Mo. Code Regs. Ann. tit. 10, § 10-5.455
PURPOSE: This rule will reduce the volatile organic compounds emissions from industrial cleaning operations that use organic solvents.
(1) Applicability.
provided in subsections (1)(C) through (1)(G) of this rule, the provisions of this rule shall apply to any stationary source that emits at least three (3) tons per twelve (12)-month rolling period or more of volatile organic compounds (VOCs) from cleaning operations at the source, in the absence of air pollution control equipment, and stores and/or disposes of these solvent materials.
(C) The following solvent cleaning operations are not subject to the provisions of this rule:
ink, or cured adhesives;
press or graphic arts pre-press area, including the cleaning of film processors, color scanners, plate processors, film cleaning, and plate cleaning;
Nonmanufacturing areas include cafeterias, laboratories, pilot facilities, restrooms, janitorial cleaning, including graffiti removal, and office buildings; and
units within the following source categories listed for regulation under section 183(e) of the Clean Air Act:
coatings;
materials;
als;
ings;
and
(D) The following solvent cleaning operations are exempt from the VOC-content limitations specified in subsection (3)(A) of this rule:
ware, scientific instruments, and high-precision optics;
lowing: performance laboratory tests on coatings, adhesives, or inks; research and development programs; and laboratory tests in quality assurance laboratories;
clutch assemblies where rubber is bonded to metal by means of an adhesive;
cottonseed oil before cleaning of high-precision optics;
maceutical facilities using up to one and onehalf (1.5) gallons per day of solvents;
equipment used for thin metal laminating;
cables;
printed circuit boards where surface mounted devices have already been attached;
application processes utilized to manufacture transdermal drug delivery product using less than three (3) gallons per day of ethyl acetate;
used to apply coating on satellites and radiation effect coatings;
used to apply solvent-borne fluoropolymer coatings;
beam adhesive application;
ink application equipment if the facility uses less than one and one-half (1.5) gallons per day of solvents for such cleaning;
ening rollers, and printing plates;
with digital printing.
(160) fluid ounces) or less of the aerosol products per day.
until it can demonstrate, to the satisfaction of the director, that the total actual VOC emissions from solvent cleaning operations, before consideration of controls, is less than three (3) tons per twelve (12)-month rolling period for sixty (60) consecutive months.
(3) General Provisions.
(A) VOC-Content Limitations. No owner or operator of a source subject to this rule shall perform any cleaning operation subject to this rule unless the owner or operator meets the requirements in paragraph (3)(A)1., (3)(A)2., or (3)(A)3. of this rule—
cleaning solutions (minus water and exempt compounds) shall not exceed the following emissions limitations:
turing process or surface preparation for coating, adhesive, or ink application.
ment.
tions.
as-used cleaning solution used does not exceed eight millimeters of mercury (8.0 mmHg) measured at twenty degrees Celsius (20 °C) (sixty-eight degrees Fahrenheit (68 °F)); or
installed and operated that reduces VOC emissions from the subject cleaning operation by at least eighty-five percent (85%) overall. The owner or operator may use an emission control system other than an afterburner or carbon adsorber if such device reduces VOC emission from the subject cleaning operation by at least eighty-five percent (85%) by mass, the owner or operator submits a plan to the director detailing appropriate monitoring devices, test methods, record-keeping requirements, and operation parameters for such a control device, and such a plan is approved by the director and the U.S. Environmental Protection Agency (EPA) within federally-enforceable permit conditions.
(B) Cleaning Devices and Methods. The owner or operator of a facility that is subject to this rule shall employ one (1) or more of the following cleaning devices and methods:
bottles from which solvents are applied;
vent 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; and
ator of the cleaner complies with all of the following:
escaping from the solvent container by using such devices as a cover or a valve when the remote reservoir is not being used, cleaned, or repaired;
that will prevent liquid solvent from splashing outside of the remote reservoir cleaner;
absorbent materials, such as cloth, leather, wood, or rope;
of all liquid leaks. Auxiliary equipment, such as pumps, pipelines, or flanges, shall not have any liquid leaks, visible tears, or cracks. Any liquid leak, visible tear, or crack detected shall be repaired within one (1) calendar day, or the leaking section of the remote reservoir cold cleaner shall be drained of all solvent and shut down until it is repaired or replaced;
where the cleaning solvent is collected in a container or a collection system which is closed except for solvent collection openings and, if necessary, openings to avoid excessive pressure build-up inside the container; and
cleaning solvent is discharged into a container which is closed except for solvent collection openings, and, if necessary, other openings to avoid excessive pressure build-up inside the container. The discharged solvent from the equipment must be collected into containers without atomizing into the open air. The solvent may be flushed through the system by air or hydraulic pressure or by pumping.
(C) Operating Requirements. The owner or operator of a source subject to the requirements of this section shall comply with the following for each subject cleaning operation:
ly cover and store applicators used to apply cleaning solvents;
tions, cleaning towels, and applicators used to apply cleaning solvents in closed containers that are nonleaking and nonabsorbent;
cleaning operation; and
imize emissions.
(E) Requirements for coatings, inks, and resin manufacturers. Coating, ink, and resin manufacturers must comply with the following requirements:
vats, high dispersion mills, grinding mills, tote tanks, and roller mills by one (1) or more of the following methods:
that either contains less than 1.67 pounds per gallon (0.20 kilograms per liter) of VOC or has a composite vapor pressure no more than eight millimeters of mercury (8.0 mmHg) at twenty degrees Celsius (20 °C);
from equipment cleaning to a VOC emission control system that has an overall capture and control efficiency of at least eighty percent (80%) by weight for the VOC emissions. Where such reduction is achieved by incineration, at least ninety percent (90%) of the organic carbon shall be oxidized to carbon dioxide;
those allowed in subparagraph (3)(E)1.A. of this rule provided no more than sixty (60) gallons (two hundred twenty-eight (228) liters) of fresh solvent shall be used per month. Organic solvent that is reused or recycled (either onsite or offsite), for further use in equipment cleaning or the manufacture of coating, is not included in this limit; or
practices:
be maintained leak free;
rials must be drained from the cleaned equipment upon completion of cleaning;
materials, including waste solvents, shall not be stored or disposed of in such a manner that will cause or allow evaporation into the atmosphere; and
materials in closed containers; and Specific to the St. Louis Metropolitan Area
ing, the owner or operator of a facility shall—
storage or disposal of cloth or paper impregnated with organic compounds that is used for cleanup or coating, ink, or resin removal; and
compounds to be used for cleanup or coating, ink, or resin removal in open containers.
(4) Reporting and Record Keeping. All owners and operators subject to this rule shall maintain records as required by this section sufficient to determine continuous compliance with this rule. These records shall be kept for at least five (5) years to be automatically extended if enforcement action is pending. These records shall be made available immediately upon request for review by the Department of Natural Resources’ personnel and other air pollution control agencies upon presentation of proper credentials.
(A) The owner or operator of a facility that includes an industrial solvent cleaning operation shall keep records detailing specific VOC uses as necessary for the director to determine monthly compliance. All facility records must include the following:
and/or stored at the site. The list shall include the following information:
name/code/manufacturer;
cleaning solvents, based upon EPA Method 24, of each cleaning material, in pounds per gallon of material, as applied or the VOC composite partial vapor pressures of the solvents or solvent solutions used in the industrial cleaning operations. This calculation need only be performed once for each batch of cleaning solution used; and
cleaning solvent as applied; and
lowing information:
volume in gallons for each cleaning solvent used;
ing activity associated with each solvent used;
aerosol products in ounces used; and
(summation of gallons × VOC content (in pounds per gallon)).
(B) If a facility includes automatic equipment, records shall also include, as applicable, the following:
ment that prepares each batch of cleaning solution(s) on site, records for each batch shall include:
each cleaning solution;
solvent in the cleaning solution;
automatic equipment, with date, time, description of changes in the cleaning solution constituents (e.g., cleaning solvents), and description of changes to the proportion of cleaning solvent and water (or other non- VOC);
solvent and water (or other non-VOC) used to prepare the as-used cleaning solution;
cleaning solution, with the supporting calculations; and
equipment, detailing periodic checks;
ment that does not prepare cleaning solution(s) on site, records for each batch of cleaning solution shall include:
each cleaning solution;
subsequent modification of the batch;
solvent in the cleaning solution;
solvent and water (or other non-VOC) used to prepare the as-used cleaning solution; and
cleaning solution, with supporting calculations; and
prepared at the site, but are used as-purchased, the manufacturer’s specifications for VOC content may be used if such manufacturer’s specifications are based on the results of tests of the VOC content in accordance with EPA Method 24.
(C) Any owner or operator using an emission control device pursuant to this rule shall maintain records, on a daily basis, of key system operating parameters for emission control equipment, including, but not limited to:
control system used;
nance, including dates and duration of any outages;
cleaning operation employs a thermal oxidizer or catalytic oxidizer to achieve and main- 10 CSR 10-5
tain compliance, the owner or operator shall comply with the following requirements:
ing and continuous temperature recording equipment shall be installed and operated to accurately measure the operating temperature(s) for the control device; and
collected and recorded each day of operation of the solvent cleaning operation and the control device, and the information shall be maintained at the facility for a period of five (5) years:
time for the control device, monitoring equipment, and the associated solvent cleaning operation;
(3)-hour periods of operation during which the average combustion temperature was more than fifty degrees Fahrenheit (50 °F) below the average combustion temperature during the most recent emission test that demonstrated that the solvent cleaning operation was in compliance; and
three (3)-hour periods of operation during which the average temperature of the dryer exhaust gases immediately before the catalyst bed was more than fifty degrees Fahrenheit (50 °F) below the average temperature of the dryer exhaust gases during the most recent emission test that demonstrated that the solvent cleaning operation was in compliance, and all three (3)-hour periods during which the average temperature difference across the catalyst bed was less than eighty percent (80%) of the average temperature difference during the most recent emission test that demonstrated that the solvent cleaning operation was in compliance; and
cleaning operation employs a carbon adsorption system to achieve and maintain compliance, the owner or operator shall comply with the following requirements:
ment that records all of the following shall be installed and operated for the carbon adsorption system:
ing and recording system that is capable of accurately measuring and recording the concentration of organic compounds in the exhaust gases from the carbon adsorption system;
equipment that are capable of accurately measuring and recording the total mass steam flow rate for each regeneration cycle of each carbon bed; and
equipment that are capable of accurately measuring and recording the temperature of each carbon bed after regeneration (and after completion of any cooling cycle(s)); and
collected and recorded each day of operation of the solvent cleaning operation and the carbon adsorption system:
time for the carbon adsorption system, monitoring equipment, and the associated solvent cleaning operation;
that employs a continuous emission monitoring and recording system to measure and record the concentration of organic compounds in the exhaust gases, all three (3)- hour periods of operation during which the average concentration level or reading in the exhaust gases is more than twenty percent (20%) greater than the exhaust gas organic compound concentration level or reading measured by the most recent performance test that demonstrated that the solvent cleaning operation was in compliance;
tem that employs monitoring and recording equipment to measure and record the total mass steam flow rate for each regeneration cycle of each carbon bed, all carbon bed regeneration cycles during which the total mass steam flow rate was more than ten percent (10%) below the total mass steam flow rate during the most recent performance test that demonstrated that the solvent cleaning operation was in compliance; and
tem that employs monitoring and recording equipment to measure and record the temperature of each carbon bed after regeneration (and after completion of any cooling cycle(s)) was more than ten percent (10%) greater than the carbon bed temperature during the most recent performance test that demonstrated that the solvent cleaning operation was in compliance.
(5) Test Methods. Certain test methods mentioned in this rule may be found in 10 CSR 10-6.030. Other EPA test methods specific to this rule may be found in 40 CFR 60, Appendix A.
(A) Control Efficiency Testing. To demonstrate compliance with the emission limits of subsection (3)(C) of this rule, an initial emission test shall be performed after any required control equipment is installed. The emission limits shall not have been met until compliance has been verified through this testing. Testing shall also be required after significant modifications to any control equipment required by this rule. Significant modifications include any repairs or changes that might substantially alter or affect the overall control efficiency. This subsection outlines the methods to be used for any such testing.
ical operating conditions and flow rates compatible with scheduled production during any emission testing.
shall be used to select the sampling sites.
appropriate, shall be used to determine the velocity and volumetric flow rate of the exhaust stream.
shall be used to determine the concentration of oxygen (O2) and carbon dioxide (CO2).
mine moisture content.
used to determine the VOC concentration of the exhaust stream entering and exiting the control device, unless the alternate limit in paragraph (3)(C)2. of this rule is being used for compliance, in which case only the VOC concentration of the exit exhaust shall be determined. In cases where the anticipated outlet VOC concentration of the control device is less than fifty parts per million by volume (50 ppmv) as carbon, EPA Method 25A shall be used.
7. If EPA Method 25A is used—
or catalytic oxidizer may be corrected by using EPA Method 18 or 25 to determine non-VOC components (methane and ethane) and subtracting these from the Method 25A result; and
by EPA Method 18 or 25 if the average corrected outlet reading is greater than fifty (50) ppmv VOC as carbon.
to three (3) separate runs, each lasting a minimum of sixty (60) minutes unless the director determines that the circumstances dictate shorter sampling times.
probe temperature of two hundred sixty-five degrees Fahrenheit (265 °F). To prevent condensation, the probe should be heated to at least the gas stream temperature, typically close to three hundred fifty degrees Fahrenheit (350 °F).
mum temperature of two hundred twenty degrees Fahrenheit (220 °F) for the sampling components leading to the analyzer. To prevent condensation when testing heatset printing presses, the sampling components and flame ionization detector lock should be heated to at least the gas stream temperature, typically close to three hundred fifty degrees Fahrenheit (350 °F).
or the temperature of the gas upstream of the catalyst bed may be used as the operating parameter for determining continuous compliance with the emission standard of subsection (3)(C) of this rule. This temperature shall be computed as the time-weighted average of the temperature values recorded during the test. The owner or operator must maintain the oxidizer at a three (3)-hour average temperature no less than fifty degrees Fahrenheit (50 °F) below the average temperature observed during the most recent stack test to demonstrate continuous compliance.
methods specified in this subsection may be approved by the director on a case-by-case basis. The owner or operator shall submit sufficient documentation for the director to find that the methods specified in this subsection will yield inaccurate results and that the proposed adaptation is appropriate.
the procedure in 10 CSR 10-6.030(20).
(B) VOC Content Testing for Cleaning Solutions. The VOC content or VOC composite partial vapor pressure of cleaning solutions shall be determined by one (1) of the following:
content or by an appropriate method for VOC composite partial vapor pressure of a sample of the cleaning solution. The analysis may be performed by the supplier of those materials;
combines EPA Method 24 analytical data for the concentrated materials used to prepare the cleaning solution and the proportions in which they are mixed to make the cleaning solution as applied. Owners or operators may use formulation information provided with the concentrated materials used to prepare the cleaning solution, such as the container label, the product data sheet, or the Material Safety Data Sheet (MSDS) to document the VOC content of the concentrated material; or
MSDS or manufacturer’s formulation data sheet may be used.
AUTHORITY: section 643.050, RSMo Supp. 2011.* Original rule filed Oct. 7, 1994, effective May 28, 1995. Amended: Filed July 15, 1996, effective Feb. 28, 1997. Amended: Filed Nov. 30, 2010, effective Aug. 30, 2011. Amended: Filed Sept. 16, 2011, effective May 30, 2012. *Original authority: 643.050, RSMo 1965, amended 1972, 1992, 1993, 1995, 2011; transferred from 203.050 in 1986. Specific to the St. Louis Metropolitan Area