justicedao/ipfs_state_laws huggingface dataset:
340-232-0130 Petroleum Refineries This rule shall apply to all petroleum refineries: (1) Vacuum-Producing Systems: (a) Noncondensable VOC from vacuum producing systems shall be piped to an appropriate firebox, incinerator or to a closed refinery system; (b) Hot wells associated with contact condensers shall be tightly covered and the collected VOC introduced into a closed refinery system. (2) Wastewater Separators: (a) Wastewater separators' forebays shall incorporate a floating pontoon or fixed solid cover with all openings sealed totally enclosing the compartmented liquid contents, or a floating pontoon or double deck-type cover equipped with closure seals between the cover edge and compartment wall; (b) Accesses for gauging and sampling shall be designed to minimize VOC emissions during actual use. All access points shall be closed with suitable covers when not in use. (3) Process Unit Turnaround: (a) The VOC contained in a process unit to be depressurized for turnaround shall be introduced to a closed refinery system, combusted by a flare, or vented to a disposal system; (b) The pressure in a process unit following depressurization for turnaround shall be less than 5 psig before venting to the ambient air. (4) Maintenance and Operation of Emission Control Equipment: Equipment for the reduction, collection or disposal of VOC shall be maintained and operated in a manner commensurate with the level of maintenance and housekeeping of the overall plant. (5) Recordkeeping: The owner or operator shall maintain a record of process unit turnarounds including an approximation of the quantity of VOC emitted to the atmosphere. Records shall be maintained for two years. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-022-0150 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 8-1991, f. & cert. ef. 5-16-91 DEQ 23-1980, f. & ef. 9-26-80 DEQ 17-1979, f. & ef. 6-22-79 DEQ 21-1978, f. & ef. 12-28-78
340-232-0200 Conveyorized Degreasers (1) The owner or operator of conveyorized cold cleaners and conveyorized vapor degreasers must comply with the following operating requirements: (a) Exhaust ventilation must not exceed 20 cubic meters per minute per square meter (65 cubic feet per minute per square foot) of degreaser opening, unless necessary to meet OSHA requirements. Workplace fans must not be used near the degreaser opening; (b) Post in the immediate work area a permanent and conspicuous pictograph or instructions clearly explaining the following work practices: (A) Rack parts for best drainage; (B) Maintain vertical speed of conveyored parts to less than 3.35 meters per minute (11 feet/minute); (C) The condenser water must be turned on before the sump heater when starting up a cold vapor degreaser. The sump heater must be turned off and the solvent vapor layer allowed to collapse before closing the condenser water when shutting down a hot vapor degreaser. (2) A routine inspection and maintenance program must be implemented for the purpose of preventing and correcting solvent losses, as for example, from dripping drain taps, cracked gaskets, and malfunctioning equipment. Leaks must be repaired immediately. (3) Sump drainage and transfer of hot or warm solvent must be carried out using threaded or other leak-proof couplings. (4) Still and sump bottoms must be kept in closed containers. (5) Waste solvent must be stored in covered containers and returned to the supplier or a disposal firm handling solvents for final disposal, such that no greater than 20 percent of the waste by weight can evaporate into the atmosphere. Handling of the waste must also be done in accordance with DEQ's Solid and Hazardous Waste Rules, OAR 340 division 100. (6) All conveyorized cold cleaners and conveyorized vapor degreasers with air/vapor interfaces of 2.0 m2 or greater must have one of the following major control devices installed and operating: (a) Carbon adsorption system, exhausting less than 25 ppm of solvent averaged over a complete adsorption cycle, based on exhaust ventilation of 15 m3/minutes per m2 of air/vapor area, when down-time covers are open; or (b) Refrigerated chiller with control effectiveness equal to or better than subsection (a); or (c) A system with control effectiveness equal to or better than subsection (a). NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 143-2018, minor correction filed 04/11/2018, effective 04/11/2018 DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-022-0186 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 8-1991, f. & cert. ef. 5-16-91 DEQ 3-1986, f. & ef. 2-12-86 DEQ 23-1980, f. & ef. 9-26-80 DEQ 17-1979, f. & ef. 6-22-79 DEQ 21-1978, f. & ef. 12-28-78
340-232-0210 Asphaltic and Coal Tar Pitch Used for Roofing Coating (1) No person shall operate or use equipment for melting, heating or holding asphalt or coal tar pitch for the on-site construction, installation, or repair of roofs unless the gas-entrained effluents from such equipment are contained by close fitting covers. (2) A person operating equipment subject to this rule shall maintain the temperature of the asphaltic or coal tar pitch below 285° C. (550° F.), or 17° C. (30° F.) below the flash point whichever is the lower temperature, as indicated by a continuous reading thermometer. (3) The provisions of this rule shall not apply to equipment having a capacity of 100 liters (26 gallons) or less; or to equipment having a capacity of 600 liters (159 gallons) or less provided it is equipped with a tightly fitted lid or cover. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-022-0190 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 8-1991, f. & cert. ef. 5-16-91 DEQ 23-1980, f. & ef. 9-26-80 DEQ 17-1979, f. & ef. 6-22-79 DEQ 21-1978, f. & ef. 12-28-78
340-232-8010 Division 232 Attachments This rule contains copies of EPA Methods referenced in this Division. [NOTE: View a PDF of referenced EPA Methods by clicking on "Tables" link below.] [ED. NOTE: To view attachments referenced in rule text, click here to view rule.] Statutory/Other Authority: 468.020, 468A.025, 468A.050 & 468A.070 Statutes/Other Implemented: 468A.025, 468A.050 & 468A.070 History: DEQ 13-2019, adopt filed 05/16/2019, effective 05/16/2019
340-234-0005 Applicability and Jurisdiction (1) This division applies in all areas of the state. (2) Subject to the requirements in this division and OAR 340-200-0010(3), LRAPA is designated by the EQC to implement the rules in this division within its area of jurisdiction. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020, 468A.025 & 468A.135 Statutes/Other Implemented: ORS 468A.025 & 468A.135 History: DEQ 7-2015, f. & cert. ef. 4-16-15
340-234-0100 Wigwam Waste Burners (1) Operation of wigwam waste burners is prohibited. (2) Emissions from wigwam waste burners included in a source's netting basis as of October 18, 2007 shall not be subtracted from the netting basis, except as provided in OAR 340-222-0046. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0010 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 37, f. 2-15-72, ef. 3-1-72
340-234-0140 Wigwam Waste Burners: Existing Administrative Agency Orders The provisions of OAR 340-234-0100 supersede any specific existing agency orders directed against specific parties or persons to abate air pollution. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A .025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0027 DEQ 22-1995, f. & cert. ef. 10-6-95 DEQ 4-1993, f. & cert. ef. 3-10-93, Renumbered from 340-025-0080 SA 30 f. 6-7-68, cert. ef. 8-1-68
340-234-0200 Kraft Pulp Mills: Statement of Policy and Applicability (1) Policy. Recent technological developments have enhanced the degree of malodorous emission control possible for the kraft pulping process. While recognizing that complete malodorous and particulate emission control is not presently possible, consistent with the meteorological and geographical conditions in Oregon, it is hereby declared to be the policy of DEQ to: (a) Require, in accordance with a specific program and time table for all sources at each operating mill, the highest and best practicable treatment and control of atmospheric emissions from kraft mills through the utilization of technically feasible equipment, devices, and procedures. Consideration will be given to the economic life of equipment, which when installed, complied with the highest and best practicable treatment requirement. (b) Require degrees and methods of treatment for major and minor emission points that will minimize emissions of odorous gases and eliminate ambient odor nuisances. (c) Require effective monitoring and reporting of emissions and reporting of other data pertinent to air quality or emissions. DEQ will use these data in conjunction with ambient air data and observation of conditions in the surrounding area to develop and revise emission and ambient air standards, and to determine compliance therewith. (d) Encourage and assist the kraft pulping industry to conduct a research and technological development program designed to progressively reduce kraft mill emissions, in accordance with a definite program, including specified objectives and time schedules. (2) Applicability. OAR 340-234-0200 through 340-234-0270 apply to existing and new kraft pulp mills. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040 with the exception of references to Total Reduced Sulfur. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0155 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 50, f. 2-9-73, ef. 3-1-73
340-234-0220 Kraft Pulp Mills: More Restrictive Emission Limits The DEQ may establish more restrictive emission limits than the numerical emission standards contained in OAR 340-234-0210 and maximum allowable daily mill site emission limits in kilograms or pounds per day for an individual mill upon a finding by DEQ that: (1) The individual mill is located or is proposed to be located in a special problem area or an area where ambient air standards are exceeded or are projected to be exceeded or where the emissions will have a significant impact in an area where the standards are exceeded; or (2) An odor or nuisance problem has been documented at any mill, in which case the TRS emission limits may be reduced below the regulatory limits; or DEQ may require the mill to undertake an odor emission reduction study program; or (3) Other rules which are more stringent apply. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040 with the exception of references to Total Reduced Sulfur. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0170 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 2-1990, f. & cert. ef. 1-24-90 DEQ 137, f. & ef. 6-10-77 DEQ 50, f. 2-9-73, ef. 3-1-73
340-234-0250 Kraft Pulp Mills: Reporting If required by DEQ or by permit, each mill must report data each calendar month by the last day of the subsequent calendar month as follows: (1) Applicable daily average emissions of TRS gases expressed in parts per million of H2S on a dry gas basis with oxygen concentrations, if oxygen corrections are required, for each source included in the approved monitoring program. (2) Daily average emissions of TRS gases in pounds of total reduced sulfur per equivalent ton of pulp processed, expressed as H2S, for each source included in the approved monitoring program. (3) Maximum daily three-hour average emission of SO2 based on all samples collected from the recovery furnace, expressed as ppm, dry basis. (4) All daily average opacities for each recovery furnace stack where transmissometers are utilized. (5) All six-minute average opacities from each recovery furnace stack that exceeds 35 percent. (6) Daily average kilograms of particulate per equivalent metric ton (pounds of particulate per equivalent ton) of pulp produced for each recovery furnace stack. (7) Unless otherwise approved in writing, all periods of non-condensable gas bypass must be reported. (8) Each kraft mill must furnish, upon request of DEQ, such other pertinent data as DEQ may require to evaluate the mill's emission control program. (9) Monitoring data reported must reflect actual observed levels corrected for oxygen, if required, and analyzer calibration. (10) Oxygen concentrations used to correct regulated pollutant data must reflect oxygen concentrations at the point of measurement of regulated pollutants. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040 with the exception of references to Total Reduced Sulfur. Statutory/Other Authority: ORS 468.020, 468A.025 & 468A.050 Statutes/Other Implemented: ORS 468A.025 & 468A.050 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0185 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 2-1990, f. & cert. ef. 1-24-90 DEQ 132, f. & ef. 6-10-77 DEQ 50, f. 2-9-73, ef. 3-1-73
340-234-0270 Kraft Pulp Mills: Chronic Upset Conditions If DEQ determines that an upset condition is chronic and correctable by installing new or modified process or control procedures or equipment, the owner or operator must submit to DEQ a program and schedule to effectively eliminate the deficiencies causing the upset conditions. Such reoccurring upset conditions causing emissions in excess of applicable limits may be subject to civil penalty or other appropriate action. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040 with the exception of references to Total Reduced Sulfur. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0205 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 2-1990, f. & cert. ef. 1-24-90 DEQ 50, f. 2-9-73, ef. 3-1-73
340-234-0500 Board Products Industries (Veneer, Plywood, Particleboard, Hardboard): Applicability and General Provisions (1) OAR 340-234-0500 through 340-234-0530 establish minimum performance and emission standards for veneer, plywood, particleboard, and hardboard manufacturing operations. (2) Emission limitations established herein are in addition to, and not in lieu of, general emission standards for visible emissions, fuel burning equipment, and refuse burning equipment, except as provided for in OAR 340-234-0510. (3) Each affected veneer, plywood, particleboard, and hardboard plant must proceed with a progressive and timely program of air pollution control. Each plant must, at the request of DEQ submit periodic reports in such form and frequency as directed to demonstrate the progress being made toward full compliance with OAR 340-234-0500 through 340-234-0530. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020, 468A.025 & 468A.050 Statutes/Other Implemented: ORS 468A.025 & 468A.050 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0500 DEQ 17-1993, f. & cert. ef. 11-4-93 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 132, f. & ef. 4-11-77 DEQ 26, f. 3-31-71, ef. 4-25-71
340-234-0520 Board Products Industries (Veneer, Plywood, Particleboard, Hardboard): Particleboard Manufacturing Operations (1) Truck Dump and Storage Areas: (a) Every person operating or intending to operate a particleboard manufacturing plant must enclose truck dump and storage areas holding or intended to hold raw materials to prevent windblown particle emissions from these areas from being deposited upon property not under the ownership of said person; (b) The temporary storage of raw materials outside the regularly used areas of the plant site is prohibited unless the person who desires to temporarily store such raw materials first notifies DEQ and receives written approval for said storage: (A) When authorized by DEQ, temporary storage areas must be operated to prevent windblown particulate emissions from being deposited upon property not under the ownership of the person storing the raw materials; (B) Any temporary storage areas authorized by DEQ may not be operated in excess of six (6) months from the date they are first authorized. (c) Any person who proposes to control windblown particulate emissions from truck dump storage areas other than by enclosure must apply to DEQ for written authorization to utilize alternative controls. The application must describe in detail the plan proposed to control windblown particulate emissions and indicate on a plot plan the nearest location of property not under ownership of the applicant. (2) Other Emission Sources: (a) The combined particulate emissions from particleboard plant sources including, but not limited to, hogs, chippers, and other material size reduction equipment, process or space ventilation systems, particle dryers, classifiers, presses, sanding machines, and materials handling systems must not exceed a plant specific average hourly emission rate, pounds per hour, determined by multiplying the plant production capacity by three pounds per 1000 square feet. The plant production capacity is the maximum production in terms of 1,000 square feet on a 3/4 inch basis of finished product for a typical operating shift divided by the number of hours in the operating shift. (b) Excepted from subsection (2)(a) are truck dump and storage areas, fuel burning equipment, and refuse burning equipment. (c) Compliance with the average hourly emission rate is determined by summing the emissions from the affected sources as determined by emission factor calculations or actual emissions data for a 24 hour period divided by 24. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020 & 468A.025 Statutes/Other Implemented: ORS 468A.025 History: DEQ 7-2015, f. & cert. ef. 4-16-15 DEQ 8-2007, f. & cert. ef. 11-8-07 DEQ 14-1999, f. & cert. ef. 10-14-99, Renumbered from 340-025-0320 DEQ 3-1996, f. & cert. ef. 1-29-96 DEQ 4-1995, f. & cert. ef. 2-17-95 DEQ 4-1993, f. & cert. ef. 3-10-93 DEQ 130, f. & ef. 3-22-77 DEQ 26, f. 3-31-71, ef. 4-25-71
340-234-0540 Board Products Industries (Veneer, Plywood, Particleboard, Hardboard): Testing and Monitoring All source tests must be done using the DEQ Source Sampling Manual. [NOTE: The DEQ Source Sampling Manual is published with OAR 340-200-0035.] (1) Veneer dryers, wood particle dryers, fiber dryers and press/cooling vents must be tested using DEQ Method 7. (2) Air conveying systems must be tested using DEQ Method 8. (3) Fuel burning equipment must be tested using DEQ Method 5. When combusting wood fuel by itself or in combination with any other fuel, the emission results are corrected to 12% CO2. When combusting fuels other than wood, the emission results are corrected to 50% excess air. [NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040.] Statutory/Other Authority: ORS 468.020, 468A.025 & 468A.070 Statutes/Other Implemented: 468A.025 & 468A.070 History: DEQ 13-2019, amend filed 05/16/2019, effective 05/16/2019 DEQ 7-2015, f. & cert. ef. 4-16-15
340-236-0005 Applicability and Jurisdiction (1) This division applies in all areas of the state. (2) Subject to the requirements in this division and OAR 340-200-0010(3), LRAPA is designated by the EQC to implement the rules in this division within its area of jurisdiction. NOTE: This rule is included in the State of Oregon Clean Air Act Implementation Plan that EQC adopted under OAR 340-200-0040. Statutory/Other Authority: ORS 468.020, 468A.025 & 468A.135 Statutes/Other Implemented: ORS 468A.025 & 468A.135 History: DEQ 7-2015, f. & cert. ef. 4-16-15