New Source Performance Standards Metal Furniture Surface Coatings Public Participation A public hearing on the proposed regula- tion is scheduled for January 9, 1981 at 9 a.m. at the Environ- mental Research Cen- ter Auditorium, Re-- search Triangle Park, NC. Those wishing to present additional data, views, or other com- ments on this NSPS are invited to participate. If you plan to speak at the hearing, contact Deanna Tilley, Standards Development Branch, Emission Standards and Engineering Division,(MD13), Environmental Protection Agency, Research Triangle Park, NC 27711, telephone 919-541-5477, no later than January 2, 1981. Written comments (in duplicate if possible) will be accepted on or before February 8, 1981 and should be addressed to: Central Docket Section (A-130), Attention: Docket Number A79-47, U.S. EPA, 401 M Street, SW, Washington, DC 20460. The docket contains all information considered by EPA in developing these proposed standards, and is open for public inspection. The background information document, "Surface Coating of Metal Furniture—Background Information for Proposed Standards" (EPA-450/3-80-007a), discusses this material in detail and is available from the EPA Library (MD-35), Research Tri- angle Park, NC 27711, telephone 919-541- 2777. Status of Regulation This proposed NSPS was published in the Federal Register (45 FR 79390) on November 28, 1980. A public hearing is scheduled for January 9, 1981. The final regulation is expected around November, 1981. DOES asn ssauisng IBIDIJJO 9EE Vd3 ADU36y uouoajojj ON ' P!"d sasj pue a6e»so,j saieis liliR Isll ' •Z>-n-nm cocngo Qrm ill' .0 » 2. s ^ : 11 § ° ? 3 3 O *"* «' 3 I o I § ^ 3. —• to_ Q) I 8 S 5 « 3 " x 3 O. „ 5' "' -• o- O 3 w> O < ;|g i " ^. w Z QT (C QJ Q) ff S a- 8 *$ 5 ffi Qi ™ Q. " c o, * ™ ~ C (O « S 33—5 II ffl s s| « ?• i- « 3 £. n "> » S * a (B ^ 3 « S « 2 -» a C K 9t • K S.°-S 3 - 3 3 o • |S 3 o, S - s; Or » u 2 55 aS < D. rt ™ United States Environmental Protection Agency Office of Air Quality Planning and Standards Research Triangle Park, NC 27711 December 1980 New Source Performance Standards xvEPA Metal Furniture Surface Coatings Proposed Regulation ------- •New Source Performance Standards- Metal Furniture Surface Coatings New Source Performance Standards The Clean Air Act, as amended in 1977, calls for a comprehensive national program to re- duce air pollution and improve air quality. The Act requires the U.S. Environmental Pro- tection Agency (EPA) to establish nationwide emission standards for selected new industrial stationary sources. These New Source Per- formance Standards (NSPS), in accordance with Section 111 of the Act, are designed to prevent new air pollution problems. NSPS apply to categories of new, modified, or reconstructed stationary sources that cause or contribute significantly to air pollution that could endanger public health or welfare. EPA has proposed NSPS for metal furniture sur- face coating operations. Metal Furniture Surface Coatings V Section 111 of the Clean Air Act requires EPA to set Federal emission limits for stationary sources iden- tified as significant contributors to air pol- lution that endanger public health and welfare. After careful study and evaluation, EPA has classified new, mod- ified, and reconstructed surface coating facil- ities at metal furniture manufacturing plants as one such source. Paints traditionally used in metal furniture coating operations contain organic solvent mixtures, and their use results in the emission of volatile organic compounds (VOC). VOC emissions occur during the coating application, touch-up and flash-off processes, and in the bake oven area of the plant. VOC react in the atmosphere to form ozone, the main component of photochemical smog. Ozone irritates the respiratory system and aggravates chronic respiratory diseases. It also damages plant tissues, and deteriorates rubber and other materials. In 1975, the metal furniture industry emitted about 95,000 metric tons of VOC. The selec- tion of industrial surface coating of metal furniture for regulation is based on EPA's de- termination that it is a significant source of VOC emissions as well as analyses of painting methods, yearly VOC emission rates, pro- jected industry growth, and the number and location of affected facilities in or near highly populated urban areas. There are presently 1400 metal furniture manufacturing plants nationwide, 70 percent of which are located in highly populated urban areas. EPA projects a four percent an- nual growth rate for the metal furniture in- dustry through 1985. Setting Standards to Limit Emissions The proposed NSPS would apply to all new, modified, and reconstructed metal furniture surface coating facilities for which construc- tion began after November 28, 1980. The recommended standards would limit VOC emissions to 0.70 kilogram of VOC per liter of coating solids applied. This emission limit could be met by use of 68-percent-by-volume solids coating (with a solvent density of 0.88 kilogram per liter) applied at a 60 percent transfer efficiency. In addition, waterborne, powder, and other high solid coatings and add-on control equipment may also be employed to achieve the numerical limit. VOC emissions from existing metal furniture coating operations are controlled by State air pollution regulations. If controlled only through existing State regulations, yearly VOC emissions would be about 60 percent less compared to uncontrolled operations. The proposed standards would result in an ad- ditional 30 percent emission reduction beyond State regulations. For facilities oper- ating with no pollution controls, the proposed standards would reduce VOC emissions by 51,000 metric tons during the next five years. Achieving and Maintaining the Standards lated to air quality. The proposed NSPS reflect the best dem- onstrated system of continuous emission reduction, considering costs, health, environ- mental, energy, and other impacts unre- Several different control options are available for reducing VOC emissions. Emission control technologies include the use of (1) low or- ganic solvent coatings; (2) improved trans- fer efficiencies based on coating application techniques; or (3) add-on control devices. A combination of control options would be acceptable providing equivalent VOC emission reduction could be demonstrated. These op- tions include waterborne coatings applied by electrostatic air or airless spray, dip, electro- deposition or flow techniques; powder coat- ings applied by electrostatic spray or fluidized bed; and lower content of solids within paints (less than 68-percent-by-volume solids coating if the increased solvent content is offset by higher transfer efficiencies). Two reference methods would be used to de- termine compliance with the proposed emis- sion standards. Reference Method 24 (pro- mulgated on October 3, 1980) would deter- mine the VOC content of coating materials; however, the use of coating manufacturers' data would be allowed in calculating the VOC content of coatings. Reference Method 25 (promulgated on Octobers, 1980) would be used to determine the VOC concentration in exhaust gas streams. Impacts Energy: Actual energy requirements would vary depending on the control option select- ed to meet the proposed standards. For a typical metal furniture manufacturer com- plying with existing State requirements, en- ergy use would decrease by about 20 percent (1500 gigajoules) if powder coatings were used. However, energy use would increase if waterborne coatings or incineration plus a State compliance coating were used by 3 per- cent (230 gigajoules) and 7 percent (520 giga- joules), respectively. Environmental: No adverse environmental im- pacts would result from the standards. Nega- tive impacts from control options are possible only for water and solid wastes. The impacts on solid waste and water quality would depend on the specific control option selected. Economic/Industrial: Economic impacts of the proposed NSPS would vary, depending on the control option selected. The estimat- ed total capital costs are about the same for all control options. Total annualized costs for the first five years would vary depending on the control option used, and annualized sav- ings are possible. The maximum possible eco- nomic impact would be for small manufac- turers, regardless of the control option selec- ted. It could mean up to a 1.3 percent in- crease in the wholesale price of their product. ------- |