the location of the potential leak in the  
vapor collection system. Leaks shall must be detected by a combustible gas detector  
using the test procedure described in R 336.2005.  
(8) There shall must be no visible leaks, except from the disconnection of bottom  
loading dry breaks and from raising top loading vapor heads, where a few drops are  
allowed permitted.  
(9) The vapor collection system shall must be designed and operated to prevent gauge  
pressure in the delivery vessel from exceeding 0.6 pounds per square inch and to prevent  
vacuum from exceeding -0.2 pounds per square inch gauge.  
(10) The department may require the owner or operator of any vapor collection system  
subject to the provisions of subrule (6) of this rule to test the system in accordance with R  
336.2005. The tests must shall be conducted within 60 days following receipt of written  
notification from the department. Notification of the exact time and location of the test  
shall must be given to the department, in writing, not less than 7 days before the actual  
test. Documentation of the test that states the date and location of the test, test procedures,  
the type of equipment used, and the results of the test must shall be submitted to the  
department within 60 days following the last date of the test. If the time or location of the  
test changes for any reason, then the owner or operator shall notify the department as  
soon as practical.  
(11) Any delivery vessel or component of a vapor collection system that fails to meet  
any provision of this rule shall must not be operated until the necessary repairs have been  
made, the vessel or collection system has been retested, and the test results have been  
submitted to the department.  
R 336.1628 Emission of volatile organic compounds from components of existing  
process equipment used in manufacturing synthetic organic chemicals and polymers;  
monitoring program.  
Rule 628. (1) A person shall not cause or allow the emission of a volatile organic  
compound from a component of existing manufacturing process equipment at a synthetic  
organic chemical and polymer manufacturing plant located in any of the following  
counties, unless all of the provisions of subrules (2) to (16) of this rule are met or unless  
an equivalent control method, as approved by the department under  
R 336.1602(2), including the control method described in “Standards of Performance for  
Equipment Leaks of VOC in the Synthetic Organic Chemicals Manufacturing Industry  
for which Construction, Reconstruction, or Modification Commenced After January 5,  
1981, and on or Before November 7, 2006,” 40 CFR C.F.R., Ppart 60, subpart VV  
adopted by reference in R 336.1902, is implemented:  
(a) Kent Western portion of Allegan.  
(b) Livingston Berrien.  
53  
(c) Macomb Kent.  
(d) Monroe Livingston.  
(e) Muskegon Macomb.  
(f) Oakland Monroe.  
(g) Ottawa Muskegon.  
(h) St. Clair Oakland.  
(i) Washtenaw Ottawa.  
(j) Wayne St. Clair.  
(k) Washtenaw.  
(l) Wayne.  
(2) A person shall not operate existing manufacturing process equipment at a synthetic  
organic chemical and polymer manufacturing plant unless a monitoring program is  
implemented. The monitoring program shall must provide for all of the following:  
(a) A quarterly inspection of all components in light liquid or gaseous volatile organic  
compound service that are not designated as difficult-to-monitor components.  
(b) An annual inspection of all difficult-to-monitor components in light liquid or  
gaseous volatile organic compound service. Annual inspections shall must take place  
during the period of April 1 to hrough June 30.  
(c) A weekly visual inspection of all seals of pumps in light liquid service.  
(d) An immediate inspection of all components from which a liquid, which includes  
including a volatile organic compound, is observed dripping or from which a gaseous  
volatile organic compound is observed venting to the atmosphere.  
(e) Within 2 normal business days after of its begins venting to the atmosphere, an  
inspection of each relief valve from which a volatile organic compound could discharge.  
(f) An inspection, as soon as is practical, but not later than 5 calendar days, after the  
repair of a component that was found leaking.  
(3) Except for the visual inspections required by the provisions of subrule (2)(c) of this  
rule, all inspections shall must be performed using equipment and procedures as  
specified in 40 CFR C.F.R., Ppart 60, Aappendix A, Mmethod 21, adopted by reference  
in R 336.1902. A component is leaking when a concentration of more than 10,000 ppm,  
by volume, as methane or hexane, is measured by Mmethod 21.  
(4) If implementation of the quarterly leak detection program as specified in subrule  
(2)(a) of this rule shows that 2% or less of the process valves in a given process unit are  
leaking for 2 consecutive quarters, then the inspections of process valves in that unit are  
not required for 1 quarter. If 2% or less of the process valves in a given process unit are  
leaking for 5 consecutive quarters, then the inspections may be performed annually. If a  
subsequent inspection shows that more than 2% of the process valves are leaking, then  
quarterly inspections of valves shall again be required.  
(5) The percentage of valves leaking on a process unit, as referenced in subrule (4) of  
this rule, shall must be determined by dividing the total number of valves found to be  
leaking on the process unit during the specified monitoring period by the total number of  
valves on the process unit that are required to be monitored by this rule.  
(6) The provisions of subrule (2) of this rule do not apply to either of the following:  
54  
(a) A component that is equipped with a closed vent system which that is capable of  
capturing and transporting a leakage from the component to a control device that is  
designed and operated to reduce the volatile organic compound emissions vented to it by  
95% or more.  
(b) An unsafe-to-monitor component, until conditions would no longer expose  
monitoring personnel to immediate danger.  
(7) The provisions of this rule do not apply to any of the following:  
(a) A component that contains or contacts a gaseous stream with a volatile organic  
compound concentration of less than 10% by weight. Procedures that conform to the  
general methods in the following ASTM standards, adopted by reference in R 336.1902,  
shall must be used to determine the percentage of volatile organic compound contents in  
the process fluid that is contained in or contacts a piece of equipment:  
(i) Standard Practice for General Techniques of Infrared Quantitative Analysis,”  
ASTM E168.  
(ii) Standard Practices for General Techniques of Ultraviolet-Visible Quantitative  
Analysis,ASTM E169-04; .  
(iii) Standard Practice for Packed Column Gas Chromatography,ASTM E260.  
(b) A component that operates under a vacuum.  
(c) Components of synthetic organic chemical and polymer manufacturing process  
units that produce 1,100 tons per calendar year or less of light liquid or gaseous volatile  
organic compounds.  
(d) A relief valve that has an upstream rupture disc.  
(8) A person shall seal open-ended lines with a second valve, a blind flange, a cap, or a  
plug, except when the open end is in use, as with relief valves, double block and bleed  
valves, and composite samplers. In the case of a second valve, the upstream valve must  
shall be closed first after each use.  
(9) A component that is found to be leaking pursuant to the monitoring program  
provisions of subrule (2) of this rule or for another reason must shall be repaired. Except  
as provided in subrule (11) of this rule, the leak shall must be repaired as soon as  
possible, but not more than 15 days after the leak is detected. Until such time as the leak  
is repaired and retested verifying a successful repair, the component that is causing the  
leak shall must bear a weather-resistant, numbered identifying tag that indicates the date  
the leak was discovered.  
(10) A log of all leaks that are detected under subrule (2) of this rule must shall be  
maintained by the person who operates the synthetic organic chemical and polymer  
manufacturing plant. The log shall must list all of the following information:  
(a) The leaking component and synthetic organic chemical and polymer manufacturing  
process unit.  
(b) The number of the identifying tag.  
(c) The date the leak was discovered.  
(d) The date the leak was repaired.  
55  
(e) The date the component was retested after the repair, with an indication of the  
testing results.  
(f) The person or persons who performed the inspections.  
(11) All of the following provisions apply to delays in the repair of leaking components:  
(a) If a leak cannot be repaired within 15 calendar days because the leaking component  
cannot be repaired unless the synthetic organic chemical and polymer manufacturing  
process unit is shut down, then the person who operates the synthetic organic chemical  
and polymer manufacturing plant shall maintain a log of the non-repair and the leak must  
shall be repaired at the next unit turnaround.  
(b) If a leak cannot be repaired within 15 calendar days due to circumstances beyond  
the control of the person who operates the synthetic organic chemical and polymer  
manufacturing plant, then the person shall notify the department of the circumstances  
causing the delay in repair before the end of the fifteenth day and shall maintain a log of  
the non-repair. The leak must shall be repaired in an expeditious manner, which must  
shall be within 6 months of after the date the leak was detected.  
(c) The log specified in subdivisions (a) and (b) of this subrule must shall list all of the  
following information:  
(i) The leaking component and synthetic organic chemical and polymer manufacturing  
process unit.  
(ii) The date on which the leak was discovered.  
(iii) The reason why the leak cannot be repaired within 15 days.  
(iv) The estimated date of repair.  
(v) The number of the identifying tag.  
(12) A log of all unsafe-to-monitor components that are not part of the written program  
as required by subrule (14) of this rule must shall be maintained by the person who that  
operates the synthetic organic chemical and polymer manufacturing plant. This log must  
shall list all of the following information:  
(a) The unsafe-to-monitor component and synthetic organic chemical and polymer  
manufacturing process unit.  
(b) The number of the identifying tag.  
(c) The reason why the component was unsafe to monitor.  
(d) The date, or dates, on which the component was unsafe to monitor.  
(13) Not later than 25 calendar days after the end of the previous quarter, the person  
who that operates the synthetic organic chemical and polymer manufacturing plant shall  
submit, to the department, a report that contains all of the following information for that  
quarter:  
(a) The total number of components tested, by type.  
(b) The total number of components which are found leaking and which are repaired,  
by type.  
(c) The total number of components, by synthetic organic chemical and polymer  
manufacturing process unit and type, which are found to be leaking and which are not  
repaired within the required time period and the reason for non-repair.  
56  
(d) The type or types of monitoring equipment utilized during the quarter.  
(e) The total number of unsafe-to-monitor components that are logged as required by  
the provisions of subrule (12) of this rule. The report required by this subrule must shall  
be made on a form that is provided by the department.  
(14) A person who that is subject to the provisions of this rule shall comply with both  
of the following provisions:  
(a) Ddevelop a written program detailing how the provisions of this rule will be  
implemented. The program must shall include listings, by type and synthetic organic  
chemical and polymer manufacturing process unit, of all of the following:  
(ia) All components that are regularly inspected as required in subrule (2) of this rule.  
(iib) All components that are equipped with a closed vent system subject to the  
provisions of subrule (6)(a) of this rule.  
(iiic) All components that are exempted from the provisions of this rule pursuant to the  
provisions of subrule (7)(b), (c), and (d) of this rule.  
(ivd) All difficult-to-monitor components in light liquid or gaseous volatile organic  
compound service.  
(ve) All components which that are located outside a building, which can only be  
monitored by elevating the monitoring personnel more than 6 feet above ground level,  
and which are unsafe to monitor during the period of November 1 to through March 31.  
(b) Except as noted in subrule (16) of this rule, begin inspections as required in subrule  
(2) of this rule not later than 6 months after the effective date of this rule.  
(15) The written program required by the provisions of subrule (14) of this rule and the  
logs required by the provisions of subrules (10), (11), and (12) of this rule must shall be  
made available, to any representative of the department, on Monday through Friday  
between 9 a.m. and 5 p.m., at the synthetic organic chemical and polymer manufacturing  
plant. The logs must shall be maintained kept for a minimum of 2 years.  
(16) If a synthetic organic chemical and polymer manufacturing process unit that was  
previously exempt pursuant to the provisions of subrule (7)(c) of this rule produces light  
liquid or gaseous volatile organic compounds in excess of 1,100 tons in a calendar year,  
then the provisions of this rule shall apply. Inspections shall begin not later than 6 months  
after the end of that calendar year and be are maintained for as long as the applicable  
equipment is in operation thereafter.  
R 336.1629 Emission of volatile organic compounds from components of existing  
process equipment used in processing natural gas; monitoring program.  
Rule 629. (1) A person shall not cause or allow the emission of a volatile organic  
compound from a component of existing process equipment at a natural gas processing  
plant located in any of the following counties, unless all of the provisions of subrules (2)  
to (16) of this rule are met or unless an equivalent control method, as approved by the  
department under R 336.1602(2), is implemented:  
(a) Kent Western portion of Allegan.  
(b) Livingston Berrien.  
(c) Macomb Kent.  
(d) Monroe Livingston.  
(e) Muskegon Macomb.  
57  
(f) Oakland Monroe.  
(g) Ottawa Muskegon.  
(h) St. Clair Oakland.  
(i) Washtenaw Ottawa.  
(j) Wayne St. Clair.  
(k) Washtenaw.  
(l) Wayne.  
(2) A person shall not operate existing process equipment at a natural gas processing  
plant unless a monitoring program is implemented. The monitoring program must shall  
provide for all of the following:  
(a) A quarterly inspection of all components in gaseous or liquid volatile organic  
compound service that are not designated as difficult-to-monitor components.  
(b) An annual inspection of all difficult-to-monitor components in gaseous or liquid  
volatile organic compound service. Annual inspections must shall take place during the  
period of April 1 to through June 30.  
(c) A weekly visual inspection of all pump seals from which volatile organic  
compounds could leak.  
(d) An immediate inspection of all components from which a liquid, including which  
includes a volatile organic compound, is observed dripping or from which a gaseous  
volatile organic compound is observed venting to the atmosphere.  
(e) Within 2 normal business days after of its begins venting to the atmosphere, an  
inspection of each relief valve from which a volatile organic compound could discharge.  
(f) An inspection, as soon as is practical but not later than 5 calendar days after the  
repair, of a component that was found leaking.  
(3) Except for the visual inspections required by the provisions of subrule (2)(c) of this  
rule, all inspections must shall be performed using equipment and procedures as  
specified in 40 CFR C.F.R. Ppart 60, Aappendix A, Mmethod 21, adopted by reference  
in R 336.1902. A component is leaking when a concentration of more than 10,000 ppm,  
by volume, as methane or hexane, is measured by Mmethod 21.  
(4) If implementation of the quarterly leak detection program as specified in subrule  
(2)(a) of this rule shows that 2% or less of the process valves in a given process unit are  
leaking for 2 consecutive quarters, then the inspections on process valves in that process  
unit are not required for 1 quarter. If 2% or less of the process valves in a given process  
unit are leaking for 5 consecutive quarters, then the inspection may be performed  
annually. If a subsequent inspection shows that more than 2% of the process valves are  
leaking, then quarterly inspections of valves shall again be required.  
(5) The percentage of valves leaking on a process unit, as referenced in subrule (4) of  
this rule, shall must be determined by dividing the total number of valves that are found  
to be leaking on the process unit during the specified monitoring period by the total  
number of valves on the process unit that are required to be monitored by this rule.  
(6) A relief valve that is located in a nonfractionating plant that is inspected only by  
nonplant personnel may be inspected after a pressure release the next time that the  
inspecting personnel are at the plant, instead of within 5 days as specified in subrule  
(2)(e) of this rule. A relief valve must shall not be allowed to operate for more than 30  
days after a pressure release without an inspection.  
(7) The provisions of subrule (2) of this rule do not apply to any of the following:  
58  
(a) A component that is equipped with a closed vent system which that is capable of  
capturing and transporting a leakage from the component to a control device that is  
designed and operated to reduce the volatile organic compound emissions vented to it by  
95% or more.  
(b) A pump which that is equipped with a dual seal system that includes a barrier fluid  
and which is equipped with a sensor that will detect a failure of the seal system.  
(c) An unsafe-to-monitor component, until conditions do not expose monitoring  
personnel to immediate danger.  
(8) The provisions of this rule do not apply to any of the following:  
(a) A component, except any in field gas service, that contains or contacts a process  
stream that has a volatile organic compound concentration of less than 1.0% by weight.  
A component in field gas service is excluded from the provisions of this subrule.  
Procedures that conform to the general methods in the following ASTM standards,  
adopted by reference in R 336.1902, must shall be used to determine the percentage of  
volatile organic compound contents in the process fluid that is contained in or contacts a  
piece of equipment:  
(i) Standard Practice for General Techniques of Infrared Quantitative Analysis,”  
ASTM E168.  
(ii) Standard Practices for General Techniques of Ultraviolet-Visible Quantitative  
Analysis,ASTM E169-04; .  
(iii) Standard Practice for Packed Column Gas Chromatography,ASTM E260.  
(b) A component that operates under a vacuum.  
(c) A component in heavy liquid service.  
(d) A reciprocating compressor in field gas service.  
(e) A natural gas processing plant which has a capacity of less than 10,000,000 cubic  
feet per day and which does not fractionate natural gas liquids.  
(f) A relief valve that has an upstream rupture disc.  
(9) A person shall seal open-ended lines with a second valve, a blind flange, a cap, or a  
plug, except when the open end is in use, as with relief valves and double block and bleed  
valves. In the case of a second valve, the upstream valve must shall be closed first after  
each use.  
(10) A component that is found to be leaking pursuant to the monitoring program  
provisions of subrule (2) of this rule or for another reason must shall be repaired. Except  
as provided in subrule (12) of this rule, the leak must shall be repaired as soon as  
possible, but not more than 15 days after the leak is detected. Until such time as the leak  
is repaired and retested verifying a successful repair, the component that is causing the  
leak shall bear a weather-resistant, numbered identifying tag that indicates the date the  
leak was discovered.  
(11) A log of all leaks that are detected pursuant to the provisions of this rule must shall  
be maintained by the person who that operates the natural gas processing plant. The log  
must shall list all of the following information:  
(a) The leaking component and natural gas process unit.  
(b) The number of the identifying tag.  
(c) The date the leak was discovered.  
(d) The date the leak was repaired.  
59  
(e) The date the component was retested after the repair, with an indication of the  
testing results.  
(f) The person or persons who performed the inspections.  
(12) All of the following provisions apply to delays in the repair of leaking components:  
(a) If a leak cannot be repaired within 15 calendar days because the leaking component  
cannot be repaired unless the natural gas process unit is shut down, then the person who  
that operates the natural gas processing plant shall maintain a log of the non-repair and  
the leak must shall be repaired at the next unit turnaround.  
(b) If a leak cannot be repaired within 15 calendar days due to circumstances beyond  
the control of the person who that operates the natural gas processing plant, then the  
person shall notify the department of the circumstances causing the delay in repair before  
the end of the fifteenth day and shall maintain a log of the non-repair. The leak must  
shall be repaired in an expeditious manner, which must shall not be more than 6 months  
from after the date the leak was detected.  
(c) The log specified in subdivisions (a) and (b) of this subrule must shall list all of the  
following information:  
(i) The leaking component and natural gas process unit.  
(ii) The date on which the leak was discovered.  
(iii) The reason why the leak cannot be repaired within 15 days.  
(iv) The estimated date of repair.  
(v) The number of the identifying tag.  
(13) A log of all unsafe-to-monitor components that are not part of the written program  
as required by the provisions of subrule (15) of this rule must shall be maintained by the  
person who that operates the natural gas processing plant. The log must shall list all of  
the following information:  
(a) The unsafe-to-monitor component and natural gas process unit.  
(b) The number of the identifying tag.  
(c) The reason why the component was unsafe to monitor.  
(d) The date, or dates, on which the component was unsafe to monitor.  
(14) Not later than 25 calendar days after the end of the previous quarter, the person  
who that operates the natural gas processing plant shall submit, to the department, a  
report that contains all of the following information for that quarter:  
(a) The total number of components tested, by type.  
(b) The total number of components which that are found leaking and which are  
repaired, by type.  
(c) The total number of components, by natural gas process unit and type , which that  
are found to be leaking and which are not repaired within the required time period and the  
reason for non-repair.  
(d) The type or types of monitoring equipment utilized during the quarter.  
(e) The total number of unsafe-to-monitor components that are logged as required by  
the provisions of subrule (13) of this rule. The report required by this subrule must shall  
be made on a form that is provided by the department.  
(15) A person who that is subject to the provisions of this rule shall comply with both  
of the following provisions:  
60  
(a) dDevelop a written program detailing how the provisions of this rule will be  
implemented. The program must shall include listings, by type and natural gas process  
unit, of all of the following:  
(ia) All components that are regularly inspected as required in subrule (2) of this rule.  
(b) All components that are subject to the provisions of subrule (7)(a) and (b) of this  
rule.  
(iiic) All components that are exempted from the provisions of this rule pursuant to the  
provisions of subrule (8) of this rule.  
(ivd) All difficult-to-monitor components in gaseous or liquid volatile organic  
compound service.  
(ve) All components which are located outside a building, which can only be monitored  
by elevating the monitoring personnel more than 6 feet above ground level, and which  
are unsafe to monitor during the period of November 1 to through March 31.  
(b) Begin inspections, as required in subrule (2) of this rule, not later than 6 months  
after the effective date of this rule.  
(16) The written program required by the provisions of subrule (15) of this rule and the  
logs required by the provisions of subrules (11), (12), and (13) of this rule must shall be  
made available, to any representative of the department, on Monday through Friday  
between 9 a.m. and 5 p.m., at the natural gas processing plant. The logs must shall be  
maintained kept for a minimum of 2 years.  
R 336.1630 Emission of volatile organic compounds from existing paint manufacturing  
processes.  
Rule 630. (1) After April 19, 1990, a A person shall not cause or allow the emission of  
a volatile organic compound from existing equipment utilized in paint manufacturing  
located in any of the following counties, unless all of the provisions of subrules (2) to (4)  
of this rule are met or unless an equivalent control method, as approved by the  
department under R 336.1602(2), is implemented:  
(a) Kent Western portion of Allegan.  
(b) Livingston Berrien.  
(c) Macomb Kent.  
(d) Monroe Livingston.  
(e) Muskegon Macomb.  
(f) Oakland Monroe.  
(g) Ottawa Muskegon.  
(h) St. Clair Oakland.  
(i) Washtenaw Ottawa.  
(j) Wayne St. Clair.  
(k) Washtenaw.  
(l) Wayne.  
(2) All stationary and portable mixing tanks and high-speed dispersion mills must shall  
be equipped with covers that completely cover the tank or mill opening, except for an  
opening which is no larger than necessary to allow for safe clearance for the mixer shaft.  
The tank opening must shall be covered at all times, except when operator access is  
necessary.  
61  
(3) The cleaning of paint manufacturing equipment and paint shipping containers must  
shall be done by methods and materials that minimize the emission of volatile organic  
compounds.  
These methods and materials shall must include 1 of the following:  
(a) Hot alkali or detergent cleaning.  
(b) High-pressure water cleaning.  
(c) Cleaning by use of an organic solvent if the equipment being cleaned is completely  
covered or enclosed, except for an opening that is no larger than necessary to allow for  
safe clearance considering the method and materials being used.  
(4) Wash solvent must shall be stored only in closed containers.  
(5) The provisions of this rule do not apply to tanks or equipment which, pursuant to the  
provisions of this subrule that were in effect on April 19, 1989, was exempt from the  
provisions of this rule that were in effect on April 19, 1989, but which are now subject to  
the provisions of this rule, until 1 year after the effective date of this rule.  
R 336.1631 Emission of volatile organic compounds from existing process equipment  
utilized in manufacture of polystyrene or other organic resins.  
Rule 631. (l) After December 31, 1989, a A person shall not cause or allow the  
emission of volatile organic compounds from existing process equipment that is utilized  
in the manufacturing of polystyrene or other organic resins located in any of the  
following counties, unless all of the provisions of subrules (2) to (10) of this rule are met  
or unless an equivalent control method, as approved by the department under R  
336.1602(2), is implemented:  
(a) Kent Western portion of Allegan.  
(b) Livingston Berrien.  
(c) Macomb Kent.  
(d) Monroe Livingston.  
(e) Muskegon Macomb.  
(f) Oakland Monroe.  
(g) Ottawa Muskegon.  
(h) St. Clair Oakland.  
(i) Washtenaw Ottawa.  
(j) Wayne St. Clair.  
(k) Washtenaw.  
(l) Wayne.  
(2) The emission of volatile organic compounds from existing material recovery  
equipment that is utilized in the manufacture of polystyrene resin by a continuous process  
must shall not be more than 0.12 pounds per 1,000 pounds of polystyrene resin produced.  
(3) A person shall not operate an existing reactor, thinning tank, or blending tank that is  
utilized in the manufacture of a completed organic resin unless either of the following  
provisions is complied with:  
(a) All volatile organic compounds emitted from existing reactors, thinning tanks, and  
blending tanks must shall be vented to control equipment that is designed and operated to  
reduce the quantity of volatile organic compounds by not less than 95 weight percent.  
Reflux condensers that are essential to the operation of the resin reactor are not  
considered to be control equipment.  
62  
(b) The total volatile organic compounds emitted to the atmosphere from the reactors,  
thinning tanks, and blending tanks do not exceed 0.5 pounds per 1,000 pounds of  
completed organic resin produced.  
(4) Notwithstanding the provisions of subrule (3) of this rule, a person shall not operate  
an existing reactor, thinning tank, or blending tank utilized in the manufacture of a dry  
organic resin at the Solutia, Inc. of Trenton unless either 1 of the following provisions is  
complied with:  
(a) All volatile organic compounds emitted from existing reactors, thinning tanks, and  
blending tanks must shall be vented to control equipment that is designed and operated to  
reduce the quantity of volatile organic compounds by not less than 95 weight percent.  
Reflux condensers that are essential to the operation of the resin reactor are not  
considered to be control equipment.  
(b) The total volatile organic compounds emitted to the atmosphere from the reactors,  
thinning tanks, and blending tanks do not exceed 2.6 pounds per 1,000 pounds of dry  
organic resin produced.  
(5) Compliance with the emission limits specified in subrules (2), (3), and (4) of this  
rule must shall be determined using the method described in R 336.2060 or an alternate  
method acceptable to the department. Upon request by the department, a person who that  
is responsible for processes that are subject to the provisions of subrule (2), (3), or (4) of  
this rule shall submit, to the department, test data necessary for a determination of  
compliance.  
(6) Compliance with the emission limits specified in subrules (2), (3), and (4) of this  
rule must shall be determined using the method described in R 336.2060 or an alternate  
method acceptable to the department under R 336.1602(2). Upon request by the  
department, a person who that is responsible for processes that are subject to the  
provisions of subrule (2), (3), or (4) of this rule shall submit, to the department, test data  
necessary for a determination of compliance. including, but not limited to, the  
following:  
(a) Emissions test data.  
(b) Material balance calculations.  
(c) Process production rates.  
(d) Control equipment specifications and operating parameters.  
(7) A person who that is responsible for the operation of existing process equipment  
that is subject to the provisions of this rule shall submit, to the department, a written  
program for compliance with this rule or evidence of compliance with this rule. The  
written program for compliance shall must be submitted to the department before  
October 19, 1989.  
(8) The program required by subrule (7) of this rule shall must include the method by  
which compliance with this rule shall must be achieved, a description of new equipment  
to be installed or modifications to existing equipment to be made, and a timetable that  
specifies, at a minimum, all of the following dates:  
(a) The date or dates equipment shall must be ordered.  
(b) The date or dates construction, modification, or process changes must shall begin.  
(c) The date or dates initial start-up of equipment must shall begin.  
(d) The date or dates final compliance must shall be achieved.  
63  
(9) A person may discontinue the operation of a natural gas-fired afterburner , which  
that is used to achieve compliance with the emission limits in this rule, between  
November 1 and March 31, unless the afterburner is used to achieve compliance with, or  
is required by, any of the following:  
(a) Any other Another provisions of these rules.  
(b) A permit to install.  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department.  
(10) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 pursuant to the provisions of subrule (9) of this rule, then both  
of the following provisions shall apply during this time period:  
(a) All other provisions of this rule, except for the emission limits, shall remain in  
effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
R 336.1632 Emission of volatile organic compounds from existing automobile, truck,  
and business machine plastic part coating lines.  
Rule 632. (1) A person shall not cause or allow the emission of volatile organic  
compounds from an automobile, truck, or business machine plastic part coating line in  
any of the following counties unless all of the provisions of subrules (2) to (214) of this  
rule are met, as applicable:  
(a) Kent Western portion of Allegan.  
(b) Livingston Berrien.  
(c) Macomb Kent.  
(d) Monroe Livingston.  
(e) Muskegon Macomb.  
(f) Oakland Monroe.  
(g) Ottawa Muskegon.  
(h) St. Clair Oakland.  
(i) Washtenaw Ottawa.  
(j) Wayne St. Clair.  
(k) Washtenaw.  
(l) Wayne.  
(2) After December 31, 1989, and until December 31, 1992, a person shall not cause or  
allow the emission of volatile organic compounds from the coating of plastic parts of  
automobiles and trucks from any existing coating line in excess of the applicable  
emission rates as specified in table 65.  
(23) The After December 31, 1992, both of the following provisions must shall be met:  
(a) A person shall not cause or allow the emission of volatile organic compounds from  
the coating of plastic parts of automobiles and trucks from any existing coating line in  
excess of the applicable emission rates as specified in table 66.  
64  
(b) Except as provided for in subrule (160) of this rule, any coating that is subject to an  
emission rate specified in table 66 must shall not be applied with conventional air-  
atomizing spray equipment. All spray equipment must shall be installed, maintained, and  
operated in accordance with the recommendations and design of the equipment  
manufacturer.  
(4) After December 31, 1991, both of the following provisions shall be met:  
(ca) A person shall not cause or allow the emission of volatile organic compounds from  
the coating of plastic parts of business machines from any existing coating line in excess  
of the applicable emission rates as specified in table 67.  
(db) Except as provided for in subrule (160) of this rule, any prime or topcoat coating  
that is subject to the emission rate specified in table 67 must shall not be applied with air-  
atomizing spray equipment. All spray equipment must shall be installed, maintained, and  
operated in accordance with the recommendations and design of the equipment  
manufacturer.  
(35) If a part consists of both plastic and metal surfaces and is exempted from the  
provisions of R 336.1621 or R 336.1621a based on the provisions of R 336.1621(9)(e)  
and R 336.1621a(2)(b)(ii) respectively, the part is shall be subject to this rule.  
(46) If a coating line is subject to the provisions of R 336.1610, R 336.1610a,  
R 336.1621, or R 336.1621a, the coating line shall be is exempt from this rule.  
(57) A person who that is responsible for the operation of a coating line that is subject  
to this rule shall obtain current information and maintain daily records necessary for a  
determination of compliance with the provisions of this rule, as required in R 336.2041.  
(68) For each coating line, compliance with the emission limits specified in this rule  
shall be is based upon all of the following:  
(a) The volume-weighted average of all coatings which that belong to the same coating  
category and which are used during each calendar day averaging period. The department  
commission may specifically authorize compliance, under R 336.1602(2), to be based  
upon a longer averaging period, not to exceed which shall not be more than 1 calendar  
month.  
(b) If coatings belonging to more than 1 coating category are used on the same coating  
line during the specified averaging period, then compliance must shall be determined  
separately for each coating category.  
(c) The information and records as required by subrule (57) of this rule.  
(79) Compliance with the emission limits specified in this rule shall be determined using  
the following methods:  
(a) For the emission limits specified in subrules (2) to (4) of this rule, the method  
described in either R 336.2040(12)(a) if the coating line does not have an add-on  
emissions control device or R 336.2040(12)(b) if the coating line has 1 or more add-on  
emissions control devices.  
(b) For the emission limits established pursuant to the provisions of subrule (13) or  
(14) of this rule, the method described in R 336.2040(12) that is applicable to the form of  
these established emission limits.  
(10) A person who is responsible for the operation of an existing coating line that is  
subject to the provisions of this rule shall submit, to the commission, an acceptable  
written program for compliance with, or evidence of compliance with, the provisions of  
subrules (3) and (4) of this rule. This evidence shall include available emission test data,  
65  
material balance calculations, control equipment specifications, or other information that  
demonstrates compliance. The written program for compliance or evidence of  
compliance shall be submitted to the commission according to the following schedule:  
(a) Before July 1, 1990, for compliance with the provisions of subrule (4) of this rule.  
(b) Before July 1, 1991, for compliance with the provisions of subrule (3) of this rule.  
(11) The program for compliance that is required by the provisions of subrule (10) of  
this rule shall include the method by which compliance with this rule shall be achieved, a  
description of the new equipment to be installed or modifications to existing equipment  
to be made, and a timetable that specifies, at a minimum, all of the following dates:  
(a) The date or dates equipment shall be ordered.  
(b) The date or dates construction, modification, or process changes shall begin.  
(c) The date or dates initial start-up of equipment shall begin.  
(d) The date or dates final compliance shall be achieved if the date or dates are not the  
same as the date or dates specified in subdivision (c) of this subrule.  
(812) A modification of coating applicator equipment for the primary purpose of  
achieving compliance with the provisions of subrules (3)(b) and (4)(b) (2)(b) and (d) of  
this rule, to the extent that such the modification does not increase the potential to emit,  
shall must not be subject to the provisions of R 336.1220 and R 336.1702.  
(13) As part of the compliance program required by the provisions of subrule (10) of  
this rule, a person who is responsible for the operation of a coating line that is subject to  
this rule may request alternate provisions to those specified in this rule. The commission  
may establish alternate provisions for a period of time to be specified by the commission  
if all of the following conditions are met:  
(a) The coating line that is subject to the alternate provisions is in compliance, or on a  
legally enforceable schedule of compliance, with the other rules of the commission.  
(b) Compliance with the provisions of this rule is not technically or economically  
reasonable.  
(c) All measures that are both technically feasible and economically reasonable to reduce  
volatile organic compound emissions as required by this rule have been implemented in  
accordance with, or will be implemented in accordance with, a schedule approved by the  
commission. All alternate provisions approved by the commission shall become part of a  
legally enforceable order or part of an approved permit to install or operate.  
(14) The program for compliance that is required by the provisions of subrule (10) of  
this rule may address a combination of coating lines that are subject to the provisions of  
this rule, or 1 or more coating lines that are subject to the provisions of this rule in  
combination with 1 or more existing sources that are subject to the provisions of other  
rules of this part, if all of the following conditions are met:  
(a) All of the requirements specified in the United States Environmental Protection  
Agency's emissions trading policy statement, 51 F.R. 43814, December 4, 1986, adopted  
by reference in R 336.1902, are met.  
(b) All existing sources are within the same stationary source.  
(c) The total volatile organic compound emissions do not exceed the sum of the  
emissions allowed from each existing source using calculation methods acceptable to the  
commission and incorporating all of the requirements of the emissions trading policy  
statement.  
66  
(d) Emission reductions are accomplished in the time interval required for individual  
existing sources.  
(e) All emission limits established by this program become part of a legally enforceable  
order of the commission, permit to install, or permit to operate.  
(915) The provisions of this rule, with the exception of the provisions of subrule (57) of  
this rule, do not apply to any of the following:  
(a) Automobile, truck, or business machine plastic part coating lines which are  
within a stationary source located within the 2015 ozone nonattainment areas and  
have a combined actual emission rate of volatile organic compounds of less than or  
equal to 15 pounds per calendar day.  
(ba) Automobile, truck, or business machine pPlastic coating lines within any  
stationary source located in Ottawa, the eastern portion of Muskegon as defined in R  
336.1601, or Kent Counties and that have a total combined emission rate of volatile  
organic compounds from plastic coating lines of less than 30 tons per calendar year. The  
total combined emission rate must shall include emissions from coatings and coating  
operations exempted from this rule. If the total combined emissions equal or exceed 30  
tons in any subsequent year, the provisions of this rule shall thereafter permanently  
applyies to these plastic coating lines for as long as the applicable equipment is in  
operation.  
(cb) The application of adhesion primes.  
(dc) The application of electrostatic prep coats.  
(ed) The application of resist coats.  
(fe) The application of stencil coats.  
(gf) The application of texture coats to automobile or truck parts.  
(hg) The application of vacuum metalizing coatings.  
(ih) The application of gloss reducer.  
(ji) An automobile, truck, or business machine plastic part coating operation located  
in Ottawa, the eastern portion of Muskegon, or Kent Counties consisting of an  
applicator and any subsequent flash-off area or oven, or both, from which the total  
emission rate of volatile organic compounds is equal to or less than 2,000 pounds per  
calendar month and 10.0 tons per calendar year. The total combined emission rate of  
volatile organic compounds from these exempted operations at a stationary source shall  
must not be more than 30.0 tons per calendar year. If the total emission rate for an  
operation is more than 2,000 pounds in any subsequent month or 10 tons per year in a  
subsequent year, the provisions of this rule shall thereafter permanently apply to these  
automobile, truck, or business machine plastic part coating operations for as long as  
the applicable equipment is in operation.  
(kj) Low-use coatings that total 55 gallons or less per rolling 12-month period at a  
stationary source.  
(106) The provisions of subrules (3)(b) and (4)(b) subrule (2)(b) and (d) of this rule do  
not apply to the equipment used in any of the following:  
(a) The application of the final coat of metallic topcoat.  
(b) The application of waterborne coatings.  
(c) The application of touch-up and repair coatings.  
(d) Coating operations controlled by add-on emission controls.  
67  
(e) Coating operations for which an acceptable demonstration has been made that  
conventional air-atomizing spray equipment is the only technically feasible application  
method.  
(f) Other coating operations that together account for a total of 20% or less of the total  
volume of coatings applied by nonexempt coating application equipment calculated on a  
calendar day basis.  
(117) A person may discontinue the operation of a natural gas-fired afterburner, which  
that is used to achieve compliance with the emission limits in this rule, between  
November 1 and March 31 unless the afterburner is used to achieve compliance with, or  
is required by, any of the following:  
(a) Any other Another provisions of these rules.  
(b) A permit to install.  
(c) A permit to operate.  
(d) A voluntary agreement.  
(e) A performance contract.  
(f) A stipulation.  
(g) An order of the department commission.  
(128) If the operation of a natural gas-fired afterburner is discontinued between  
November 1 and March 31 pursuant to the provisions of subrule (117) of this rule, then  
both of the following provisions apply during this time period:  
(a) All other provisions of this rule, except for the emission limits, shall remain in  
effect.  
(b) All other measures that are used to comply with the emission limits in this rule  
between April 1 and October 31 shall must continue to be used.  
(19) Table 65 reads as follows:  
Table 65  
Volatile organic compound emission limitations for existing  
automobile and truck plastic parts coating lines after 12/31/89  
Coating category  
Pounds of volatile organic compounds  
allowed to be emitted per gallon of coating  
(minus water) as applied  
1. High bake coating-exterior and interior  
parts1,2  
(a) Prime  
(i) Flexible coating  
(ii) Nonflexible coating  
(b) Topcoat  
5.0  
4.0  
(i) Basecoat  
(ii) Clearcoat  
4.6  
4.3  
4.7  
(iii) Non-basecoat/clearcoat  
2. Air-dried coating--exterior parts3  
(a)Prime1  
6.1  
68  
(b)Topcoat  
(i) Basecoat  
(ii) Clearcoat  
(iii) Non-basecoat/clearcoat  
3. Air-dried coating--interior parts3  
4. Touch-up and repair3  
5.8  
5.4  
6.3  
6.3  
6.3  
1For red and black coatings, the emission limitation shall be determined by  
multiplying the appropriate limit in this table by 1.15.  
2When 40 C.F.R. Part 60, Appendix A, Method 24 is used to determine the volatile  
organic compound content of a coating, the applicable emission limitation shall be  
determined by adding 0.5 to the appropriate limit in this table.  
3When 40 C.F.R. Part 60, Appendix A, Method 24 is used to determine the volatile  
organic compound content of a coating, the applicable emission limitation shall be  
determined by adding 0.1 to the appropriate limit in this table.  
(2013) Table 66 reads as follows:  
Table TABLE 66  
Volatile organic compound emission limitations for existing  
automobile and truck plastic parts coating lines after 12/31/92  
Pounds of volatile organic compounds  
allowed to be emitted per gallon of coating  
(minus water) as applied  
Coating category  
1. High bake coating--exterior and interior  
parts1,2  
(a) Prime  
(i) Flexible coating  
(ii) Nonflexible coating  
(b) Topcoat  
4.5  
3.5  
(i) Basecoat  
(ii) Clearcoat  
4.3  
4.0  
4.3  
(iii) Non-basecoat/clearcoat  
2. Air-dried coating--exterior parts1,3  
(a)Prime  
4.8  
(b)Topcoat  
(i) Basecoat  
(ii) Clearcoat  
(iii) Non-basecoat/clearcoat  
3. Air-dried coatinginterior parts1,3  
4. Touch-up and repair3  
5.0  
4.5  
5.0  
5.0  
5.2  
1For red and black coatings, the emission limitation must shall be determined by multiplying the  
appropriate limit in this table by 1.15.  
69  
2When 40 CFR C.F.R. Ppart 60, Aappendix A, Mmethod 24 is used to determine the volatile organic  
compound content of a coating, the applicable emission limitation must shall be determined by adding 0.5  
to the appropriate limit in this table.  
3When 40 CFR C.F.R. Ppart 60, Aappendix A, Mmethod 24 is used to determine the volatile organic  
compound content of a coating, the applicable emission limitation must shall be determined by adding 0.1  
to the appropriate limit in this table.  
(214) Table 67 reads as follows:  
Table TABLE 67  
Volatile organic compound emission limitations for existing business machine plastic  
parts coating lines after 12/31/91  
Pounds of volatile organic compounds allowed  
Coating category  
to be emitted per gallon of coating (minus  
water) as applied  
1. Prime  
2. Topcoat  
3. Texture coat  
4. Fog coat  
5. Touch-up and repair  
2.9  
2.9  
2.9  
2.2  
2.9  
R 336.1633 Emission of volatile organic compounds from existing plastic parts and  
products surface coating; and pleasure craft coating operations in 2015 ozone  
nonattainment areas.  
Rule 633. (1) As used in this rule:  
(a) “Pleasure craft” means vessels that are manufactured or operated primarily  
for recreational purposes, or leased, rented, or chartered to a person for recreation  
purposes. The person responsible for the vessels is responsible for certifying that the  
intended use is for recreational purposes.  
(b) “Pleasure craft surface coating” means any marine coating, except  
unsaturated polyester resin (fiberglass) coatings, applied by brush, spray, roller, or  
other means to a pleasure craft.  
(2) A person shall not cause or allow the emission of any volatile organic  
compound from the surface coating of miscellaneous plastic parts and products, or  
pleasure craft coatings in excess of the limitations of this rule in miscellaneous  
plastic parts and products operations or pleasure craft operations from any existing  
source located within the 2015 ozone nonattainment area, in excess of the  
applicable emission rates provided in subrule (4) of this rule.  
(3) The provisions of this rule do not apply to the following:  
(a) With the exception of the requirements in subrule (6) of this rule,  
miscellaneous plastic parts or pleasure craft coating lines within any stationary  
source and that have a total combined actual emission rate of volatile organic  
compounds, including related cleaning activities, of less than 15 pounds per day  
before consideration of controls. If the combined actual emission rate equals or is  
70  
more than 15 pounds per day for a subsequent day, then this rule permanently  
applies to these coating lines.  
(b) The portion of a plastic parts and products surface coating and pleasure craft  
coating operations that is addressed in R 336.1610, R 336.1610a, R 336.1620,  
R 336.1620a, R 336.1635, R 336.1636, R 336.1637, R 336.1638, and R 336.1639.  
(c) Gel coats applied to fiber-reinforced plastic (fiberglass composite) products.  
(d) Body fillers and putties used to repair surface defects in fiberglass composite  
parts, or putties used to bond fiberglass composite parts together.  
(e) The following plastic parts coatings processes are exempt from subrule (4) of  
this rule:  
(i) Touch-up and repair coatings.  
(ii) Stencil coatings applied on clear or transparent substrates.  
(iii) Clear or translucent coatings.  
(iv) Coatings applied at a paint manufacturing facility while conducting  
performance tests on the coatings.  
(v) Any individual coating category used in volumes less than 50 gallons in any 1  
year, if substitute compliant coatings are not available, if the total usage of all  
coatings does not exceed 200 gallons per year, per facility.  
(vi) Reflective coating applied to highway cones.  
(vii) Mask coatings that are less than 0.5 millimeter thick (dried) and the area  
coated is less than 25 square inches.  
(viii) Electromagnetic interference/radio frequency interference shielding  
coatings.  
(ix) Heparin-benzalkonium chloride containing coatings applied to medical  
devices, if the total usage of all such coatings does not exceed 100 gallons per year,  
per facility.  
(4) A person shall not cause or allow the emission of any volatile organic  
compound from surface coatings from plastic parts and product operations or from  
surface coatings from pleasure craft operations, unless the following provisions are  
met:  
(a) A person responsible for the coating line engaged in the surface coating of  
existing miscellaneous plastic parts and products, and surface coating of pleasure  
crafts in the 2015 ozone nonattainment areas shall limit volatile organic compound  
emissions from all volatile organic compound-containing materials, such as coatings,  
thinners, and other additives, used by each miscellaneous plastic parts and  
products, and pleasure craft surface coating line by complying with either  
subdivision (c), (d), or (e) of this subrule.  
(b) A person subject to this rule shall not apply volatile organic compound-  
containing coatings to existing miscellaneous plastic parts and products, or pleasure  
craft surfaces subject to the provisions of this rule, unless the coating is applied with  
properly operating equipment according to an operating procedure specified by the  
equipment manufacturer, executive officer, or designee, and by the use of 1 of the  
following methods:  
(i) Electrostatic attraction.  
(ii) Flow coat.  
(iii) Dip coat.  
71  
(iv) Roll coater.  
(v) High-Volume, Low-Pressure (HVLP) Spray.  
(vi) Airless spray.  
(vii) Air-assisted airless spray.  
(viii) A person subject to this rule may request, in writing to the department, and  
the department may approve, other coating application methods that demonstrate  
the capability of achieving a transfer efficiency equivalent to or better than that  
achieved by HVLP spraying.  
(c) A miscellaneous plastic parts coating and pleasure craft coating operation must  
not cause or allow the emission of volatile organic compounds from the coating of  
metallic surfaces from any plastic parts or pleasure craft coating line in any of the  
2015 ozone nonattainment areas in excess of the applicable content limits, expressed  
in terms of mass of volatile organic compound per volume of coating excluding  
water and exempt compounds, as applied, as specified in table 68 and table 68-a, or  
emission rates expressed in terms of mass of volatile organic compound per volume  
of solids as applied, as specified in table 68-b and table 68-c:  
TABLE 68  
Plastic Parts and Products Volatile Organic Compound Content Limits  
Coating Category  
lbs VOC/gal coating  
General 1 Component  
2.3  
General Multi Component  
Electric Dissipating Coatings and Shock-Free Coatings  
Extreme Performance  
3.5  
6.7  
3.5 (2-pack coatings)  
Metallic  
3.5  
Military Specification  
2.8 (1-pack)  
3.5 (2-pack)  
Mold-Seal  
6.3  
5.7  
6.7  
6.7  
Multi-colored Coatings  
Optical Coatings  
Vacuum-Metalizing  
TABLE 68-a  
Pleasure Craft Surface Coating Volatile Organic Compound Content Limits  
lbs VOC/gal coating  
lbs VOC/gal coating  
Before January 1, 2026  
On or after January 1, 2026  
Coating Category  
Extreme High Gloss Topcoat  
High Gloss Topcoat  
Pretreatment Wash Primers  
Finish Primer/Surfacer  
High Build Primer Surfacer  
5.0  
3.5  
6.5  
5.0  
2.8  
4.1  
3.5  
6.5  
3.5  
2.8  
72  
Aluminum Substrate  
Antifoulant Coating  
Other Substrate Antifoulant  
Coating  
All other pleasure craft surface 3.5  
coatings for metal or plastic  
4.7  
3.4  
4.7  
2.8  
3.5  
TABLE 68-b  
Plastic Parts and Products Volatile Organic Compound Emission Rate Limits  
Coating Category  
lbs VOC/gal solids  
General 1 Component  
3.35  
General Multi Component  
Electric Dissipating Coatings and Shock-Free Coatings  
Extreme Performance  
6.67  
74.7  
6.67 (2-pack coatings)  
Metallic  
6.67  
Military Specification  
4.52 (1-pack)  
6.67 (2-pack)  
43.7  
Mold-Seal  
Multi-colored Coatings  
Optical Coatings  
Vacuum-Metalizing  
25.3  
74.7  
74.7  
TABLE 68-c  
Volatile organic compound emissions limitations for existing pleasure craft surface  
coating lines.  
lbs VOC/gal solids  
lbs VOC/gal solids  
Before January 01, 2026  
On or after January 01, 2026  
Coating Category  
Extreme high gloss topcoat  
High gloss topcoat  
15.5  
6.7  
9.2  
6.7  
Pretreatment wash primers  
Finish primer/surfacer  
High build primer surfacer  
Aluminum substrate  
antifoulant coating  
55.6  
15.5  
4.6  
55.6  
6.7  
4.6  
12.8  
12.8  
Other substrate antifoulant  
coating  
All other pleasure craft  
surface coatings for metal or  
plastic  
6.3  
6.7  
4.4  
6.7  
73  
(d) A miscellaneous plastic parts coating and pleasure craft coating operation  
applicable to this rule can choose to use an equivalent volatile organic compound  
emission rate limit based on the use of a combination of low-volatile organic  
compound coatings specified in table 68 to table 68-c, specified methods of  
application specified under subdivision (b) of this subrule, and add-on controls. The  
overall emission reduction efficiency needed to demonstrate compliance is  
determined each day as follows:  
(i) Obtain the emission limitation from table 68 to table 68-c. If using the pound of  
volatile organic compound per gallon of coating, excluding water, as applied limit  
from table 68 or table 68-b, then calculate the emission limitation in a solids basis  
according to the following equation:  
S = C / [1 (C/7.36 lb/gal)]  
Where:  
S = The volatile organic compound emission limitation in terms of pound of  
volatile organic compound per gallon of coating solids.  
C = The volatile organic compound emission limitation in terms of pound of  
volatile organic compound per gallon of coating, (excluding water) as applied.  
(ii) Calculate the required overall emission reduction efficiency of the control  
system for the day according to the following equation:  
E = [(VOCa S)/VOCa] x 100  
Where:  
E = The required overall emission reduction efficiency of the control system for  
the day.  
VOCa = The maximum VOC content of the coatings, as applied, used each day on  
the subject coating line, in units of lb VOC/gal coating solids, as determined by the  
applicable test methods and procedures specified in subdivision (h) of this subrule.  
S = The volatile organic compound emission limitation in terms of pound of  
volatile organic compound per gallon of coating solids.  
(e) Should product performance requirements or other needs dictate the use of  
higher-volatile organic compound materials than those that would meet the  
recommended emission limits, a facility can choose to use add-on control equipment  
that must have an overall control efficiency of 90% or higher instead of using low-  
volatile organic compound coatings and specified application methods.  
(f) For each coating line, compliance with the emission limits specified in this rule  
is based upon all of the following:  
(i) The volume-weighted average of all coatings that belong to the same coating  
category, and are used during each calendar day averaging period. The department  
may specifically authorize compliance, under R 336.1602(2), to be based upon a  
longer averaging period, not to exceed more than 1 calendar month.  
74  
(ii) If coatings belonging to more than 1 coating category are used on the same  
coating line during the specified averaging period, then compliance must be  
determined separately for each coating category.  
(iii) The information and records as required by subrule (6) of this rule.  
(g) Compliance with the emission limits specified in subrule (4) of this rule, must  
be determined using the method described in either R 336.2040(12)(a) if the coating  
line does not have an add-on emissions control device or R 336.2040(12)(b) if the  
coating line has 1 or more add-on emissions control devices.  
(5) The following work practices are required for storage, mixing operations, and  
handling operations for coatings, thinners, cleaning, and coating-related waste  
materials. The person responsible for a miscellaneous plastic parts coating and  
pleasure craft coating operation shall develop written procedures for compliance  
with the following provisions:  
(a) Store all volatile organic compound-containing coatings, thinners, coating-  
related waste, and cleaning materials in closed containers.  
(b) Ensure that mixing and storage containers used for volatile organic compound-  
containing coatings, thinners, coating-related waste, and cleaning materials are kept  
closed at all times, except when depositing or removing these materials.  
(c) Minimize spills of volatile organic compound-containing coatings, thinners,  
coating-related waste, and cleaning materials.  
(d) Convey volatile organic compound-containing coatings, thinners, coating-  
related waste, and cleaning materials from 1 location to another in closed containers  
or pipes.  
(e) Minimize volatile organic compound emissions from cleaning of application,  
storage, mixing, and conveying equipment by ensuring that equipment cleaning is  
performed without atomizing the cleaning solvent and all spent solvent is captured  
in closed containers.  
(6) A person that is responsible for the operation of a coating line that is subject to  
this rule shall obtain current information and maintain daily records necessary for  
the determination of compliance with the provisions of this rule, as required in R  
336.2041.  
R 336.1634 Emissions of volatile organic compounds from existing industrial  
solvent cleaning in 2015 ozone nonattainment areas.  
Rule 634. (1) As used in this rule, composite partial vapor pressure” means the  
sum of the partial pressures of the VOC compounds in a solvent.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from the use of solvent materials in excess of the limitations of this rule in solvent  
cleaning operations, which are described as follows:  
(a) Released during the production, repair, maintenance, or servicing of parts,  
products, tools, machinery, equipment or in general work areas including storage or  
disposal of these solvent materials.  
(b) Located in the 2015 ozone nonattainment area.  
(3) With the exception of subrule (6) of this rule, the provisions of this rule do not  
apply to the following activities:  
(a) Janitorial cleaning.  
75  
(b) Stripping of cured coatings, cured ink, or cured adhesives.  
(c) Cleaning operations in printing pre-press or graphic areas including  
lithographic, letterpress, flexographic, screen printing, and rotogravure printing  
operations.  
(d) Cleaning operations associated with digital printing.  
(e) Cleaning operations for which limits or work practice standards are contained  
within R 336.1610, R 336.1610a, R 336.1620, R 336.1620a, R 336.1621,  
R 336.1621a, R 336.1624, R 336.1624a, R 336.1632, R 336.1633, R 336.1635,  
R 336.1636, R 336.1637, R 336.1638, and R 336.1639.  
(f) Cleaning operations at a facility with emissions less than 3 tons per rolling 12-  
month period for all cleaning activity, before consideration of controls. If the  
combined actual emission rate equals or is more than 3 tons per year on a 12-  
month rolling basis before consideration of controls, as determined in a  
subsequent month, then this rule permanently applies to the cleaning operations at  
that facility.  
(4) A person that generates volatile organic compound from the use of industrial  
cleaning solvent shall meet the following provisions:  
(a) The volatile organic compound emissions from the process must meet 1 of the  
following:  
(i) The solvent or solvent solutions must have a volatile organic compound  
composite partial vapor pressure of less than or equal to 8 mm of Hg at 20 degrees  
Celsius.  
(ii) The process must have an emission rate of 0.42 pounds of volatile organic  
compounds per gallon as applied, except as described for the solvent cleaning  
operations listed in table 68-d.  
TABLE 68-d  
Pounds of volatile  
organic compounds  
allowed to be  
emitted per gallon as  
Solvent Cleaning Operation  
applied  
(i.) Product cleaning during manufacturing process or  
surface preparation for coating, adhesive, or ink  
application:  
1. Electrical apparatus components and electronic  
components  
2. Medical devices and pharmaceuticals  
0.83  
6.7  
(ii.) Repair and maintenance cleaning:  
1. Electrical apparatus components and electronic  
components  
0.83  
2. Medical devices and pharmaceuticals:  
(i.) Tools, equipment, and machinery  
(ii.) General work surfaces  
76  
6.7  
5.0  
(iii.) Cleaning of ink application equipment:  
1. Publication gravure printing  
0.83  
4.2  
5.4  
2. Screen printing  
3. Ultraviolet ink and electron beam ink application  
equipment, except screen printing  
0.83  
N/A  
4. Specialty flexographic printing  
(iv.) Exemptions from emissions limits in this subdivision:  
1. Cleaning conducted as part of the following:  
performance laboratory tests on coatings,  
adhesives, or inks; research and development  
programs; and laboratory tests in quality  
assurance laboratories.  
2. Medical device and pharmaceutical facilities using  
up to 1.5 gallons per day of solvents.  
3. Cleaning with aerosol products if the source uses  
1.25 gallons or less per day  
(b) A person subject to this rule shall utilize all of the following cleaning devices  
and methods as applicable:  
(i) Wipe cleaning.  
(ii) Closed containers or hand-held spray bottles from which solvents are applied  
without a propellant-induced force.  
(iii) Cleaning equipment that has a solvent container that can be, and is closed  
during cleaning operations, except when depositing and removing objects to be  
cleaned, and is closed during non-operation with the exception of maintenance and  
repair to the cleaning equipment itself.  
(iv) Remote reservoir cleaner if the operator of the cleaner complies with all of the  
following:  
(A) Prevents solvent vapors from escaping from the solvent container by using  
such devices as a cover or valve when the remote reservoir is not being used,  
cleaned, or repaired.  
(B) Directs solvent flow in a manner that prevents liquid solvent from splashing  
outside of the remote reservoir cleaner.  
(C) Does not clean porous or absorbent materials, such as cloth, leather, wood, or  
rope.  
(D) Uses only solvent containers and auxiliary equipment free of all liquid leaks.  
visible tears, or cracks.  
(v) Non-atomized solvent flow method where the cleaning solvent is collected in a  
container or a collection system that is closed except for solvent collection openings  
and, if necessary, openings to avoid excessive pressure build-up inside the container.  
(vi) Solvent flushing method where the cleaning solvent is discharged into a  
container that is closed except for solvent collection openings and, if necessary,  
openings to avoid excessive pressure build-up inside the container. The discharged  
77  
solvent from the equipment must be collected into containers without atomizing into  
the open air.  
(c) Instead of complying with subdivisions (a) and (b) of this subrule for a solvent  
cleaning operation, a person that is subject to this rule may comply by installing and  
operating volatile organic compound emission control equipment for the solvent  
cleaning operation. The volatile organic compound emission control equipment  
must have an overall control efficiency of 85%.  
(d) Instead of complying with subdivisions (a) and (b) of this subrule, a  
manufacturer of coatings, inks, resins, or adhesives may comply with subdivision  
(e) of this subrule or the following:  
(i) Clean portable tables or stationary mixing vats, high dispersion mills, grinding  
mills, tote tanks, and roller mills by 1 or more of the following methods:  
(A) Use a cleaning solvent that either contains less than 1.67 pounds per gallon of  
volatile organic compound or has a composite vapor pressure no more than 8 mm of  
Hg at 20 degrees Celsius.  
(B) Comply with the following work practices:  
(1) Equipment being cleaned must be maintained leak free.  
(2) Volatile organic compound-containing cleaning materials must be drained  
from the cleaned equipment upon completion of cleaning.  
(3) Volatile organic compound-containing cleaning materials, including waste  
solvent, must not be stored or disposed of in a manner that causes or allows  
evaporation into the atmosphere.  
(4) Store all volatile organic compound-containing cleaning materials in closed  
containers.  
(C) Collect and vent the emissions from equipment cleaning to a volatile organic  
compound emission control system that has an overall capture and control  
efficiency of not less than 85%, by weight, for the volatile organic compound  
emissions. If such a reduction is achieved by incineration, not less than 90% of the  
organic carbon must be oxidized to carbon dioxide.  
(D) Use organic solvents other than those allowed in subdivision (f)(i) of this  
subrule provided no more than 60 gallons of fresh solvent must be used per month.  
Organic solvent that is reused or recycled, either on-site or off-site, for further use  
in equipment cleaning or the manufacture of coating, ink, or adhesive must not be  
included in this limit. Also, store all volatile organic compound-containing cleaning  
materials in closed containers.  
(ii) When using solvent for wipe cleaning, a person shall cover open containers  
used for the storage or disposal of cloth or paper impregnated with organic  
compounds that have been used for cleanup, or coating, ink, or adhesive removal.  
(e) Work practices must be used to minimize volatile organic compound  
emissions from the use, handling, storage, and disposal of cleaning solvents and  
shop towels. Work practices must include, at a minimum, but not limited to, the  
following:  
(i) All volatile organic compound-containing solvents used in solvent cleaning  
operations must be stored in non-absorbent, non-leaking containers which must  
be kept closed at all times except when filling or emptying.  
78  
(ii) Cloth and paper moistened with volatile organic compound-containing  
solvents must be stored in closed, non-absorbent, non-leaking containers.  
(iii) Air circulation around cleaning operations must be minimized.  
(f) Except as allowed by this subrule, a person shall not atomize any solvent unless  
the emissions are vented to volatile organic compound emission control equipment  
that meets subdivision (c) of this subrule. The following activities are allowed to  
atomize solvent without use of a control:  
(i) Cleaning of the nozzle tips of automated spray equipment systems, except for  
robotic systems.  
(ii) Cleaning with spray bottles or containers described in subdivision (b)(ii) of  
this subrule.  
(iii) Printing operations where the roller or blanket wash is applied automatically.  
(5) Compliance with this rule must be determined as follows:  
(a) For limits specified in subrule (4)(a) of this rule, compliance must be based  
upon all volatile organic containing compounds using manufacturers formulation  
data, United States Environmental Protection Agency method 24 analysis, safety  
data sheets, an alternate method, or combination of the methods stated within this  
subdivision, as approved by the department and in sufficient detail to demonstrate  
compliance with the limitations described in subrule (4) of this rule.  
(b) If a person responsible for a solvent cleaning operation that is subject to this  
rule employs volatile organic compound emission control equipment to comply with  
this rule, pursuant to subrule (4)(c) of this rule:  
(i) Compliance with required control efficiency limits must be determined by  
performing emission tests in accordance with a stack testing protocol approved by  
the department.  
(ii) Additional testing of the volatile organic compound emission control  
equipment for a solvent cleaning operation in accordance with this rule may be  
required by the department to ensure continued compliance.  
(c) As appropriate, the composite partial vapor pressure of solvents must be  
determined by using generally acceptable methods including, but not limited to,  
ASTM standards, commonly published materials and references, or standard  
chemical laws and calculations.  
(6) A person operating a solvent cleaning operation shall obtain current  
information and maintain records for all requirements in sufficient detail to  
determine compliance and make the records available to the department upon  
request. The following methods must be used:  
(a) The person operating a solvent cleaning operation that is subject to 1 or more  
of the volatile organic compound-content limitations or exemptions specified in  
subrule (4) of this rule shall collect and record the following information for each  
cleaning material subject to a volatile organic compound-content limitation as  
necessary to determine compliance with that limitation:  
(i) The name and identification of each cleaning material and the associated  
solvent cleaning activity.  
(ii) The volatile organic compound content, of each cleaning material, as  
determined in subrule (5) of this rule, in pounds per gallon of material, as employed  
79  
or the volatile organic compound composite partial vapor pressures of the solvents  
or solvent solutions used in the industrial cleaning operations.  
(iii) The volume, in gallons, of each solvent employed in the solvent cleaning  
operation.  
(iv) The total volume, in gallons, of all the solvents employed in the solvent  
cleaning operation.  
(b) If a person operating a solvent cleaning operation employs a control device to  
achieve and maintain compliance, that person shall create and submit an  
approvable preventative maintenance and monitoring plan to the department  
which includes details about all appropriate parameters to be monitored and  
recordkeeping sufficient to determine compliance.  
(c) A person exempting their solvent cleaning operations as allowed by subrule (3)  
of this rule shall maintain all information necessary to demonstrate, in sufficient  
detail, the applicability of those exemptions and must provide that information to  
the department upon request.  
R 336.1635 Emission of volatile organic compounds from existing offset  
lithographic and letterpress printing lines in 2015 ozone nonattainment areas.  
Rule 635. (1) As used in this rule:  
(a) “Batch” means a supply of fountain solution that is prepared and used without  
alteration until completely used or removed from the printing process. Batch applies  
to solutions prepared in discrete batches or solutions that are continuously blended  
with automatic mixing units. A fountain solution that is continuously blended with  
an automatic mixing unit is considered to be the same batch until the recipe or mix  
ratio is changed.  
(b) “Cleaning solution” means liquid solvents or solutions used to remove ink and  
debris from the operating surfaces of the printing press and its parts including  
blanket washes, roller washes, plate cleaners, metering roller cleaners, impression  
cylinder cleaners, rubber rejuvenators, and other cleaners used for cleaning a press,  
press parts, or to remove dried ink from the areas around a press. Cleaning solution  
does not include cleaners used on electronic components of a press, pre-press  
cleaning operations, post-press cleaning operations, cleaning supplies used to clean  
the floor of the area around a press, other than dried ink, or cleaning performed in  
parts washers or cold cleaners.  
(c) “Letterpress printing line” means all operations of  
letterpress printing processes characterized by the image area being raised relative  
to the nonimage area and including, but not limited to, pre-press and post-press  
operations that support the activity. Varnishes, glues, and other coatings that are  
applied by an offset lithographic printing process are part of offset lithographic  
printing operations and are not considered as a separate process, for example, paper  
coating.  
(d) “Non-heatset” means a lithographic printing process where the printing inks  
are set without the use of heat and dry by absorption or oxidation , or  
both. For the purposes of this rule, use of an infrared heater or printing conducted  
using ultraviolet-cured or electron beam-cured inks is considered non-heatset.  
80  
(e) Offset lithographic printing line” means offset printing presses characterized  
by a planographic plate where the image and nonimage area are in the same  
geographical plane and the related processes necessary to directly support the  
operation of those offset lithographic printing processes including, but not limited  
to, pre-press and post-press operations. Varnishes, glues, and other coatings that are  
applied by an offset lithographic printing process are part of offset lithographic  
printing operations and are not considered as a separate process, for example, paper  
coating.  
(f) “Printing processmeans any equipment, operation, or system where printing  
ink or a combination of printing ink, surface coating, or adhesive is applied, dried,  
or cured. A printing process may  
include any equipment that applies, conveys, dries, or cures inks or surface coatings  
including, but not limited to, presses, digital output devices, fountain solutions,  
heaters, and dryers.  
Commented [GJ9]: It is not clear what this means so I  
suggest it should be deleted as it will cause confusion.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from an offset lithographic and letterpress printing line located in the 2015 ozone  
nonattainment area, in excess of the applicable emission rates indicated in the  
following subrules, unless all of the applicable provisions of the following subrules  
are met.  
(3) Except as provided in subrule (6) of this rule, the provisions of this rule do not  
apply to the following:  
(a) All offset lithographic and letterpress printing operations, including cleaning  
activities, before consideration of controls, that have volatile organic compound  
emissions less than or equal to 3 tons per rolling 12-month period.  
Commented [GJ10]: Please delete this once in always in  
provision as it is not supported by current EPA  
requirements. It is not in the CTG for offset lithographic  
printing or letterpress printing.  
(b) In lieu of calculating emissions to establishing that the facility's total actual VOC  
emissions, before the application of control systems and devices, from all  
lithographic or letterpress printing operations (including emissions from cleaning  
solutions used on lithographic or letterpress printing presses and fountain solutions)  
are less than three tons of VOCs per rolling twelve-month period the owner or  
operator may monthly records of material usage demonstrating the following  
thresholds have not been exceeded:  
Formatted: Font: (Default) Times New Roman  
Type of Letterpress or Offset Lithographic12-Month Rolling Threshold  
Printing Operation  
Sheet-fed only  
768 gallons of cleaning solvent and  
fountain solution additives  
Non-heatset Web only  
768 gallons of cleaning solvent and  
fountain solution additives  
81  
Combination of Sheet-fed and Non-heatset 768 gallons of cleaning solvent and  
Web  
fountain solution additives.  
Heatset Web only  
5400 pounds of ink, cleaning solvent and  
fountain solution additives  
A facility that employs a combination of printing technologies that includes a heatset  
web offset lithographic printing press may not use this option for demonstrating  
actual emissions are less than three tons of VOCs per rolling twelve-month period.  
Commented [GJ11]: This allows smaller facilities to  
determine if the rule is applicable to them without having to  
perform complex emission calculations.  
(b) One hundred and ten gallons of cleaning materials that do not meet either  
requirement in subrule (4)(e)(i) per rolling 12-month period used at the stationary  
source.  
(c) The fountain solutions of sheet fed offset lithographic presses with a sheet size  
of 11 by 17 inches or smaller.  
(d) The fountain solutions of any offset lithographic press with fountain solution  
reservoirs totaling less than 1 gallon.  
(e) A person operating an offset lithographic and letter press printing line may  
exclude low-use inks or coatings that total 55 gallons or less per rolling 12-month  
period at a stationary source from the provisions of this rule, except for subrule (6)  
of this rule.  
Commented [GJ12]: Exclude from what? The applicability  
determination?  
(f) The following operations are exempt from add-on control requirements  
described in subrule (4) of this rule:  
(i) Any heatset web offset lithographic press or heatset web letterpress with  
potential volatile organic compound emissions less than 25 tpy before control from  
the dryer.  
In lieu of calculating emissions to establish that the heatset web offset lithographic  
or heatset web letterpress printing press potential VOC ink oil emissions, before  
control, from the press dryer of any heatset web offset lithographic printing press or  
heatset web letterpress printing press are less than twenty-five tons per year the  
owner or operator may maintain monthly records of material usage demonstrating  
the following threshold has not been exceeded:  
Commented [GJ13]: This allows smaller facilities to  
determine if the rule is applicable to them without having to  
perform complex emission calculations.  
Formatted: No bullets or numbering  
Threshold Heatset Only  
25 tons per press per year  
12-Month Rolling Threshold  
62,500 pounds of ink and varnish  
(ii) Any heatset web offset lithographic press or heatset web letterpress that is  
limited through a federally enforceable permit to actual volatile organic compound  
emissions from the dryer less than 25 tpy from the dryer.  
(iii) Any heatset web offset lithographic or heatset letterpress press used for book  
printing with a web width of 22 inches or less.  
(4) A person shall not cause or allow the emission of any volatile organic compound  
from an existing offset lithographic or letterpress printing line, unless the following  
82  
provisions are met or unless an equivalent control method, as approved by the  
department under R 336.1602(2), is implemented:  
(a) Except as described in subrule (3) of this rule, a control system is required for  
dryer operations of heatset web offset lithographic printing and heatset letterpress  
printing operations. Each dryer must meet 1 of the following control requirements:  
(i) 90% control efficiency for dryers installed before the effective date of this rule.  
(ii) 95% control efficiency for dryers installed after the effective date of this rule.  
(iii) Maintain a maximum outlet concentration of volatile organic compounds of  
20 ppmv as hexane on a dry basis.  
(b) The fountain solution used in a heatset web offset lithographic printing line has  
a volatile organic compound content that meets 1 of the following requirements:  
(i) The fountain solution, as applied, must be at or below 1.6% alcohol by weight.  
(ii) If refrigerated to below 60 degrees Fahrenheit, the fountain solution, as  
applied, must be at or below 3% alcohol by weight.  
(iii) The fountain solution, as applied, must contain 5% or less of alcohol  
substitute and no alcohol.  
(iv) Where it can be demonstrated to the satisfaction of the director that a subject  
offset lithographic printing press cannot be operated with fountain solutions  
meeting the limits in paragraph (b)(i), (b)(ii), or (b)(iii) of this rule for reasons of  
technological or economic feasibility the permitting authority may establish site-  
specific limits based upon evidence of technological or economic infeasibility subject  
to approval by USEPA as a state implementation plan revision.  
(c) The fountain solution used in a sheet-fed offset lithographic printing line must  
have a volatile organic compound content that meets 1 of the following  
requirements:  
Commented [GJ14]: The provides the printing operation  
some flexibility if they are not able to meet the fountain  
solution limits.  
(i) The fountain solution, as applied, must be at or below 5% alcohol by weight.  
(ii) If refrigerated to below 60 degrees Fahrenheit, the fountain solution, as  
applied, must be at or below 8.5% alcohol by weight.  
(iii) Where it can be demonstrated to the satisfaction of the director that a subject  
offset lithographic printing press cannot be operated with fountain solutions  
meeting the limits in paragraph (c)(i) or (c)(ii) of this rule for reasons of  
technological or economic feasibility the permitting authority may establish site-  
specific limits based upon evidence of technological or economic infeasibility subject  
to approval by USEPA as a state implementation plan revision.  
Commented [GJ15]: The provides the printing operation  
some flexibility if they are not able to meet the fountain  
solution limits.  
(d) Nonheatset web offset lithographic printing press must be less than 5% alcohol  
substitute by weight on press and no alcohol in the fountain solution. Where it can  
be demonstrated to the satisfaction of the director that a subject offset lithographic  
printing press cannot be operated with fountain solutions meeting the limits in  
paragraph (d) of this rule for reasons of technological or economic feasibility the  
permitting authority may establish site-specific limits based upon evidence of  
technological or economic infeasibility subject to approval by USEPA as a state  
implementation plan revision.  
Commented [GJ16]: The provides the printing operation  
some flexibility if they are not able to meet the fountain  
solution limits.  
(e) The cleaning solutions used with printing lines subject to this rule must meet 1  
of the following requirements:  
83  
(i) The cleaning solutions must have a volatile composite vapor pressure of less  
than 10 mm Hg at 20 degrees Celsius or be less than 70% volatile organic compound  
by weight.  
(ii) All cleaning materials and used shop towels must be kept in closed containers.  
(5) Compliance with the emission limits specified in this rule must be based upon  
all of the following provisions, as applicable:  
(a) Compliance with required control efficiency limits must be determined by  
performing emission tests in accordance with (Reference the appropriate section in  
1040 or 1041 and a stack testing protocol approved by the department.  
(b) Compliance with the emission limits specified in subrule (4) of this rule must  
be based upon all volatile organic containing compounds used during each calendar  
month by using manufacturers’ formulation data, United States Environmental  
Protection Agency method 24 analysis, safety data sheets, an alternate method, or  
combination of the methods stated within this subdivision, as approvable by the  
department and in sufficient detail to demonstrate compliance with the limitations  
described in subrule (4) of this rule.  
(c) If more than 1 control option or emission limit listed in subrule (4) of this rule  
is used on a printing line, then compliance must be determined separately for each  
option used and be based upon all materials used for each option during each  
period.  
(6) For the purpose of this rule, recordkeeping for all requirements and  
applicability demonstrations must be maintained in sufficient detail to demonstrate  
compliance with all applicable standards of the rule. Records must include, but are  
not limited to, the following:  
(a) The volume and volatile organic compound content of each alcohol and alcohol  
substitute added to make the batch of fountain solution, based upon the approvable  
method described in subrule (5)(b) of this rule.  
(b) The calculated volatile organic compound content of the final, mixed batch of  
solution, as applied.  
(c) All cleaning solutions employed in all the offset lithographic and letterpress  
printing operations and quantities for those subject to subrule (3)(b), either  
composite vapor pressure or volatile organic compound contents as necessary  
to demonstrate compliance with subrule (4) of this rule.  
(d) Monthly volatile organic compound emissions and materials usage as needed  
to demonstrate the emissions are below the thresholds described in subrule (3)  
of this rule.  
Commented [GJ17]: The only instance where the CTG  
requires records of solvent consumption to be kept are for  
the 110 gallons per 12 month rolling period for the solvents  
that don’t meet either the vapor pressure or VOC content  
limit.  
(e) Approvable retention factors must be utilized for volatile organic compound  
content in absorptive printed substrates and shop towels used in cleaning and used  
in emission calculations and control efficiencies. For purposes of determining VOC  
emissions from offset lithographic printing operations, the following retention  
factors and capture efficiencies shall be used:  
Commented [GJ18]: Monthly emission records would  
only be required to show that the facility is exempt from the  
requirements. Once applicable, the CTG does not require  
monthly emission records to be kept.  
(i) A portion of the VOC contained in inks and cleaning solution is retained in the  
printed substrate or in the shop towels used for cleaning. The following retention  
84  
factors shall be used:  
(a) A twenty per cent VOC retention factor shall be used for heatset inks  
printed on absorptive substrates, meaning eighty per cent of the VOC in  
the ink is emitted during the printing process and is available for capture  
and control by an add-on pollution control device.  
(b)A ninety-five per cent VOC retention factor shall be used for sheet-fed  
and non-heatset web inks printed on absorptive substrates, meaning five  
per cent of the VOC in the ink is emitted during the printing process.  
(c) A fifty per cent VOC retention factor shall be used for cleaning solution  
VOC in shop towels for cleaning solutions with a VOC composite vapor  
pressure of no more than ten mmHg at twenty degrees Celsius (sixty-eight  
degrees Fahrenheit) if the contaminated shop towels are kept in closed  
containers, meaning fifty per cent of the VOC used on the shop towels is  
emitted during the cleaning process.  
(ii) portion of the VOC contained in inks, fountain solutions, and automatic blanket  
washes on heatset web presses is captured in the press dryer for control by add- on  
pollution control devices. The following capture efficiencies shall be used:  
(a) A one hundred per cent VOC carry over efficiency shall be used for inks.  
All the VOC in the ink that is not retained is assumed to be volatilized in  
the press dryer. Capture efficiency testing for heatset dryers is not  
required if it is demonstrated that pressure in the dryer is negative  
relative to the surrounding press room and the airflow is into the dryer.  
(b)A seventy per cent VOC carry over efficiency shall be used for fountain  
solutions containing alcohol substitutes.  
(c) A forty per cent VOC carry over efficiency shall be used for automatic  
blanket wash solutions with a VOC composite vapor pressure of no more  
than ten mmHg at twenty degrees Celsius (sixty-eight degrees  
Fahrenheit).  
(7) Any offset lithographic or letter printing press line that utilizes control  
requirements to meet standards in subrule (4) of this rule must have an approvable  
operation and preventative maintenance plan. The plan must include, at a  
minimum, the following, as applicable:  
(a) A continuous temperature monitoring and recording system.  
(b) A maintenance schedule for all control equipment with spare part list.  
85  
(c) A malfunction abatement plan to be implemented in the event of abnormal  
situations involving the control equipment.  
R 336.1636 Emission of volatile organic compounds from existing miscellaneous  
industrial adhesives operations in 2015 ozone nonattainment areas.  
Rule 636. (1) As used in this rule:  
(a) “Electrodeposition” means a water-borne dip coating process in which  
opposite electrical charges are applied to the substrate and the coating. The coating  
is attracted to the substrate due to the electrochemical potential difference that is  
created.  
(b)“Flow coating” means a non-atomized technique of applying coating to a  
substrate with a fluid nozzle with no air supplied to the nozzle.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from the use of adhesives in excess of the limitations of this rule in miscellaneous  
industrial adhesive operations from any existing source located within the 2015  
ozone nonattainment area, in excess of the applicable emission rates provided in  
subrule (4) of this rule.  
(3) The provisions of this rule do not apply to the following:  
(a) Except as provided in subrule (7) of this rule, any miscellaneous industrial  
adhesive operations at a stationary source that has a total combined actual emission  
rate of volatile organic compounds equal to or less than 3 tons per 12-month rolling  
period, before consideration of control equipment. If the combined actual emission  
rate equals or is more than 3 tons per year on a 12-month rolling basis before  
consideration of controls, as determined in a subsequent month, then this rule  
permanently applies to the applicable operations at that facility.  
(b) The portion of an adhesive process that is addressed in R 336.1610,  
R 336.1610a, R 336.1620, R 336.1620a, R 336.1624, R 336.1624a, R 336.1635, or  
R 336.1637.  
(c) The provisions of subrule (4) of this rule do not apply to the following:  
(i) Adhesive or adhesive primers being tested or evaluated in any research and  
development operation or quality assurance or analytical laboratory.  
(ii) Adhesives or adhesive primers used in the assembly, repair, or manufacture of  
aerospace or undersea-based weapon systems.  
(iii) Adhesives or adhesives primers used in medical equipment manufacturing  
operations.  
(iv) Aerosol adhesive and aerosol adhesive primer application operations.  
(v) Operations using adhesives and adhesive primers that are supplied to the  
manufacturer in containers with a net volume of 16 ounces, or a net weight of 1  
pound or less.  
(vi) Cyanoacrylate adhesive application operations.  
(vii) Operations using polyester bonding putties to assemble fiberglass parts at  
fiberglass boat manufacturing facilities and at other reinforced plastic composite  
manufacturing facilities.  
(viii) Digital printing operations.  
86  
(4) A person shall not cause or allow the emission of volatile organic compounds  
from miscellaneous industrial adhesive application operations, unless the following  
provisions are met:  
(a) A person with a source subject to the requirements of this rule shall comply  
with the limitations in subdivision (b) or (c) of this subrule unless a demonstration is  
made to the satisfaction of the department under R 336.1602(2).  
(b) A person with adhesive application operations listed in table 69 shall comply  
with the following volatile organic compound emission limitations, minus water and  
exempt compounds, as applied, using 1 or more of the application methods listed  
within this subdivision. If an adhesive is used to bond dissimilar substrates together,  
the substrate category with the highest volatile organic compound emission  
limitation applies:  
(i) Electrostatic spray.  
(ii) High volume low pressure (HVLP) spray.  
(iii) Flow coating.  
(iv) Roll coating or hand application, including non-spray application methods  
similar to hand or mechanically powered caulking gun, brush, or direct hand  
application.  
(v) Dip coating, including electrodeposition.  
(vi) Airless spray.  
(vii) Air-assisted airless spray.  
(viii) An equivalent adhesive application method approved in writing by the  
department.  
TABLE 69  
Volatile organic compound emission limitations for existing general and specialty  
adhesive application operations.  
Substrate Category  
Pounds of volatile organic compounds  
allowed to be emitted per gallon of  
coating (minus water) as applied.  
General Adhesive Application Operations  
Reinforced plastic composite  
Flexible vinyl  
1.7  
2.1  
0.3  
1.0  
2.1  
0.3  
2.1  
Metal  
Porous material (except wood)  
Rubber  
Wood  
Other substrates  
Specialty Adhesive Application Operations  
Ceramic tile installation  
Contact adhesive  
1.1  
2.1  
1.3  
Cover base installation  
87  
Floor covering installation (indoor)  
Floor covering installation (outdoor)  
Floor covering installation (perimeter  
bonded sheet vinyl)  
1.3  
2.1  
5.5  
Metal to urethane/rubber molding or  
casting  
7.1  
Motor vehicle adhesive  
2.1  
6.3  
1.7  
3.3  
4.2  
7.1  
2.1  
Motor vehicle weatherstrip adhesive  
Multipurpose construction  
Plastic solvent welding (ABS)  
Plastic solvent welding (except ABS)  
Sheet rubber lining installation  
Single-ply roof membrane  
installation/repair (except EPDM)  
Structural glazing  
0.8  
6.5  
0.8  
1.4  
Thin metal laminating  
Tire repair  
Waterproof resorcinol glue  
Adhesive primer application operations  
Motor vehicle glass bonding primer  
Plastic solvent welding adhesive primer  
Single-ply roof membrane adhesive  
primer  
7.5  
5.4  
2.1  
Other adhesive primer  
2.1  
(c) As an alternative to meeting subdivisions (a) and (b) of this subrule, a person  
with a source subject to this rule shall employ a capture system and control device  
that provides not less than 85% reduction in the overall emissions of volatile organic  
compound from the application operation. The adhesive operation would not have  
to limit the volatile organic compound content of the adhesive materials and would  
not need to use any particular adhesive application method.  
(5) A person subject to this rule shall develop written procedures for compliance  
with the following work practices for each miscellaneous adhesive application  
operation at the source:  
(a) Store all volatile organic matter-containing adhesives, adhesive primers,  
process-related waste materials, cleaning materials, and used shop towels in closed  
containers.  
(b) Ensure that mixing and storage containers used for volatile organic compound-  
containing adhesives, adhesive primers, process-related waste materials, and  
88  
cleaning materials are kept closed at all times except when depositing or removing  
these materials.  
(c) Minimize spills of volatile organic compound-containing adhesives, adhesive  
primers, process-related waste materials, and cleaning materials.  
(d) Convey volatile organic compound-containing adhesives, adhesive primers,  
process-related waste materials, and cleaning materials from 1 location to another  
in closed containers or pipes.  
(e) Minimize volatile organic compound emissions from the cleaning of  
application, storage, mixing, and conveying equipment by ensuring that equipment  
cleaning is performed without atomizing the cleaning solvent and all spent solvent is  
captured in closed containers.  
(6) Compliance with this rule is determined as follows:  
(a) For the emission limits specified in this rule, use the following methods:  
(i) For the emission limits specified in subrules (4)(b) of this rule, the method  
described in either R 336.2040(12)(a) if the adhesive line does not have an add-on  
emissions control device or R 336.2040(12)(b) if the adhesive line has 1 or more add-  
on emissions control devices.  
(ii) For the overall control efficiency specified in subrule (4)(c) of this rule, the  
method described in R 336.2040(11).  
(b) For each adhesive line, all of the following:  
(i) The volume-weighted average of all adhesives that belong to the same adhesive  
category, and are used during each calendar day averaging period. The department  
may specifically authorize compliance, under R 336.1602(2), to be based upon a  
longer averaging period, not to exceed more than 1 calendar month.  
(ii) If adhesives that belong to more than 1 adhesive category are used on the  
same adhesive line during the specified averaging period, then compliance must be  
determined separately for each coating category.  
(iii) The information and records required by subrule (7) of this rule.  
(c) The manufacturer’s specifications for volatile organic compound content for  
adhesives may be used if the specifications are based on results of tests of the volatile  
organic compound content conducted in accordance with methods specified in  
subdivisions (a) or (b) of this subrule, as applicable.  
(d) For reactive adhesives, an acceptable compliance procedure is described in  
“Determination of Weight Volatile Matter Content and Weight Solids Content of  
Reactive Adhesives,40 CFR, part 63, subpart PPPP, appendix A, adopted by  
reference in R 336.1902.  
(7) A person that is responsible for the operation of a miscellaneous industrial  
adhesive application operation that is subject to this rule shall obtain current  
information and keep records necessary for the determination of compliance with  
this rule, as required in R 336.2041.  
R 336.1637 Emissions of volatile organic compounds from existing fiberglass boat  
manufacturing in 2015 ozone nonattainment areas.  
Rule 637. (1) As used in this rule, fiberglass boat manufacturing” means the  
manufacturing of hulls or decks of boats from fiberglass or build molds to make  
fiberglass boat hulls or decks.  
89  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from an existing fiberglass boat manufacturing facility located in the 2015 ozone  
nonattainment areas unless all of the provisions of the following subrules are met.  
(3) The provisions of this rule do not apply to the following:  
(a) Except as provided in subrule (6) of this rule, any fiberglass boat  
manufacturing operations that have an actual emission rate of volatile organic  
compounds less than 2.7 tons per 12-month rolling period, before consideration of  
control equipment. If the combined actual emission rate equals or is more than 2.7  
tons per year on a 12-month rolling basis before consideration of controls, as  
determined in a subsequent month, then this rule permanently applies to the  
fiberglass boat manufacturing operations at that facility.  
(b) Miscellaneous industrial adhesives used in the assembly of fiberglass boats.  
Polyester resin putties used to assemble fiberglass parts are not considered  
industrial adhesives for the purposes of this exclusion and apply to this part.  
(c) Surface coatings applied to fiberglass boats.  
(d) Surface coating for fiberglass and metal recreational boats, for example,  
pleasure craft, addressed under R 336.1633.  
(e) Facilities that manufacture solely parts of boats or boat trailers, but do not  
manufacture hulls or decks of boats from fiberglass or build molds to make  
fiberglass boat hulls or decks.  
(f) Closed molding operations.  
(g) Except as provided in subrule (6) of this rule, all of the following:  
(i) Production resins that must meet specifications for use in military vessels or  
must be approved by the United States Coast Guard for use in the construction of  
lifeboats, rescue boats, and other life-saving appliances approved under 46 CFR  
subchapter Q, or the construction of small passenger vessels regulated by 46 CFR  
subchapter T.  
(ii) Production and tooling resins, and pigmented, clear, and tooling gel coat used  
for part or mold repair and touch up. The total resin and gel coat materials that  
meet these criteria must not exceed 1% by weight of all resin and gel coat used at a  
facility on a 12-month rolling average basis.  
(iii) Pure, 100% vinylester resin used for skin coats.  
(4) A person shall not cause or allow the emission of any volatile organic compound  
from fiberglass boat manufacturing operations, unless the following provisions are  
met:  
(a) A person with a source subject to the requirements of this rule shall comply  
with the limitations in subdivisions (b), (c), or (d) of this subrule. For sources  
complying pursuant to subdivision (b) or (c) of this subrule, if the non-monomer  
volatile organic compound content of a resin or gel coat exceeds 5%, by weight, the  
excess non-monomer volatile organic compound must be added to the monomer  
volatile organic compound of the resin or gel coat. The excess non-monomer volatile  
organic compound must be calculated in accordance with the following equation:  
Excess Non-Monomer VOC = Non-monomer VOC Content 5%, by weight  
90  
(b) A person shall not cause or allow the emission of volatile organic compounds  
from resin or gel coat from any existing source applicable to this rule in any of the  
2015 ozone nonattainment areas as defined in R 336.1601, in excess of the applicable  
monomer requirements in table 69-a of this subrule.  
TABLE 69-a  
Alternative volatile organic compound content requirements for molding resin  
and gel coat operations.  
Operation  
Application Method  
Weighted-Average  
Monomer VOC Content  
(weight percent)  
Production resin  
Production resin  
Pigment gel coat  
Clear gel coat  
Tooling resin  
Atomized  
28.0  
35.0  
33.0  
48.0  
30.0  
39.0  
40.0  
Nonatomized  
Any method  
Any method  
Atomized  
Nonatomized  
Any method  
Tooling resin  
Tooling gel coat  
(c) A person subject to the requirements of this rule may elect to include some or  
all of the subject resin and gel coat operations at the source in the emissions  
averaging alternative. All subject resin and gel coat operations that do not utilize the  
emissions averaging alternative must comply with the requirements in subdivision  
(b) or (d) of this subrule, as well as with all other applicable requirements in this  
rule. Resin and gel coat operations utilizing the emissions averaging alternative  
must comply with a source-specific monomer volatile organic compound mass  
emission limit on a 12-month rolling average basis, calculated at the end of each  
calendar month. using the following equations:  
(i) A person subject to subdivision (c) of this subrule shall use equation 6-1 to  
determine the source-specific monomer volatile organic compound mass emission  
limit for resin and gel coats included in the emissions average:  
Equation 6-1:  
Monomer VOC Limit = 46(MR)+159(MPG)+291(MCG)+54(MTR)+214(MTG  
)
Where:  
Monomer = Total allowable monomer volatile organic compound that can VOC  
be emitted from the open molding operations included in the limit average,  
expressed in kilograms per 12-month period.  
MR = Mass of production resin used in the past 12 months, excluding any  
materials that are exempt, expressed in megagrams (Mg).  
MPG = Mass of pigmented gel coat used in the past 12 months, excluding any  
materials that are exempt, expressed in Mg.  
91  
MCG = Mass of clear gel coat used in the past 12 months, excluding any materials  
that are exempt, expressed in Mg.  
MTR = Mass of tooling resin used in the past 12 months, excluding any materials  
that are exempt, expressed in Mg.  
MTG = Mass of tooling gel coat used in the past 12 months, excluding any materials  
that are exempt, expressed in Mg.  
The numerical coefficients associated with each term on the righthand side of  
equation 6-1 are the allowable monomer volatile organic compound emission rates  
for that particular material in units of kg VOC/Mg of material used.  
(ii) At the end of the first 12-month averaging period, and at the end of each  
subsequent month, the person with a source subject to this subdivision (c) shall use  
equation 6-2 to calculate the monomer volatile organic compound emissions from  
the resin and gel coat operations included in the emissions average. The monomer  
volatile organic compound emissions calculated using equation 6-2 must not exceed  
the monomer volatile organic compound limit calculated using equation 6-1.  
EQUATION 6-2:  
Monomer VOC Emissions = ( PVR)(MR ) + (PVPG)(MPG) + (PVCG)(MCG) +  
(PVTR)(MTR) + (PVTG)(MTG  
)
Where:  
Monomer VOC Emissions= Monomer volatile organic compound emissions  
calculated using the monomer volatile organic compound emission equations for  
each operation included in the average, expressed in kilograms.  
PVR = Weighted-average monomer volatile organic compound emission rate for  
production resin used in the past 12 months, expressed in kg/Mg, calculated in  
accordance with equation 6-3 in subdivision (c)(iii) of this subrule.  
MR = Mass of production resin used in the past 12 months, expressed in Mg.  
PVPG = Weighted-average monomer volatile organic compound emission rate for  
pigmented gel coat used in the past 12 months, expressed in kg/Mg, calculated  
pursuant to equation 6-3.  
MPG = Mass of pigmented gel coat used in the past 12 months, expressed in Mg.  
PVCG = Weighted-average monomer volatile organic compound emission rate for  
clear gel coat used in the past 12 months, expressed in kg/Mg, calculated pursuant to  
equation 6-3.  
MCG = Mass of clear gel coat used in the past 12 months, expressed in Mg.  
PVTR = Weighted-average monomer volatile organic compound emission rate for  
tooling resin used in the past 12 months, expressed in kg/Mg, calculated pursuant to  
equation 6-3.  
MTR = Mass of tooling resin used in the past 12 months, expressed in Mg.  
92  
PVTG = Weighted-average monomer volatile organic compound emission rate for  
tooling gel coat used in the past 12 months, expressed in kg/Mg, calculated pursuant  
to equation 6-3.  
MTG = Mass of tooling gel coat used in the past 12 months, expressed in Mg.  
(iii) For purposes of equation 6-2, the person with a source subject to this subdivision (c)  
shall use equation 6-3 to calculate the weighted-average monomer volatile organic  
compound emission rate for the previous 12 months for each resin and gel coat  
operation included in the emissions average, except as provided in subdivision (f) of  
this subrule.  
EQUATION 6-3:  
풊=ퟏ  
푴 푷푽  
PVOP  
=
풊=ퟏ  
Where:  
PVOP = Weighted-average monomer volatile organic compound emission rate for  
each open molding operation (PVR, PVPG, PVCG, PVTR, and PVTG) included in  
the average, expressed in kg of monomer volatile organic compound per Mg of  
material applied.  
Mi = Mass of resin or gel coat (i) used within an operation in the past 12 months,  
expressed in Mg.  
n = Number of different open molding resins and gel coats used within an  
operation in the past 12 months.  
PVi = The monomer volatile organic compound emission rate for resin or gel coat  
(i) used within an operation in the past 12 months, expressed in kg of monomer  
volatile organic compound per Mg of material applied. The monomer volatile  
organic compound emission rate formulas in subdivision (c)(iv) of this rule must be  
used to compute PVi. If a source includes filled resins in the emissions average, the  
source must use the value of PVF, calculated using equation 6-4 in subdivision  
(f)(iii) of this rule, as the value of Pvi for those resins.  
i = Subscript denoting a specific open molding resin or gel coat applied.  
(iv) For purposes of equation 6-3 and subdivision (f)(iii) of this subrule, the  
following monomer volatile organic compound emission rate formulas applies. The  
formulas calculate monomer volatile organic compound emission rates in terms of  
kg of monomer volatile organic compound per Mg of resin or gel coat applied.  
"VOC%" means the monomer volatile organic compound content as supplied,  
expressed as a weight percent value between 0 and 100%.  
TABLE 69-b  
Monomer volatile organic compound emission rate formulas for molding  
operations.  
93  
Operation  
Application Method  
Formula to calculate the monomer  
VOC emission rate.  
Production resin, tooling resin  
Production resin, tooling resin  
Atomized  
0.014 x (Resin VOC%)2.425  
0.01185 x (Resin VOC%)2.425  
Atomized, plus vacuum  
bagging with roll-out  
Atomized, plus vacuum  
bagging without roll-out  
Nonatomized  
Nonatomized, plus vacuum 0.0110 x (Resin VOC%)2.275  
bagging with roll-out  
Nonatomized, plus vacuum 0.0076 x (Resin VOC%)2.275  
bagging without roll-out  
Production resin, tooling resin  
0.00945 x (Resin VOC%)2.425  
0.014 x (Resin VOC%)2.275  
Production resin, tooling resin  
Production resin, tooling resin  
Production resin, tooling resin  
Pigmented gel coat, clear gel  
coat, tooling gel coat  
All methods  
0.445 x (Gel coat VOC%)1.675  
(d) A person subject to the requirements of this rule may elect to employ an add-  
on control device with a minimum overall control efficiency that meets the monomer  
volatile organic compound emission limitations specified in table 69-a of this rule.  
All subject resin and gel coat operations that do not utilize the add-on control  
alternative must comply with the requirements in subdivision (b) or (c) of this  
subrule, as well as with all other applicable requirements in this rule.  
(e) A person subject to subdivision (d) of this subrule shall meet the volatile  
organic compound emission limit determined using equation 6-1 in subdivision (c)(i)  
of this subrule. In equation 6-1, however, instead of using the mass of each material  
used over the past 12 months to determine the emission limitation, the person shall  
use the mass of each material used during the applicable control device performance  
test. If the measured emissions at the outlet of the control device are less than the  
emission limit, then the facility is considered to have achieved compliance with the  
emission limit.  
(f) For all filled production and tooling resins, the person subject to this subrule  
shall adjust the monomer volatile organic compound emission rates determined  
pursuant to subdivisions (b) and (c) of this subrule using equation 6-4 in paragraph  
(iii) of this subdivision. If complying pursuant to subdivision (c) of this subrule, the  
value of PVF, calculated using equation 6-4, must be used as the value of PVi in  
equation 6-3, as set forth in subdivision (c)(iii) of this subrule. If the non-monomer  
volatile organic compound content of a filled resin exceeds 5%, by weight, based on  
the unfilled resin, the excess non-monomer VOC must be added to the monomer  
volatile organic compound content in accordance with the equation set forth in  
subdivision (a) of this subrule. If complying pursuant to subdivision (b) of this  
subrule, the emission rate determined by equation 6-4 must not exceed any of the  
following limitations:  
(i) Tooling Resin: 119.1 lbs monomer VOC/Mg filled resin applied.  
(ii) Production Resin: 101.4 lbs monomer VOC/Mg filled resin applied.  
(iii) Equation 6-4.  
94  
PVF = (PVU)(100 - percent filler) / 100  
Where:  
PVF = The as-applied monomer volatile organic compound emission rate for a  
filled production resin or tooling resin, pounds of monomer volatile organic  
compound per ton of filled material.  
PVU = The monomer volatile organic compound emission rate for the neat  
(unfilled) resin, before filler is added, as calculated using the formulas in table 69-b  
of this rule.  
Percent filler = The weight-percent of filler in the as-applied filled resin system.  
(5) A person subject to this rule, shall develop written procedures for compliance  
with the following work practices for each fiberglass boating manufacturing  
operation at the source:  
(a) All resin or gel coat mixing containers with a capacity equal or greater than 55  
gallons, including those used for on-site mixing of putties and polyputties, must have  
a cover with no visible gaps in place at all times. This subdivision does not apply  
when material is being manually added to or removed from a container, or when  
mixing or pumping equipment is being placed in or removed from a container.  
(b) No person subject to this rule shall use volatile organic compound-containing  
cleaning solutions to remove cured resins and gel coats from fiberglass boat  
manufacturing application equipment. Additionally, a person shall not use volatile  
organic compound-containing solutions for routine cleaning of application  
equipment unless 1 of the following applies:  
(i) The volatile organic compound content of the cleaning solution is less than or  
equal to 5%, by weight.  
(ii) The composite vapor pressure of the cleaning solution is less than or equal to  
0.50 mmHg at 68 degrees Fahrenheit.  
(6) A person that is responsible for the operation of a fiberglass boat  
manufacturing facility that is subject to this rule shall obtain current information,  
and keep records necessary, for a determination of compliance with this rule,  
including, but not limited to, all of the following:  
(a) The total amounts, in pounds, of atomized molding production operations  
listed in table 69-a and table 69-b used per month and the weighted-average volatile  
organic compound contents for each operation, expressed as weight percent.  
(b) All calculations performed pursuant to this rule.  
(c) The volatile organic compound content of each non-monomer resin and gel  
coat employed.  
(d) For each cleaning material employed for routine application equipment  
cleaning, either the volatile organic compound content, by weight percent or the  
composite vapor pressure, in mmHg, whichever is the applicable requirement  
selected to comply with the cleaning solvent requirements of subrule (5)(b) of this  
rule.  
R 336.1638 Emissions of volatile organic compounds from existing wood furniture  
manufacturing in 2015 ozone nonattainment areas.  
95  
Rule 638. (1) As used in this rule:  
(a) "Wood furniture" means any product made of wood, a wood product such as  
rattan or wicker, or an engineered wood product, such as particleboard.  
(b) "Wood furniture component" means any part that is used in the manufacture  
of wood furniture, including, but not limited to, drawer sides, cabinet doors, seat  
cushions, and laminated tops. Wood furniture component does not include foam  
seat cushions manufactured and fabricated at a facility that does not engage in other  
wood furniture or wood furniture component manufacturing operations.  
(c) "Wood furniture manufacturing operations" means the finishing, gluing,  
cleaning, and washoff operations associated with the production of wood furniture  
or wood furniture components.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from an existing wood furniture manufacturing facility located in the 2015 ozone  
nonattainment areas unless all of the provisions of the following subrules are met.  
(3) Except as provided in subrule (6) of this rule, the provisions of this rule do not  
apply to any wood furniture manufacturing operations that have a potential to emit  
for volatile organic compounds from all wood furniture finishing operations at the  
facility, including any related cleaning activities, of less than 25 tons per year. If the  
potential to emit equals or is more than 25 tons per year on a 12-month rolling basis  
before consideration of controls, as determined in a subsequent month, then this  
rule permanently applies to the wood furniture finishing operations at that facility.  
(4) A person shall not cause or allow the emission of any volatile organic compound  
from wood furniture manufacturing operations, unless the following provisions are  
met:  
(a) A person with a source subject to the requirements of this rule shall comply  
with the limitations in subdivision (b), (c), (d), or (e) of this subrule.  
(b) A person shall not cause or allow the emission of volatile organic compounds  
from any existing source applicable to this rule in any of the 2015 ozone  
nonattainment areas, in excess of the applicable requirements in table 69-c of this  
subrule.  
TABLE 69-c  
Volatile organic compound emission limitations for existing wood furniture  
manufacturing coating operations.  
Coating Category  
lb of VOC per lb of solids, as  
applied  
Topcoat only  
0.8  
Topcoat (in combination with sealer)  
Sealer (in combination with topcoat)  
Acid-cured alkyd amino vinyl sealer  
Acid-cured alkyd amino conversion  
varnish topcoat  
1.8  
1.9  
2.3  
2.0  
Strippable spray booth coatings  
0.8  
96  
(c) Using finishing materials where actual emissions are less than or equal to  
allowable emissions using 1 of the following averaging equations:  
Equation 6-5:  
0.9 i=1→N(0.8)(TCi)) ≥ Σi=1→N ERTCi (TCi)  
Equation 6-6:  
0.9 (Σi=1→N(1.8)(TCi) + (1.9)(SEi) + (9.0)(WCi) + (1.2)(Bci) + (0.791) (STi)) ≥  
Σi=1→N ERTCi(TCi) + ERSEi(SEi) + ERWCi(WCi) +  
ERBCi(BCi) + ERSTi(STi)  
Where:  
N = number of finishing materials participating in averaging.  
TCi = kilograms of solids of topcoat “i” used.  
SEi = kilograms of solids of sealer “i” used.  
WCi = kilograms of solids of washcoat “i” used.  
BCi = kilograms of solids of basecoat “i” used.  
STi = liters of stain “i” used.  
ERTCi = VOC content of topcoat “i” in kg VOC/kg solids, as-applied.  
ERSEi = VOC content of sealer “i” in kg VOC/kg solids, as-applied.  
ERWCi = VOC content of washcoat “i” in kg VOC/kg solids, as-applied.  
ERBCi = VOC content of basecoat “i” in kg VOC/kg solids, as-applied.  
ERSTi = VOC content of stain “i” in kg VOC/liter (kg/l), as-applied.  
(d) Using a control system that achieves an equivalent reduction in emissions as the  
requirements of table 69-c, according to the following provisions:  
(i) Determine the overall control efficiency needed to demonstrate compliance using  
the following equation:  
O = ((V - E)/V)(100)  
Where:  
O = overall control efficiency of the capture system and control device as  
percentage.  
V = actual volatile organic compound content of the finishing system material as-  
applied to the substrate in pounds of volatile organic compound per pound of solids  
(lbs VOC/lb solids), or, if multiple finishing materials are used, the daily weighted  
average.  
E = equivalent volatile organic compound emission limits in lbs VOC/lb solids.  
(ii) Document that the value of Vin the equation under paragraph (i) of this  
subdivision is obtained from the volatile organic compounds and solids content of the as-  
applied finishing material.  
(iii) Calculate the overall efficiency of the capture system and control device,  
using the procedures in R 336.2040.  
97  
(e) Using a combination of the methods presented in subdivisions (b), (c), and (d)  
of this subrule.  
(5) A person subject to this rule, shall develop written procedures for compliance  
with the following work practices for each wood furniture manufacturing operation  
at the source:  
(a) Use cleaning materials containing no more than 8.0% by weight volatile  
organic compound for cleaning spray booth components other than conveyors,  
continuous coaters and their enclosures, or metal or plastic filters.  
(b) Store volatile organic compound-containing cleaning materials in closed  
containers.  
(c) Collect all volatile organic compound-containing cleaning material used to  
clean spray guns and spray gun lines in a container and keep the container covered  
except when adding or removing material.  
(d) Control emissions of volatile organic compound-containing cleaning material  
from washoff operations by doing both of the following:  
(i) Equipping the tank used for washoff operations with a cover and keeping the  
cover closed when the tank is not being used.  
(ii) Minimizing dripping by tilting or rotating the part to drain as much cleaning  
material as possible into the tank.  
(e) Use strippable spray booth materials containing no more than 0.8 pound of  
volatile organic compound per pound of solids, as applied.  
(f) Use of conventional air spray to apply finishing materials only under any of the  
following conditions:  
(i) When applying finishing materials that have an as applied volatile organic  
compound content no greater than 1.0 pound per pound of solids.  
(ii) When applying final touch-up and repair finishing materials.  
(iii) When using a control device to meet the applicable requirements of this rule.  
(6) For the purpose of this rule, recordkeeping for all requirements and  
applicability demonstrations must be maintained in sufficient detail to demonstrate  
compliance with all applicable standards of the rule. Records must include, but are  
not limited, to the following:  
(a) All calculations performed pursuant to this rule.  
(b) Monthly volatile organic compound emissions and materials usage as needed  
to meet thresholds described in subrule (3) of this rule.  
(c) For each cleaning material employed for routine application equipment  
cleaning, either the volatile organic compound content, by weight percent or the  
composite vapor pressure, in mmHg, whichever is the applicable requirement  
selected to comply with the cleaning solvent requirements of subrule (5)(a) of this  
rule.  
R 336.1639 Emission of volatile organic compounds from existing aerospace  
manufacturing and rework operations in 2015 ozone nonattainment areas.  
Rule 639. (1) As used in this rule:  
(a) “Aerospace vehicle or component” means any fabricated part, processed part,  
assembly of parts, or completed unit, with the exception of electronic components, of  
any aircraft including but not limited to airplanes, helicopters, missiles, rockets, and  
98  
space vehicles.  
(b) “Aqueous cleaning solvents” means a solvent in which water is not less than  
80% of the solvent as applied.  
(2) A person shall not cause or allow the emission of any volatile organic  
compounds from any existing aerospace manufacturing or reworking sources  
located within the 2015 ozone nonattainment areas, in excess of the applicable  
emission rates provided in subrule (4) of this rule.  
(3) With the exception of subrule (6) of this rule, any of the following aerospace  
manufacturing or reworking operations at a stationary source where aerospace  
components and vehicles are cleaned or coated is exempt from the limits established  
in this rule:  
(a) Facilities with total potential to emit volatile organic compound of less than 25  
tons per year for all operations combined.  
(b) Facilities that use separate formulations in volumes of less than 50 gallons per  
year up to a maximum of 200 gallons total for formulations applied annually.  
(c) Research and development operations.  
(d) Quality control operations.  
(e) Laboratory testing facilities.  
(f) Electronic parts and assembly processes, except for cleaning and coating of  
completed assemblies.  
(g) Rework operations performed on space vehicles or antique aerospace vehicles  
and components.  
(h) Touchup, aerosol, and United States Department of Defense classified coating  
applications.  
(4) A person shall not cause or allow the emission of volatile organic compounds  
from aerospace manufacture and rework operations, unless the following provisions  
are met:  
(a) Except as allowed by subdivision (b) of this subrule, a person that applies  
specialty coatings to aerospace vehicles or components, including any volatile  
organic compound-containing materials added to the original coating supplied by  
the manufacturer, shall comply with the following volatile organic compound  
emission limitations, minus water and exempt compounds, as applied using1 or  
more of the coating types listed within table 69-d.  
TABLE 69-d  
Volatile organic compound content limits for aerospace manufacturing and rework  
(lbs of VOC/gallon coating)  
Coating Type  
Limit  
Coating Type  
Limit  
Ablative coating  
Adhesion promoter  
Adhesive bonding primers:  
Cured at 250 degrees Fahrenheit or  
below  
5.0  
7.4  
Flight-test coatings:  
Missile or single use aircraft  
All other  
3.5  
7.0  
7.1  
Fuel-tank coating  
6.0  
7.1  
Cured above 250 degrees Fahrenheit  
8.6  
High-temperature coating  
99  
Adhesives:  
Insulation covering  
Intermediate release coating  
Lacquer  
Maskants:  
Bonding maskant  
Critical use and line sealer maskant  
Seal coat maskant  
Metallized epoxy coating  
Mold release  
Optical anti-reflective coating  
Part marking coating  
Pretreatment coating  
Primer  
6.2  
6.3  
6.9  
Commercial interior adhesive  
Cyanoacrylate adhesive  
Fuel tank adhesive  
Nonstructural adhesive  
Rocket motor bonding adhesive  
Rubber-based adhesive  
Structural autoclavable adhesive  
Structural nonautoclavable adhesive  
Antichafe coating  
6.3  
8.5  
5.2  
3
7.4  
7.1  
0.5  
7.1  
5.5  
5.2  
7.1  
4.6  
10.3  
8.5  
10.3  
6.2  
6.5  
6.3  
7.1  
6.5  
2.9  
Bearing coating  
Caulking and smoothing compounds  
Chemical agent-resistant coating  
Primer for general aviation rework  
facility  
Chemical milling maskant, type I  
5.2  
4.5  
Chemical milling maskant, type II  
Clear coating  
Commercial exterior aerodynamic  
1.3  
6.0  
Rain erosion-resistant coating  
Rocket motor nozzle coating  
Scale inhibitor  
7.1  
5.5  
7.3  
7.0  
5.4  
structure primer  
Screen print ink  
Compatible substrate primer  
Corrosion prevention compound  
Cryogenic flexible primer  
Dry lubricative material  
Cryoprotective coating  
Electric or radiation-effect coating  
Electrostatic discharge and  
electromagnetic  
6.5  
5.9  
5.4  
7.3  
5.0  
6.7  
Sealants:  
Extrudable/rollable/brushable sealant  
Sprayable sealant  
Silicone insulation material  
Solid film lubricant  
Specialized function coating  
Temporary protective coating  
Thermal control coating  
Topcoat (incl self priming)  
Topcoat for general aviation rework  
facility (incl self priming)  
Wet fastener installation coating  
2.3  
5.0  
7.1  
7.3  
7.4  
2.7  
6.7  
3.5  
6.7  
Elevated-temperature skydrol-resistant  
commercial primer  
6.2  
4.5  
5.6  
7.1  
Epoxy polyamide topcoat  
5.5  
5.4  
Exterior primer for large commercial  
aircraft (components or assembled)  
Fire-resistant (interior) coating  
Flexible primer  
Wing coating  
6.7  
5.3  
(b) The content limits described in table 69-d can be met by using approved air  
pollution control equipment if the control system has combined volatile organic  
compound emissions capture and control equipment efficiency of not less than  
81% by weight.  
(c) A person shall use 1 or more of the following application techniques in  
applying any primer or topcoat to aerospace vehicles or components, except as  
allowed by subdivision (d) of this subrule:  
(i) Flow/curtain coat.  
(ii) Dip coat.  
(iii) Roll coating.  
100  
(iv) Brush coating.  
(v) Cotton-tipped swab applications.  
(vi) Electrodeposition coating.  
(vii) High volume low pressure (HVLP) spraying.  
(viii) Electrostatic spray.  
(ix) Other coating application methods equivalent to HVLP or electrostatic  
spray applications that are equivalent to HVLP.  
(d) A person is not required to meet application techniques listed in subdivision  
(c) of this subrule in the following situations:  
(i) Airbrush or extension on the spray gun to properly reach limited access  
spaces.  
(ii) Application of specialty coatings.  
(iii) Application of coating that contain fillers that adversely affect atomization  
with HVLP spray guns and cannot be applied by other means required in  
subdivision (c) of this subrule.  
(iv) Application of coatings that normally have a dried film thickness of less  
than 0.0013 centimeters and cannot be applied by other means required in  
subdivision (c) of this subrule.  
(v) Airbrush methods for stenciling, lettering, and other identification  
markings.  
(vi) Hand-held spray can application methods.  
(vii) Touch-up and repair operations.  
(e) Cleaning using hand wiping must use an aqueous cleaning solvent or have a  
volatile organic compound composite vapor pressure less than or equal to 45  
millimeters of mercury at 20 degrees Celsius except in the following situations:  
(i) Cleaning during the manufacture, assembly, installation, maintenance, or  
testing of components of breathing oxygen systems that are exposed to breathing  
oxygen.  
(ii) Cleaning during the manufacture. assembly, installation, maintenance, or  
testing of parts, subassemblies, or assemblies that are exposed to strong oxidizers  
or reducers.  
(iii) Cleaning and surface activation before adhesive bonding.  
(iv) Cleaning of electronics parts and assemblies containing electronics parts.  
(v) Cleaning of aircraft and ground support equipment fluid systems that are  
exposed to the fluid, including air-to-air exchangers and hydraulic fluid systems.  
(vi) Cleaning of fuel cells, fuel tanks, and confined spaces.  
(vii) Surface cleaning of solar cells, coated optics, and thermal control surfaces.  
(viii) Cleaning during fabrication, assembly, installation, and maintenance of  
upholstery, curtains, carpet, and other textile materials used on the interior of  
aircraft.  
(ix) Cleaning of metallic and nonmetallic materials used in honeycomb cores  
during the manufacture or maintenance of these cores, and cleaning of the  
completed cores used in the manufacture of aerospace vehicles or components.  
(x) Cleaning of aircraft transparencies, polycarbonate, or glass substrates.  
(xi) Cleaning and solvent usage associated with research and development,  
quality control, or laboratory testing.  
101  
(xii) Cleaning operations, using nonflammable liquids, conducted within 5 feet of  
energized electrical systems.  
(xiii) Cleaning operations identified as essential under the Montreal Protocol for  
which the administrator has allocated essential use allowances or exemptions in 40  
CFR section 82.4.  
(f) For cleaning solvents used in the flush cleaning of parts, assemblies, and  
coating unit components, the used cleaning solvent, except for semiaqueous  
cleaning solvents, must be emptied into an enclosed container or collection system  
that is kept closed when not in use or captured with wipers, provided they comply  
with the housekeeping requirements of subdivision (g) of this subrule. Aqueous  
cleaning solvents are exempt from these requirements.  
(g) All spray guns must be cleaned by 1 or more of the following methods:  
(i) Enclosed spray gun cleaning system if it is kept closed when not in use and  
leaks are repaired within 14 days after the leak is first discovered, or the enclosed  
cleaner must be shut down until the leak is repaired.  
(ii) Unatomized discharge of solvent into a waste container that is kept closed  
when not in use.  
(iii) Disassembly of the spray gun and cleaning in a vat that is kept closed when  
not in use.  
(iv) Atomized spray into a waste container that is fitted with a device designed to  
capture atomized solvent emissions.  
(h) All fresh and used cleaning solvents, except aqueous and semiaqueous  
cleaning solvents, used in solvent cleaning operations must be stored in containers  
that are kept closed at all times except when filling or emptying. This includes  
cloth and paper, or other absorbent applicators, moistened with cleaning solvents  
except for cotton-tipped swabs used for very small cleaning operations.  
(i) A person shall implement handling and transfer procedures to minimize spills  
during filling and transferring the cleaning solvent to or from enclosed systems,  
vats, waste containers, and other cleaning operation equipment that hold or store  
fresh or used cleaning solvents. Aqueous cleaning solvents are exempt from these  
requirements.  
(5) Compliance with this rule must be determined as follows:  
(a) Each person operating a control device for compliance with this rule shall  
submit a monitoring plan that specifies the applicable operating parameter value, or  
range of values, to ensure ongoing compliance with subrule (4)(b) of this rule. The  
monitoring device must be installed, calibrated, operated, and maintained in  
accordance with the manufacturer’s specifications, or an equivalent plan  
approvable by the department.  
(b) Each person using an enclosed spray gun cleaner shall visually inspect the seals  
and all other potential sources of leaks at least once per month in any calendar year  
in which it is used. Each inspection must occur while the spray gun cleaner is in  
operation.  
(c) For coatings and cleaning solvents that are not waterborne or water-reducible,  
the volatile organic compound content of each formulation must be determined,  
less water and less exempt solvents, as applied using manufacturer's supplied data  
or method 24 of 40 CFR part 60, appendix A. If there is a discrepancy between the  
102  
manufacturer's formulation data and the results of the method 24 analysis,  
compliance must be based on the results from the method 24 analysis. For water-  
borne, or water-reducible, coatings, and aqueous and semiaqueous cleaning  
solvents, manufacturer's supplied data alone can be used to determine the volatile  
organic compound content of each formulation.  
(d) For hand-wipe cleaning solvents required in subrule (4)(e) of this rule,  
manufacturers' supplied data or standard engineering reference texts or other  
equivalent methods must be used to determine the vapor pressure or volatile  
organic compound composite vapor pressure for blended cleaning solvents.  
(6) A person subject to this rule shall obtain current information and maintain  
records for all requirements in sufficient detail to determine compliance, and must  
be made available to the department upon request. These records must include the  
following, as applicable:  
(a) A list of coatings and usages as described in table 69-d must be maintained  
with category and volatile organic compound content as applied on a monthly basis.  
(b) Each owner or operator using cleaning solvents as described in this rule shall  
maintain on a monthly basis a list of the following:  
(i) For aqueous and semi aqueous hand-wipe cleaning solvents, materials used  
with corresponding water contents.  
(ii) For vapor pressure compliant hand-wipe cleaning solvents, cleaning solvents  
with their respective vapor pressures or, for blended solvents, volatile organic  
compound composite vapor pressures.  
(iii) For cleaning solvents with a vapor pressure greater than 45 mm Hg, a list of  
exempt hand-wipe cleaning processes.  
(c) Each owner or operator using control equipment under subrule (4)(b) of this  
rule shall record monitoring parameters as specified in the monitoring plan  
required under subrule (5)(a) of this rule.  
(d) Except for specialty coatings, any source that complies with the recordkeeping  
requirements of the Aerospace NESHAP, 40 CFR 63.752, complies with the  
requirements of this subrule.  
R 336.1640 Emission of volatile organic compounds from existing storage vessels in  
the oil and natural gas industry located in the 2015 ozone nonattainment areas.  
Rule 640. (1) As used in this rule, "storage vesselmeans a tank or other vessel  
that contains an accumulation of oil and gas related liquids, and that is constructed  
primarily of non-earthen materials, such as wood, concrete, steel, fiberglass, or  
plastic that provide structural support.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
in excess of the limitations of this rule from the use of existing storage vessels  
utilized in the oil and natural gas production, natural gas processing, and natural  
gas transmission and storage segments of the oil and natural gas industry that meet  
both of the following criteria:  
(a) A storage vessel located in the 2015 ozone nonattainment area.  
(b) A storage vessel used for the storage of crude oil or condensates, intermediate  
hydrocarbon liquids, or produced water.  
103  
(3) Except as provided in subrule (6) of this rule, the provisions of this rule do not  
apply to the following:  
(a) Storage vessels with a potential to emit volatile organic compounds of less than  
6 tons per year. This potential to emit can be limited by a federally enforceable  
permit or order.  
(b) Storage vessels with uncontrolled actual volatile organic compound emissions  
of less than 4 tons per 12-month rolling average. If the combined actual emission  
rate equals or is more than 4 tons per year on a 12-month rolling basis before  
consideration of controls, as determined in a subsequent month, then this rule  
permanently applies to the storage vessel.  
(c) Vessels that are skid-mounted or permanently attached to a mobile source,  
such as trucks, railcars, barges, or ships, and are intended to be located at a site for  
less than 180 consecutive days.  
(d) Process vessels, such as surge control vessels, bottoms receivers, or knockout  
vessels.  
(e) Pressure vessels designed to operate in excess of 204.9 kilopascals (29.7 pounds  
per square inch) and that are not expected to have emissions to the atmosphere  
during normal operation.  
(f) A storage vessel with a capacity greater than 100,000 gallons used to recycle  
water that has been passed through 2 stage separation.  
(g) VOC emission control requirements do not apply to storage vessels subject and  
controlled in accordance with the requirements for storage vessels in “Standards of  
Performance for Volatile Organic Liquid Storage Vessels (Including Petroleum  
Liquid Storage Vessels) for Which Construction, Reconstruction, or Modification  
Commenced After July 23, 1984” 40 CFR part 60, “National Emission Standards  
for Organic Hazardous Air Pollutants From the Synthetic Organic Chemical  
Manufacturing Industry for Process Vents, Storage Vessels, Transfer Operations,  
and Wastewater” 40 CFR part 63, subpart G, “National Emission Standards for  
Hazardous Air Pollutants From Petroleum Refineries” 40 CFR part 63, subpart  
CC, “National Emission Standards for Hazardous Air Pollutants From Oil and  
Natural Gas Production Facilities” 40 CFR part 63, subpart HH, or “National  
Emission Standards for Storage Vessels (Tanks) Control Level 2” 40 CFR part 63,  
subpart WW. All regulations stated within this subdivision are adopted by  
reference in R 336.1902.  
(4) A person subject to the requirements of this rule shall not cause or allow the  
emission of any volatile organic compound from storage vessels, unless emissions  
are reduced by 95% by weight or greater as determined by subrule (5) of this rule  
and the following provisions are met, as applicable:  
(a) If utilized, an enclosed combustion control device for the volatile organic  
compound emissions from material storage must meet 1 of the following:  
(i) Emissions must be less than 275 ppm by volume as propane on a wet basis  
corrected to 3% oxygen.  
(ii) The control must be operated at a minimum temperature of 760 degrees  
Celsius, provided a valid performance test as required in subrule (5) of this rule is  
104  
on file that demonstrated the combustion zone temperature is an indicator of  
sufficient destruction efficiency.  
(iii) The vent stream must be introduced into the flame zone of the boiler or  
process heater.  
(b) A person using a control device to reduce emissions shall meet the following  
requirements:  
(i) Covers must satisfy all of the following:  
(A) The covers and all openings on the cover must form a continuous  
impermeable barrier over the entire surface area of the liquid in the vessel.  
(B) Each cover opening must be secured in a closed sealed position when material  
is in the unit except during time necessary to use the opening, such as adding,  
removing, sampling, or inspecting material in the unit, maintaining equipment, or  
venting through a closed vent system.  
(C) Each storage vessel thief hatch must be maintained and operated with a  
mechanism to ensure that the lid remains properly seated and sealed under normal  
operating conditions.  
(ii) Closed vent systems must satisfy all of the following, unless routed to a  
process:  
(A) The closed vent system must route all gases, vapors, and fumes to the control  
device.  
(B) The closed vent system must have no detectable emissions when using, at a  
minimum, olfactory, visual, and auditory inspections.  
(C) Any bypass must have a properly operated and maintained flow indictor at  
the inlet with an alarm that is recorded when activated. Low leg drains, high point  
bleeds, analyzer vents, and open-ended valves or lines and safety devices are not  
considered bypasses.  
(D) The closed vent system must be properly designed and operated, as described  
in subrule (5) of this rule.  
(iii) Control devices must satisfy all of the following, if applicable:  
(A) The control device must be operated and maintained properly as described in  
subrule (5) of this rule.  
(B) When using a combustion control device, it must have a continuous burning  
pilot flame or alternative approved by the department.  
(C) When using a flare as a control device, it must be designed and operated in  
accordance with the requirements of 40 CFR 60.18(b), adopted by reference in  
R 336.1902.  
(D) When using carbon absorption as a control device, the carbon must be  
regenerated or reactivated.  
(c) If a floating roof is used to reduce emissions, the storage vessel must meet all  
relevant requirements of “Standards of Performance for Storage Vessels for  
Petroleum Liquids for Which Construction, Reconstruction, or Modification  
Commenced After May 18, 1978, and Prior to July 23, 1984,” 40 CFR 60.112b(a)(1)  
or (2), and all relevant monitoring, inspection, recordkeeping, and reporting  
requirements in “Standards of Performance for Volatile Organic Liquid Storage  
Vessels (Including Petroleum Liquid Storage Vessels) for Which Construction,  
105  
Reconstruction, or Modification Commenced After July 23, 1984.” 40 CFR part 60,  
subpart Kb,. Both are adopted by reference in R336.1902.  
(5) Compliance with this rule must be determined as follows:  
(a) Initial performance and compliance testing must be conducted in accordance  
with a stack testing protocol approved by the department.  
(b) All control devices must have an approvable operation and maintenance plan  
that contains, at a minimum, the following:  
(i) A schedule of maintenance for the control devices in use.  
(ii) An inspection schedule at least once every calendar month.  
(iii) Written instructions from the manufacturer.  
(c) An analysis must be performed, documented, and maintained that the closed  
vent system is of sufficient design and capacity to ensure all emissions from the  
storage vessel is routed to the control device or process and that the control device is  
of sufficient design and capacity to accommodate all emissions from the storage  
vessel.  
(d) The person subject to this rule for a closed vent system shall conduct and  
maintain records of annual visual inspections for defects that could result in air  
emissions.  
(6) A person operating a storage vessel subject to this rule shall obtain current  
information and maintain records for all applicability and requirements in  
sufficient detail to determine compliance. The records must be made available to the  
department upon request. The records must include the following, as applicable:  
(a) Records of each volatile organic compound emission determination for each  
storage vessel.  
(b) Records of deviations in cases where the storage vessel was not operated in  
compliance with requirements.  
(c) Records of the identification and location of each storage vessel subject to  
emission control requirements.  
R 336.1641 Emission of volatile organic compounds from existing pneumatic  
controllers in the oil and natural gas industry located in the 2015 ozone  
nonattainment areas.  
Rule 641. (1) As used in this rule:  
(a) “Bleed rate” means the rate in standard cubic feet per hour at which natural  
gas is continuously vented, or bleeds, from a pneumatic controller.  
(b) “Pneumatic controller” means an automated instrument used to maintain a  
process condition, such as liquid level, pressure, delta pressure and temperature.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
associated with the oil and natural gas production and natural gas processing  
segments of the oil and natural gas industry, in excess of the limitations of this rule  
from the use of existing single continuous bleed natural gas-driven pneumatic  
controllers, when the controllers are both of the following:  
(a) Located inside the 2015 ozone nonattainment areas.  
(b) Utilized at a natural gas processing plant or with equipment located from  
either the wellhead to the natural gas processing plant or to the point of custody  
transfer to an oil pipeline.  
106  
(3) Except as described in subrule (6) of this rule, the provisions of this rule do not  
apply to a pneumatic controller if there is a functional need for a bleed rate greater  
than the requirements as described in subrule (4) of this rule and it is properly  
tagged. A functional need includes, but is not limited to, response time, safety, and  
positive actuation.  
(4) Except as allowed in subrule (3) of this rule, a person subject to the  
requirements of this rule shall not allow either of the following:  
(a) Any continuous venting for any pneumatic controllers located at a natural gas  
processing plant.  
(b) A bleed rate greater than 6 standard cubic feet per hour from equipment from  
the wellhead to the natural gas processing plant or point of custody transfer to an oil  
pipeline.  
(5) Compliance with this rule must be determined by maintaining records as  
described in subrule (6) of this rule which includes, at a minimum, tagging all  
pneumatic controllers with an identifying number and the installation date, to allow  
traceability to the records for that controller.  
(6) A person operating a pneumatic controller shall obtain current information  
and maintain records for all requirements in sufficient detail to determine  
compliance. The records must be made available to the department upon request.  
This includes records and all other information needed to establish both of the  
following for each pneumatic controller, as applicable:  
(a) The bleed rates.  
(b) A description of its functional need if exempting the equipment from  
requirements in subrule (4) of this rule.  
R 336.1642 Emission of volatile organic compounds from existing pneumatic pumps  
in the oil and natural gas industry located in the 2015 ozone nonattainment areas.  
Rule 642. (1) As used in this rule, "pneumatic pumpmeans a positive  
displacement reciprocating unit driven by natural gas used for injecting precise  
amounts of chemicals into a process stream or for freeze protection glycol  
circulation.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
associated with oil and natural gas production and natural gas processing segments  
of the oil and natural gas industry in excess of the limitations of this rule from the  
use of existing single natural gas driven pneumatic pumps when the pumps are both  
of the following:  
(a) Located inside the 2015 ozone nonattainment area.  
(b) Utilized at a natural gas processing plant or well site.  
(3) Except as required in subrule (6), the provisions of this rule do not apply to a  
pneumatic pump that is either of the following:  
(a) If it is determined through an engineering assessment that routing a pneumatic  
pump to a control device or a process is technically infeasible due to insufficient gas  
pressure or control device capacity, including the event in which there is no control  
device or in which the control device or process is removed from the site, the  
following provisions must be met:  
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(i) An assessment of technical infeasibility must be conducted and must include,  
but is not limited to, safety considerations, distance from the control device,  
pressure losses and differentials in the closed vent system, and the ability of the  
control device to handle the pneumatic pump emissions which are routed to them.  
This assessment must be prepared under supervision of a qualified professional  
engineer.  
(ii) The professional engineer shall sign and certify this prepared assessment.  
(b) In operation less than 90 days per calendar year. For purposes of this rule,  
any period of operation during a calendar day counts toward the 90-day annual  
threshold.  
(4) A person shall not cause or allow the emission of any volatile organic  
compound from pneumatic pumps, unless the following provisions are met:  
(a) At natural gas processing plants, zero emissions or 100% control from each  
diaphragm pump by use of a control device or instrument air system in place of the  
natural gas-driven pump.  
(b) At a well site, emissions from each existing diaphragm pump with control  
devices, must be reduced by 95% by weight or greater as determined by subrule (5)  
of this rule, or, if 95% control is not achievable, by the maximum control efficiency  
possible as described in subrule (6) of this rule.  
(c) At a well site that installs a control device after March 1, 2023, the emissions  
from the pneumatic pump must be captured and routed to the control device.  
(d) If reducing emissions by use of a control device or by routing to a process, the  
pneumatic pump must connect emissions through a closed vent system meeting the  
requirements of R 336.1640(4)(b)(ii).  
(5) Compliance with this rule must be determined as follows:  
(a) All pneumatic pumps must be tagged with an identifying marker to allow  
tracking for reporting as described in subrule (6) of this rule.  
(b) Initial performance and compliance testing must be conducted in accordance  
with a stack testing protocol approved by the department.  
(c) All control devices must have an approvable operation and maintenance plan  
that contains, at a minimum, the following:  
(i) A schedule of maintenance for the control devices in use.  
(ii) An inspection schedule at least once every calendar month.  
(iii) Written instructions from the manufacturer.  
(6) A person operating a pneumatic pump subject to this rule shall obtain current  
information and maintain records for all requirements in sufficient detail to  
determine compliance. The records must be made available to the department upon  
request and must include the following, as appropriate:  
(a) Notes of all pumps with control, and the respective control efficiencies, as  
determined by a stack test.  
(b) For all pumps with a control efficiency less than the control efficiency required  
by subrule (4) of this rule, infeasibility of meeting applicable criteria for capture and  
control for any uncontrolled pump which may include factors such as safety,  
distance, pressure losses and differentials, and the capacity of any available existing  
control device, to show that subrule (4) of this rule is not attainable.  
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(c) For all pumps at well sites without controls, a statement of confirmation that  
no control device has been installed.  
(d) Before March 1, 2023, an initial report must be submitted to the department  
describing initial compliance.  
(e) A report must be submitted to the department if a control device is installed on  
site after March 1, 2023.  
R 336.1643 Emission of volatile organic compounds from existing compressors in  
the oil and natural gas industry located in the 2015 ozone nonattainment areas.  
Rule 643. (1) As used in this rule:  
(a) “Centrifugal compressor” means any machine for raising the pressure of a  
natural gas by drawing in low-pressure natural gas and discharging significantly  
higher-pressure natural gas by means of mechanical rotating vanes or impellers.  
Screw, sliding vane, and liquid ring compressors are not centrifugal compressors for  
the purposes of this rule.  
(b) “Reciprocating compressor” means a piece of equipment that increases the  
pressure of a process gas by positive displacement, employing linear movement of  
the driveshaft.  
(2) A person shall not cause or allow the emission of any volatile organic compound  
from the use of existing compressors utilized in oil and natural gas production and  
natural gas processing segments of the oil and natural gas industry, in excess of the  
limitations of this rule that are both:  
(a) Located in the 2015 ozone nonattainment areas.  
(b) Located between the wellhead and point of custody transfer to the natural gas  
transmission and storage segment, and are either of the following:  
(i) A single centrifugal compressor using wet seals.  
(ii) A reciprocating compressor.  
(3) The provisions of this rule do not apply to the following:  
(a) Individual reciprocating compressor, or an individual centrifugal compressor  
using wet seals located at a well site, or an adjacent well site, and is servicing more  
than 1 well site.  
(b) Individual centrifugal compressor using dry seals.  
(4) A person shall not cause or allow the emission of any volatile organic  
compound from the centrifugal compressors, unless the following provisions are  
met:  
(a) Emissions from a centrifugal compressor wet seal fluid degassing system must  
be reduced by 95%.  
(b) When emissions from a centrifugal compressor are controlled by a control  
device, the following requirements must be met:  
(i) The wet seal fluid degassing system must be equipped with a cover that meets  
the following requirements:  
(A) The cover and all openings on the cover must form a continuous  
impermeable barrier over the entire surface area of the liquid in the wet seal fluid  
degassing system.  
109  
(B) Each cover opening must be secured in a closed, sealed position, for example,  
covered by a gasketed lid or cap, except during those times when it is necessary to  
use an opening as follows:  
(1) To inspect, maintain, repair, or replace equipment.  
(2) To vent gases or fumes from the unit through a closed vent collection system  
that meets the cover requirements and closed vent system requirements of  
R 336.1640.  
(ii) The closed vent system must be routed to a process or a control device that is  
designed to route all gases, vapors, and fumes emitted from the volatile organic  
compound emissions source to a control device or to a process.  
(iii) A continuous parameter monitoring system must be properly installed and  
operated to monitor all relevant control device operational variables.  
(5) A person shall not cause or allow the emission of any volatile organic  
compound from reciprocating compressors, unless the following provisions are  
met:  
(a) Compressor rod packing must be replaced within 36 months from the date of  
the most recent rod packing.  
(b) Rod packing emissions must be routed to a process by using a closed vent  
collection system that operates under negative pressure and meets the cover  
requirements and closed vent system requirements of R 336.1640. The closed vent  
system must be designed to route all volatile organic compound containing gases,  
vapors, and fumes to the process.  
(6) A person operating a compressor shall obtain current information and  
maintain records for all requirements in sufficient detail to determine compliance ,  
which must be made available to the department upon request. The following  
methods must be used:  
(a) An identification of each existing centrifugal compressor using a wet seal  
system.  
(b) Records of deviations where the centrifugal or reciprocating compressor was  
not operated in compliance with requirements.  
(c) Inlet gas flow rate.  
(d) Records of the maintenance and repair log.  
(e) Records of the visible emissions test following return to operation from a  
maintenance or repair activity.  
(f) Records of the cumulative number of hours of operation or number of months  
since the previous replacement of the reciprocating compressor rod packing.  
(g) Records of any control device operational variables monitored as part of the  
required continuous parameter monitoring system.  
R 336.1644 Emission of volatile organic compounds from fugitive emissions from  
the oil and natural gas industry located in the 2015 ozone nonattainment areas.  
Rule 644. (1) A person shall not cause or allow the emission of any volatile organic  
compound from existing fugitive emissions in the oil and natural gas production and  
natural gas processing segments of the oil and natural gas industry, in excess of the  
limitations of this rule that are both:  
(a) Located in the 2015 ozone nonattainment area.  
110  
(b) Either of the following:  
(i) Well sites.  
(ii) Gathering and boosting station located from the wellhead to the point of  
custody transfer to the natural gas transmission and storage segment or an oil  
pipeline.  
(2) The provisions of this rule do not apply to well sites that meet any of the  
following:  
(a) Produce on average, less than or equal to 15-barrel equivalents per day.  
(b) Have gas to oil ratios of less than 300 standard cubic foot of gas per barrel of  
oil produced, except as described in subrule (4) of this rule.  
(c) Only contain well heads.  
(3) A person shall not cause or allow the emission of any volatile organic  
compound from fugitive emissions unless a leak detection and repair program is  
implemented, as described in subrule (4) of this rule.  
(4) A leak detection and repair program must be developed and implemented for  
compliance with this rule and must contain the following components:  
(a) For well sites the program must include the following:  
(i) Semiannual monitoring using optical gas imaging (OGI) and repair of  
components that are found to be leaking.  
(ii) Each fugitive emissions component repaired or replaced be resurveyed to  
ensure there is no leak after repair or replacement by the use of either 40 CFR, part  
60, appendix A, method 21, adopted by reference in R 336.1902, or OGI, no later  
than 30 days after finding fugitive emissions.  
(b) For gathering and boosting stations in the production segment the program  
must include the following:  
(i) Quarterly monitoring using OGI and repair of components that are found to  
be leaking.  
(ii) Each fugitive emissions component repaired or replaced be resurveyed to  
ensure there is no leak after repair or replacement by the use of either 40 CFR, part  
60, appendix A, method 21, adopted by reference in R 336.1902, or OGI no later  
than 30 days after finding fugitive emissions.  
(c) The department can allow 40 CFR, part 60, appendix A, method 21, adopted  
by reference in R 336.1902, with a repair threshold of 500 ppm as an alternative  
compliance means to OGI.  
(5) A person operating a compressor shall obtain current information and  
maintain records for all requirements in sufficient detail to determine compliance,  
which must be made available to the department, upon request. These records must  
include the following, as applicable:  
(a) To demonstrate continuous compliance with the fugitive emission standards  
the following provisions must be met, as applicable:  
(i) A monitoring survey of each collection of fugitive emissions components at a  
well site must be conducted at least semiannually, not less than 4 months apart, after  
the initial survey.  
(ii) A monitoring survey of the collection of fugitive emissions components at a  
gathering and boosting station must be conducted at least quarterly, not less than 60  
days apart, after the initial survey.  
111  
(iii) A written plan must be developed to include the identification and location of  
each fugitive emissions component designated as difficult-to-monitor, an  
explanation of why each are designated as difficult to monitor, and a schedule for  
monitoring at least once per calendar year for the following:  
(A) Fugitive emission components designated as difficult-to-monitor, meaning  
monitoring cannot occur without elevating the monitoring personnel more than 2  
meters above the surface.  
(B) Fugitive emissions components designated as unsafe-to-monitor, meaning  
monitoring cannot be completed without exposing the monitoring personnel to  
immediate danger while conducting a monitoring.  
(b) Records maintained of the fugitive emissions monitoring plan as required  
under subrule (4) of this rule.  
R 336.1660 Standards for volatile organic compounds emissions from consumer  
products.  
Rule 660. (1) Except as provided in subrule (2) of this rule, tThe following  
provisions are adopted by reference in R 336.1902:  
(a) Before January 1, 2023, in the ozone transport commission's "OTC Model Rule  
for Consumer Products," 2006 (ver2006).  
(b) After April 30, 2023, the ozone transport commission's "OTC Model Rule for  
Consumer Products," dated May 10, 2012, (ver2012).  
(c) After December 31, 2022, the “Technical amendment to the Ozone Transport  
Commission Consumer Products Model Rule,” dated May 21, 2013. are adopted by  
reference in R 336.1902,  
(2) with Tthe following exceptions apply to the adoptions by reference in subrule  
(1)(a) and (b) of this rule:  
(a) Section (8)(b), variances.  
(b) All references to public hearings in section (8)(d) and (f).  
(b) Section (10), severability.  
(c) Section (11)(f), violations.  
(cd) In ver2006, wWhere the date "January 1, 2005” appears in the section (3)(a),  
table of standards, (f)(1)(i), and (g)(3), the following sections, the department shall  
instead recognize January 29, 2007:  
(i) Section (1), applicability.  
(ii) Section (3) (a), table, (f)(1)(i), and (g)(3) standards.  
(iii) Section (6)(d)(1), administrative requirements.  
(de) In ver2006, section 7(d)(2) and (3), where the date "2005" appears in section  
7(d)(2) and (3), the department shall instead recognize 2007. and Wwhere the date  
"March 1, 2006" appears in section 7(d)(2) and (3), the department shall instead  
recognize March 1, 2008.  
(e) In ver2012, where the date "January 1, 2005”, “January 1, 2009”, or “January  
1, 2014" appears in the section (3)(a) table of standards, (f)(1)(i), and (g)(3), the  
department shall instead recognize January 1, 2023.  
112  
(f) In ver2012, the volatile organic compound limit in section (3) table of standards  
for solid toilet/urinal care as it applies to products containing not less than 98%  
para-dichlorobenzene.  
(3) As used in the model rule:  
(a) "OTC state" means this state.  
(b) "Volatile organic compound" or "VOC" means a compound as defined in 40  
CFR 51.100. For the purpose of clarifying the definition, the provisions of 40 CFR  
51.100 are adopted by reference in R 336.1902.  
R 336.1661 Definitions for consumer products. Rescinded.  
Rule 661. As used in R 336.1660:  
(a) The "OTC state" means state of Michigan.  
(b) "Volatile organic compound" or "VOC" means a compound as defined in 40 C.F.R.  
§51.100, (2006). For the purpose of clarifying the definition, the provisions of 40 C.F.R.  
§51.100 (2006) are adopted by reference in R 336.1902.  
R 336.1662 Standards for volatile organic compounds emissions from architectural  
and industrial maintenance coatings.  
Rule 662. (1) After December 31, 2022, the provisions in the ozone transport  
commission's "Model Rule for Architectural and Industrial Maintenance (AIM)  
Coatings," are adopted by reference in R 336.1902, with the following exceptions:  
(a) Where the date “December 31, 2013” appears in “Table 1: VOC Content  
Limits for Architectural and Industrial Maintenance Coatings,” the department  
shall instead recognize December 31, 2022.  
(b) Where the date “January 1, 2014” appears in the following sections, the  
department shall instead recognize “January 1, 2023”:  
(i) Section (2), Definitions.  
(ii) Section (3), Standards.  
(iii) Section (4), Container Labeling Requirements, Table 1: VOC Content Limits  
for Architectural and Industrial Maintenance Coatings.  
(2) As used in the model rule:  
(a) Jurisdiction of the state or local air pollution control agency” means the  
department.  
(b) “Volatile Organic Compound” means the definition as promulgated in R  
336.1122(f).  
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;