§49.162. Air quality permit by rule for new or modified true minor source auto body repair and miscellaneous surface coating operations in Indian country.

Enter upon the premises where a permitted source is located or emissions-related activity is conducted or where records are required to be kept under the conditions of the permit by rule;

Have access to and copy, at reasonable times, any records that are required to be kept under the conditions of the permit by rule;

Inspect, during normal business hours or while the permitted source is in operation, any facilities, equipment (including monitoring and air pollution control equipment), practices or operations regulated or required under the permit by rule;

Sample or monitor, at reasonable times, substances or parameters for the purpose of assuring compliance with the permit by rule or other applicable requirements; and

5,000 gallons per year based on a 12-month rolling total for facilities located in ozone attainment, unclassifiable or attainment/unclassifiable areas; and

900 gallons per year based on a 12-month rolling total for facilities located in ozone nonattainment areas.

NOX emissions shall not exceed 30 ppmdv at 3 percent oxygen or 0.011 lb/MMBtu based on a 15-minute average.

CO emissions shall not exceed 400 ppmdv at 3 percent oxygen or 0.30 lb/MMBtu based on a 15-minute average.

All spray booths, preparation stations, and mobile enclosures must be equipped with an exhaust filter certified by the manufacturer to achieve at least 98 percent capture of paint overspray. The procedure used to demonstrate filter efficiency must be consistent with the American Society of Heating, Refrigerating, and Air-Conditioning Engineers (ASHRAE) Method 52.1, “Gravimetric and Dust-Spot Procedures for Testing Air-Cleaning Devices Used in General Ventilation for Removing Particulate Matter, June 4, 1992.” The test coating for measuring filter efficiency shall be a high solids bake enamel delivered at a rate of at least 135 grams per minute from a conventional (non-HVLP) air-atomized spray gun operating at 40 pounds per square inch (psi) air pressure; the air flow rate across the filter shall be 150 feet per minute. Owners and operators may use published filter efficiency data provided by filter vendors to demonstrate compliance with this requirement and are not required to perform this measurement. The requirements of this paragraph do not apply to water wash spray booths that are operated and maintained according to the manufacturer's specifications.

Spray booths and preparation stations used to refinish complete motor vehicles or mobile equipment must be fully enclosed with a full roof and four complete walls or complete side curtains, and must be ventilated at negative pressure so that air is drawn into any openings in the booth walls or preparation station curtains. However, if a spray booth is fully enclosed and has seals on all doors and other openings and has an automatic pressure balancing system, it may be operated at up to, but not more than, 0.05 inches water gauge positive pressure.

Spray booths and preparation stations that are used to coat miscellaneous parts and products or vehicle subassemblies must have a full roof, at least three complete walls or complete side curtains, and must be ventilated so that air is drawn into the booth. The walls and roof of a booth may have openings, if needed, to allow for conveyors and parts to pass through the booth during the coating process.

Mobile ventilated enclosures within the site that are used to perform spot repairs must enclose and, if necessary, seal against the surface around the area being coated such that paint overspray is retained within the enclosure and directed to a filter to capture paint overspray.

The exhaust filters of spray booths shall be equipped with pressure gauges that indicate, in inches of water, the static pressure differential across the exhaust filters.

Each spray booth located in a serious, severe, or extreme ozone nonattainment area that uses greater than 4 gallons per day of VOC-containing material shall install add-on controls (with greater than or equal to 90 percent collection efficiency and greater than or equal to 95 percent destruction efficiency) or use material with less than 5 percent VOC by weight or low VOC materials that result in an equivalent emission reduction.

The name and Material Safety Data Sheet (MSDS) for each VOC-containing material used onsite; and

The gallons of each VOC-containing material used each month and the resulting 12-month rolling total of VOC-containing material used. The 12-month rolling total is defined as the sum of the VOC material used during the current month and the VOC material used for the previous 11 months.

For each permitted source located in a serious, severe, or extreme ozone nonattainment area not complying with the control requirements in paragraph (d)(2)(ix)(F) of this section (add-on controls or low VOC-containing material), the combined daily gallons of VOC-containing material used in all spray booths.

The filter efficiency of the exhaust material;

The monthly exhaust filter pressure gauge readings specified in § 49.162(d)(3)(iii);

The date when each exhaust filter is replaced;

Any corrective actions taken to reduce overspray; and

The date of each test;

Each test plan;

Any documentation required to approve an alternate test method;

The results of each test;

The name of the company or entity conducting the analysis; and

An evaluation of the permitted source's compliance status with the requirements in paragraph (d)(2) of this section;

Summaries of the required monitoring and recordkeeping above in paragraphs (d)(3) and (4) of this section; and

The identity of the affected emissions unit(s) where the deviation occurred;

The nature of the deviation;

The length of time of the deviation;

The probable cause of the deviation; and

Any corrective actions or preventive measures taken as a result of the deviation to minimize emissions from the deviation and to prevent future deviations.

A description of the affected emissions unit and sampling location(s);

The time and date of each test;

A summary of test results, reported in units consistent with the applicable standard;

A description of the test methods and quality assurance procedures used;

A summary of any deviations from the proposed test plan and justification for why the deviation(s) was necessary;

The amount of fuel burned, raw material consumed, and product produced during each test run;

Operating parameters of the affected emissions units and control equipment during each test run;

Sample calculations of equations used to determine test results in the appropriate units; and