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North Central Coast Air Basin Attainment
South Central Coast Air Basin
San Luis Obispo and Santa Barbara Counties Unclassified
Ventura County Nonattainment
South Coast Air Basin Nonattainment
San Diego Air Basin Nonattainment
Northeast Plateau Air Basin Unclassified
Sacramento Valley Air Basin
Butte County Nonattainment
Placer, and Sacramento Counties Nonattainment
Remainder of Air Basin Unclassified
San Joaquin Valley Air Basin Nonattainment
Great Basin Valleys Air Basin Unclassified
Mojave Desert Air Basin
San Bernardino County
County Portion of federal Southeast Desert
Modified AQMA for Ozone 1 Nonattainment
Remainder of San Bernardino County and
Kern, Los Angeles, and Riverside
Counties Unclassified
Salton Sea Air Basin
Imperial County
City of Calexico 2 Nonattainment
Remainder of Imperial County and Riverside
County Unclassified
Mountain Counties Air Basin
Plumas County
Portola Valley 3 Nonattainment
Remainder of Plumas County and Amador,
Calaveras, El Dorado, Mariposa, Nevada,
Placer, Sierra, and Tuolumne Counties Unclassified
Lake County Air Basin Attainment
Lake Tahoe Air Basin Attainment
1 section 60200(b).
2 section 60200(a).
3 section 60200(c).
Note: Authority cited: Sections 39600, 39601 and 39608, Health and Safety Code. Reference: Section 39608, Health and Safety Code.
s 70100. Definitions.
(a) Ambient Air Quality Standards. Ambient air quality standards are specified concentrations and durations of air pollutants which reflect the relationship between the intensity and composition of pollution to undesirable effects.
(b) Most Relevant Effects. "Most Relevant Effects," shown in the Table of Ambient Air Quality Standards, are the effects which the standards are intended to prevent or abate.
(c) Parts Per Million (ppm). Parts per million is a volumetric unit of gas concentration, which is numerically equal to the volume of a gaseous contaminant present in one million volumes of air.
(d) Micrograms Per Cubic Meter (ug/m3). Micrograms per cubic meter is a unit of concentration which is numerically equal to the mass of a contaminant (in micrograms) present in a one cubic meter sample of air, measured at EPA reference conditions (corrected to 25 degrees Celsius, 760 torr). (40 CFR Part 50.3, November 25, 1971).
(e) Equivalent Method. "Equivalent Method" is any procedure for measuring the concentration of a contaminant, other than that specified in the air quality standard for the contaminant, which can be shown to the satisfaction of the Air Resources Board to give equivalent results at or near the level of the air quality standard.
(f) Visual Range. "Visual Range" is the distance at which a black object on the horizon has a 2 percent contrast with the horizon sky. This dis- tance can be calculated from a measured light extinction coefficient, Bext., by the formula: V r = 3.912 divided by Bext. = 3.912 divided by Bext.
(g) Carbon Monoxide (CO). Carbon Monoxide is a colorless gas, odorless under atmospheric conditions, having the molecular form CO.
(h) Sulfur Dioxide (SO 2). Sulfur dioxide is a colorless, irritating gas under atmospheric conditions, having the molecular form SO 2.
(i) Suspended Particulate Matter (PM10). Suspended particulate matter (PM10) refers to atmospheric particles, solid and liquid, except uncombined water as measured by a (PM10) sampler which collects 50 percent of all particles of 10 mm aerodynamic diameter and which collects a declining fraction of particles as their diameter increases and an increasing fraction of particles as their diameter decreases, reflecting the characteristics of lung deposition.
(j) Fine Suspended Particulate Matter (PM2.5). Fine suspended particulate matter (PM2.5) refers to suspended atmospheric particles solid and liquid, except uncombined water as measured by a PM2.5 sampler which collects 50 percent of all particles of 2.5 mm aerodynamic diameter and which collects a declining fraction of particles as their diameter increases and an increasing fraction of particles as their diameter decreases, reflecting the characteristics of lung deposition.
(k) Visibility Reducing Particles. Visibility reducing particles are atmospheric particles which significantly scatter or absorb light. The effect of these particles on light extinction is to be determined by instrumental monitoring of light scattering and absorption by ARB Method V, as adopted August 18, 1989, or by an equivalent method.
(l) Hydrogen Sulfide (H 2 S). Hydrogen sulfide is a colorless gas having the molecular form H 2 S.
(m) Nitrogen Dioxide (NO 2). Nitrogen dioxide is a red-brown gas, odorless under atmospheric conditions, having the molecular form NO 2.
(n) Lead (particulate). Lead (particulate) is suspended particulate matter containing lead (Pb).
(o) Sulfates. Sulfates are the water soluble fraction of suspended particulate matter (PM10) containing the sulfate ion (SO %L4 [FN2-]) including but not limited to strong acids and sulfate salts, as measured by MLD Method 007 (based on high-volume size-selective inlet (SSI) sampling and ion chromatography), dated January 19, 1988.%L) including but not limited to strong acids and sulfate salts, as measured by MLD Method 007 (based on high-volume size-selective inlet (SSI) sampling and ion chromatography), dated January 19, 1988.
(p) Vinyl Chloride. Vinyl chloride is a colorless gas with the molecular form CH 2 -CHCl; chloroethene.
(q) Ozone. Ozone is a colorless gas with a pungent odor, having the molecular form O 3.
(r) Extinction Coefficient. The "Extinction Coefficient" of a homogenous air mass is the natural logarithm of the fractional transmission of a beam of light per kilometer along the beam's path.
Note: Authority cited: Sections 39600, 39601 and 39606, Health and Safety Code. Reference: Sections 39602 and 39606, Health and Safety Code.
s 70100.1. Methods, Samplers, and Instruments for Measuring Pollutants.
(a) PM10 Methods. The method for determining compliance with the PM10 ambient air quality standard shall be the Federal Reference Method for the Determination of Particulate Matter as PM10 in the Atmosphere (40 CFR, Chapter 1, part 50, Appendix M, as published in 62 Fed. Reg., 38753, July 18, 1997). California Approved Samplers for PM10 are set forth in "Air Monitoring Quality Assurance Manual Volume IV, Part A: Monitoring Methods for PM10," adopted March 10, 2006, which is incorporated by reference herein. Samplers, methods, or instruments determined in writing by the Air Resources Board or the Executive Officer to produce equivalent results for PM10 shall also be California Approved Samplers for PM10. These include those continuous samplers that have been demonstrated to the satisfaction of the Air Resources Board to produce measurements equivalent to the Federal Reference Method.
(b) PM2.5 Methods. The method for determining compliance with the PM2.5 ambient air quality standard shall be the Federal Reference Method for the Determination of Particulate Matter as PM2.5 in the Atmosphere, 40 CFR, Chapter 1, part 50, Appendix L, as published in 62 Fed. Reg., 38714, July 18, 1997 and as amended in 64 Fed. Reg., 19717, April 22, 1999. The samplers listed in the Federal Reference Method must use either the WINS impactor or the U.S. EPA-approved very sharp cut cyclone (67 Fed. Reg., 15566, April 2, 2002) to separate PM2.5 from PM10. California Approved Samplers for PM2.5 are set forth in "Air Monitoring Quality Assurance Manual Volume IV, Part B: Monitoring Methods for PM2.5," adopted March 10, 2006, which is incorporated by reference herein. Samplers, methods, or instruments determined in writing by the Air Resources Board or the Executive Officer to produce equivalent results for PM2.5 shall also be California Approved Samplers for PM2.5. These include those continuous samplers that have been demonstrated to the satisfaction of the Air Resources Board to produce measurements equivalent to the Federal Reference Method.
(c) Ozone Methods. The method for determining compliance with the ozone ambient air quality standard shall be the Federal Equivalent Method for the Determination of Ozone in the Atmosphere (40 CFR, part 53). California Approved Samplers for ozone are set forth in "Air Monitoring Quality Assurance Manual Volume IV, Part C: Monitoring Methods for Ozone", as adopted March 10, 2006. Samplers, methods, or instruments determined in writing by the Air Resources Board or the Executive Officer to produce equivalent results for ozone shall also be California Approved Samplers for ozone.
Note: Authority cited: Sections 39600, 39601 and 39606, Health and Safety Code. Reference: Sections 39014, 39606, 39701 and 39703(f), Health and Safety Code.
s 70101. General Statement of Policy and Scope.
The objective of ambient air quality standards is to provide a basis for preventing or abating the effects of air pollution, including effects on health, esthetics and economy. The standards should not be interpreted as permitting, encouraging, or condoning degradation of present air quality in any air basin which now has an air quality superior to that stipulated in the standards. Pollution levels below those shown in the standards should not ordinarily produce the associated effects.
In determining compliance with the standards through air monitoring, the sites and conditions of air sampling should be so chosen as to realistically represent the exposures of people, animals, vegetation and materials.
Ambient air quality standards shall be reviewed and subject to modification whenever substantial pertinent new information becomes available and at least once every five years. To the extent feasible, review of a standard shall be coordinated with the review of any corresponding federal standard by the Environmental Protection Agency.
Note: Authority cited: Sections 39600 and 39601(a), Health and Safety Code. Reference: Sections 39602 and 39606(b), Health and Safety Code.
s 70200. Table of Standards ***
_____________
*The list of California Approved Samplers may be obtained from the Air Resources Board, Monitoring and Laboratory Division, P.O. Box 2815, Sacramento, CA 95814. Any equivalent procedure which can be shown to the satisfaction of the Air Resources Board to give equivalent results at or near the level of the air quality standard may be used.
**These standards are violated when concentrations exceed those set forth in the body of the regulation. All other standards are violated when concentrations equal or exceed those set forth in the body of the regulation.
***Applicable statewide unless otherwise noted.
****These standards are violated when particle concentrations cause measured light extinction values to exceed those set forth in the regulations.
Note: Authority cited: Sections 39600, 39601(a) and 39606, Health and Safety Code. Reference: Sections 39014, 39606, 39701 and 39703(f), Health and Safety Code; andWestern Oil and Gas Ass'n v. Air Resources Bd. (1984) 37 Cal.3d 502.
s 70200.5. Ambient Air Quality Standards for Hazardous Substances [FNa1]
-------------------------------------------------------------------------------
-------------------------------------------------------------------------------
Concentration Duration
of
and Averaging Most
Relevant
Substance Methods Periods Effects Comments
-------------------------------------------------------------------------------
Vinyl Chloride 0.010 ppm ARB
(Chloroethene Haagan-Smit 24 hours Known Low-level effects are
human undefined, but are
CH2=CHC1 Lab Method and aminal potentally serious.
car- Level is not a
thresh-
No. 101 cinogen old level and does not
necessarily pro-
(Tedlar Bag tect against harm.
Level specified is
collection gas lowest level at which
violation can be
chromatogra- reliably detected by
the method speci-
phy) fied. Ambient
concentrations at or
above the standard
constitute an
endangerment to the
health of the public.
-------------------------------------------------------------------------------
[FNa1] Applicable statewide unless otherwise noted.
Note: Authority cited: Sections 39600, 39601(a) and 39606(b), Health and Safety Code. Reference: Section 41700, Health and Safety Code.
s 70201. Determination of 24-Hour SO 2 Standard.
Note: Authority cited: Section 39601, Health and Safety Code. Reference: Section 39606, Health and Safety Code.
s 70300. General Statement of Purpose.
The objective of these criteria is to guide the state board in making designations of areas as attainment, nonattainment, nonattainment-transitional, or unclassified for each of the pollutants for which state ambient air quality standards have been established in Section 70200.
Note: Authority cited: Sections 39600, 39601, 39607, 39608 and 40925.5, Health and Safety Code. Reference: Sections 39607, 39608 and 40925.5, Health and Safety Code.
s 70301. Air Quality Data Used for Designations.
(a) Except as otherwise provided in this article, designations shall be based on "data for record. "
(1) Data for record are those data collected by or under the auspices of the state board or the districts for the purpose of measuring ambient air quality, and which the executive officer has determined comply with the siting and quality assurance procedures established in Part 58, Title 40, Code of Federal Regulations, as they existed on July 1, 1987, or other equivalent procedures.
(2) Any other data which are provided by a district or by any other person will be data for record if the executive officer determines within 90 days of submittal of complete supporting documentation that the data comply with the siting and quality assurance procedures established in Part 58, Title 40, Code of Federal Regulations, as they existed on July 1, 1987, or other equivalent procedures. If the executive officer finds there is good cause that 90 days is insufficient time to make a determination, he/she may after notification of the person requesting the data review extend the deadline for completion for the data review.
(b) Except as otherwise provided in this article, designations and reviews of designations will be based on data for record for the three calendar years prior to the year in which the designation is made or the annual review of the designation is conducted.
(c) Data as described in section 70301(a)(1) and (2) become data for record upon completion of the executive officer's review.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code: Reference: Sections 39607 and 39608, Health and Safety Code.
s 70302. Geographic Extent of Designations.
(a) An air basin will be the area designated for ozone, nitrogen dioxide, suspended particulate matter (PM10), fine suspended particulate matter (PM2.5), sulfates, and visibility reducing particles. Provided, however, if the state board finds (based on air quality data, meteorology, topography, or the distribution of population and emissions) that there are areas within an air basin with distinctly different air quality deriving from sources and conditions not affecting the entire air basin, the state board may designate an area smaller than an air basin using political boundary lines to the extent practicable. In designating an area smaller than an air basin as nonattainment, the state board will include within the area those sources whose emissions contribute to a violation of a state standard for that pollutant. Contiguous areas which would have the same designation within an air basin will be one designated area.
(b) A county or the portion of a county which is located within an air basin will be the area designated for carbon monoxide, sulfur dioxide, lead (particulate), and hydrogen sulfide. Provided, however, if the state board finds (based on air quality data, meteorology, topography, or the distribution of population and emissions) that there are areas within the county with distinctly different air quality, it may designate a smaller area. In designating an area smaller than a county as nonattainment, the state board will include within the area those sources whose emissions contribute to a violation of a state standard for that pollutant.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
s 70303. Criteria for Designating an Area as Nonattainment.
(a) The state board will designate an area as nonattainment for a pollutant if:
(1) Data for record show at least one violation of a state standard for that pollutant in the area, and the measurement of the violation meets the representativeness criteria set forth in "Criteria for Determining Data Representativeness" contained in Appendix 1 to this article; or
(2) Limited or no air quality data were collected in the area, but the state board finds, based on meteorology,topography, and air quality data for an adjacent nonattainment area, that there has been at least one violation of a state standard for that pollutant in the area being designated.
(b) An area will not be designated as nonattainment if the only recorded exceedance(s) of that state standard were based solely on data for record determined to be affected by a highly irregular or infrequent event. Data affected by a highly irregular or infrequent event will be identified as such by the executive officer in accordance with the "Air Resources Board Procedure for Reviewing Air Quality Data Possibly Affected by a Highly Irregular or Infrequent Event," set forth in Appendix 2 to this article.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
s 70303.1. Criteria for Designating an Area as Nonattainment-Transitional for Pollutants Other than Ozone.
(a) Nonattainment-transitional is a subcategory of the nonattainment designation. The state board will, if requested by a district no later than May 1 of each year pursuant to section 70306, identify that portion of a designated area within the district as nonattainment-transitional for a pollutant other than ozone with a state standard averaging time less than or equal to 24 hours and for which samples are routinely collected every day if it finds that:
(1) Data for record for the previous calendar year are consistent with the criteria established in section 70304(a)(2) and show two or fewer days at each site in the area with violations of a state standard for that pollutant (not including exceedances found to be affected by a highly irregular or infrequent event under the procedure set forth in Appendix 2 to this article);
(2) Evaluation of multi-year air quality, meteorological and emission data indicates that ambient air quality either has stabilized or is improving and that every site in the area is expected to reach attainment within three years; and
(3) The geographic extent of the area is consistent with the criteria established in section 70302.
(b) An area designated as nonattainment-transitional for a pollutant is close to attaining the state standard(s) for that pollutant. The nonattainment-transitional designation provides an opportunity for a district to review and potentially to modify its attainment plan. Any modification to an attainment plan must be consistent with state and federal regulations and statutes.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
s 70303.5. Requirements for Ozone Nonattainment-Transitional
(a) If an area within an air basin is designated as nonattainment for ozone, that area is designated as nonattainment-transitional for ozone if the following conditions are met:
(1) The area is an entire district within an air basin, or the area is the entire portion of a district within an air basin consistent with the criteria established in section 70302(a);
(2) Data for record consistent with the criteria established in section 70304(a)(2) are used to determine the number of exceedances for the previous calendar year at each monitoring location in the area;
(3) All data collected during the previous calendar year are considered in the evaluation, including data possibly affected by a highly irregular or infrequent event under the procedure set forth in Appendix 2 to this article;
(4) Each day with concentration(s) that exceed the state ozone standard is counted as one exceedance day; and
(5) No monitoring location in the area has more than three exceedance days during the previous calendar year.
(b) If an area qualifies for designation as nonattainment-transitional for ozone for the previous calendar year under section 70303.5(a), and the executive officer has determined that data for the current calendar year indicate more than three exceedance days at any one monitoring location, that area is designated as nonattainment.
Note: Authority Cited: Sections 39600, 39601, 39607 and 40925.5, Health and Safety Code. Reference: Sections 39607 and 40925.5, Health and Safety Code.
s 70304. Criteria for Designating an Area as Attainment.
(a) The state board will designate an area as attainment for a pollutant if:
(1) Data for record show that no state standard for that pollutant was violated at any site in the area; and
(2) Data for record meet representativeness and completeness criteria for a location at which the pollutant concentrations are expected to be high based on the spatial distribution of emission sources in the area and the relationship of emissions to air quality. Data representativeness criteria are set forth in "Criteria for Determining Data Representativeness" contained in Appendix 1 to this article. Data completeness criteria are set forth in "Criteria for Determining Data Completeness" contained in Appendix 3 to this article.
(b) Where there are limited or no air quality data for an area, the state board will designate the area as attainment for a pollutant it finds that no state standard for that pollutant has been violated in that area based on:
(1) Air quality data collected in the area during the most recent period since 1980 which meet the conditions in (a) above;
(2) Emissions of that pollutant or its precursors in the area have not increased since that period to a level at which the state standard might be exceeded; and
(3) Air quality data collected in the area since the time period in (1) above do not show a violation of the state standard.
(c) Where an area has limited or no air quality data for nitrogen dioxide, sulfur dioxide, sulfates, and lead (particulate), the state board shall designate that area attainment for a pollutant if it finds that no state standard for that pollutant has been violated in that area based on the "Screening Procedure for Determining Attainment Designations for Areas with Incomplete Air Quality Data" set forth in Appendix 4 to this article.
(d) A nonattainment area will not be redesignated as attainment for a pollutant if;
(1) Data for record for the monitoring site showing the greatest violation of a state standard for that pollutant no longer are available; and
(2) No other site has been identified as equivalent by the executive officer.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
s 70306. Annual Review of Designations.
(a) The executive officer will conduct annual reviews of all designations and will propose revisions to the designations as necessary to the state board. The executive officer will complete the annual reviews by November 15.
(b) Any request for a change in a designation and any submittal of information for purposes of the executive officer's consideration in the annual review of a designation shall be provided in writing to the executive officer no later than May 1 of each year.
Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
Appendix 1
Criteria for Determining Data Representativeness
This Appendix describes the criteria to be used in determining the representativeness of individual air quality measurements and statistics for the purpose of designating areas as described in this article. Data representativeness, as that term is used herein, relates to the determination of whether the amount of data reflected in an individual air quality measurement or statistic is sufficient to characterize reliably air quality during the respective averaging time of a state standard. The criteria for determining data representativeness are summarized in the accompanying table and discussed further, below.
Air quality measurements and statistics are usually computed from short term observed values. If all the short term values for the statistical time period are available, the calculated statistic is representative. However, because all the short term values for a given period often are not available, a minimum number of observations are needed to provide reasonable assurance that the calculated measurement or statistic is a reliable estimate for the averaging time specified in the state standard.
In general, air quality measurements and statistics are considered representative if a minimum of 75 percent of all the potential short term values are included and are distributed throughout the entire statistical time period. This 75 percent criteria must be met from the averaging time of the initial measurement, up to and including, the final averaging time reflected by the air quality measurement or statistic. For example, a maximum daily statistic must meet the representativeness criteria specified for a "Day." Because a daily statistic reflects a single day, it does not need to meet the representativeness criteria for any other level (Month, Quarter, or Year). In evaluating data representativeness, all measurements are considered, including those identified as affected by a highly irregular or infrequent event under the "Air Resources Board Procedure for Reviewing Air Quality Data Possibly Affected by a Highly Irregular or Infrequent Event," set forth in Appendix 2 to this article.
Individual air quality measurements and statistics used for designating an area as attainment, nonattainment-transitional, or nonattainment must be representative. Furthermore, to ensure that the group of air quality measurements or statistics used for designating an area as attainment or nonattainment-transitional reflect the time of day and the season of expected high concentrations, these data must also be complete under the "Criteria for Determining Data Completeness" set forth in Appendix 3 to this article. In contrast, the air quality measurements or statistics used for designating an area as nonattainment are not required to be complete.
Criteria for Representativeness of Air Quality Measurements and Statistics
Appendix 2
Air Resources Board Procedure for Reviewing Air Quality Data Possibly Affected
by a Highly Irregular or Infrequent Event
This Appendix describes the procedures that the Air Resources Board will use for reviewing air quality data possibly affected by a highly irregular or infrequent event with regard to the state ambient air quality standards. All decisions regarding the identification of data as being affected by a highly irregular or infrequent event will be made by the executive officer.
The executive officer will review air quality data for possible identification as affected by a highly irregular or infrequent event if the data are the only exceedances of a state ambient air quality standard in the area or if such identification would otherwise affect the designation of the area.
Three types of highly irregular or infrequent events may be identified:
1. Extreme Concentration Event
2. Exceptional Event
3. Unusual Concentration Event.
Extreme Concentration Events
An extreme concentration event is an event beyond reasonable regulatory control which causes an exceedance of a state standard. An extreme concentration event is based on a statistical procedure and may not always be linked to a specific identifiable cause. The causes of an extreme concentration event include but are not limited to unusual meteorology.
The steps for identifying an extreme concentration event are:
1. A district (or the executive officer) identifies questionable data.
2. In evaluating a possible extreme concentration event, the executive officer will use the data for the site at which the event is suspected to determine a limit for concentrations expected to recur no more frequently than once in one year. The limit will be determined using the "exponential tail method" described in Procedure for Computing the Values Used in Identifying Extreme Concentration Events (August 1998), which is incorporated by reference herein. Using conventional rounding procedures, the limit will be consistent with the level of precision in which the state standard is expressed. If the possible extreme concentration exceeds the concentration expected to recur no more frequently than once in one year, the executive officer will consult with the district in identifying the data as affected by an extreme concentration event.
3. When an extreme concentration event is identified, the executive officer will review other information, including but not limited to meteorological data, to determine whether air quality data for other sites in the area were affected by the extreme concentration event.
Exceptional Events
An exceptional event is an event beyond reasonable regulatory control which causes an exceedance of a state standard. An exceptional event must be linked to a specific cause such as an act of nature or unusual human activity. As guidance to the states for determining exceptional events, the federal Environmental Protection Agency (EPA) has published Guideline on the Identification and Use of Air Quality Data Affected by Exceptional Events,(EPA-450/4-86-007), July 1986 (the EPA Guideline). The EPA Guideline provides overall criteria for determining whether an event is exceptional with regard to the national standards. The executive officer will use the EPA Guideline as a general basis for reviewing ambient data, but will notbe bound by the specific definitions in the EPA Guideline for the various types of exceptional events because those definitions are made on a national basis. In addition, since what may be exceptional in one part of the state may be common in another, each possible event will be evaluated on a case-by-case basis.
The steps for identifying an exceptional event are:
1. A district (or the executive officer) identifies questionable data.
2. If a known exceptional event has occurred, the district gathers relevant data to document the occurrence.
3. If an exceptional event is only suspected, the district investigates available data for the possible event.
4. The district submits to the executive officer a request for identifying the data as affected by an exceptional event and also provides supporting documentation.
5. If the executive officer concurs with the district, he/she will identify the data as affected by an exceptional event.
6. If the district's request for identifying data as affected by an exceptional event cannot be supported, the district will be notified of the reasons. The executive officer will consider any additional data to support the request, but in the absence of any new evidence, will disapprove the request.
Unusual Concentration Events
An unusual concentration event is an event which causes an anomalous exceedance of a state standard and which does not qualify as an extreme concentration event or an exceptional event. An exceedance affected by an unusual concentration event may be identified only for an area designated as attainment or unclassified at the time of the exceedance.
The steps for identifying an unusual concentration event are:
1. A district (or the executive officer) identifies a questionable exceedance(s).
2. If the exceedance(s) has not been identified as having been affected by an extreme concentration event or an exceptional event, and if the area was designated as attainment or unclassified at the time of the exceedance(s), the executive officer will review the exceedance(s) to determine whether it was affected by an unusual concentration event.
3. In evaluating a possible unusual concentration event, the executive officer will consider all relevant information, including but not limited to the amount and characteristics of air quality data, emission data, meteorological data, potential public health and welfare impacts, and any applicable state, district, and federal rules and regulations. To identify the exceedance(s) as affected by an unusual concentration event, the executive officer must find, based on the relevant information, that the impact of the exceedance(s) is limited to the local area, the exceedance(s) is not expected to recur, and that the data do not support a nonattainment designation.
4. If the exceedance(s) qualifies as possibly affected by an unusual concentration event, the executive officer will consult with the district in identifying the exceedance(s) as affected by an unusual concentration event.
5. An area may retain its attainment or unclassified designation based on the identification and exclusion of an exceedance(s) affected by an unusual concentration event for no more than three consecutive years. If the executive officer identifies an exceedance(s) affected by an unusual concentration event in the area in the fourth consecutive year, the area will be redesignated as nonattainment. Note: Authority cited: Sections 39600, 39601, 39607 and 39608, Health and Safety Code. Reference: Sections 39607 and 39608, Health and Safety Code.
Appendix 3
Criteria for Determining Data Completeness
This Appendix describes the criteria to be used in determining data completeness for the purpose of designating areas as described in this article. These Criteria for Determining Data Completeness (Completeness Criteria) apply only to air quality data used in designating an area as attainment or nonattainment-transitional. Air quality data used in designating an area as nonattainment do not need to be complete. The purpose of these Completeness Criteria is to specify the minimum amount of data deemed necessary to ensure that sampling occurred at times when a violation is most likely to occur.
After a set or group of air quality measurements or statistics are deemed representative under the Criteria for Determining Data Representativeness set forth in Appendix 1 to this article, they are then evaluated under these Completeness Criteria to ensure that the group of representative measurements or statistics reflect the time of day and the season of the year during which high concentrations are likely to occur.
Complete Data
Data for a site will be complete if there are representative data (as determined in accordance with the Representativeness Criteria in Appendix 1 to this article) during the required hours (see below) of the day during the required months (see below) for the required years (see below).
Required Hours
The hours of potentially high concentration must be included. Unless a detailed evaluation determines different hours to be appropriate for a specific site, these hours are:
Pollutant Hours (PST)
Ozone 9 am-5 pm
Carbon Monoxide 3 pm-9 am (next day)
Nitrogen Dioxide 8 am-8 pm
Visibility Reducing Particles 10 am-6 pm
Other Pollutants Throughout day
Required Months
The months of potentially high concentrations must be included. Unless a detailed evaluation determines different months to be appropriate for a specific site, these months are:
Pollutant Months
Ozone July-September
Carbon Monoxide January, November-December
Nitrogen Dioxide October-December
Sulfur Dioxide September-December
Sulfates January, June-December
Lead (Particulate) January, November-December
Other Pollutants January-December
Required Years for an Attainment Designation
The number of years to be included for an attainment designation is:
(a) Three; or
(b) Two, if during these years the maximum pollutant concentration (not including data found to be affected by a highly irregular or infrequent event under the procedure set forth in Appendix 2 to this article) is less then three-fourths the applicable state ambient air quality standard; or
(c) One, if during this year the maximum pollutant concentration (not including data found to be affected by a highly irregular or infrequent event under the procedure set forth in Appendix 2 to this article) is less than one-half the applicable state ambient air quality standard.
Appendix 4
Screening Procedure for Determining Attainment Designations for Areas with
Incomplete Air Quality Data
This Appendix describes the screening procedure that will serve as the basis for making a pollutant-specific finding under Section 70304(c) that the state ambient air quality standard is being attained for areas with no or an incomplete air quality data record. The procedure is applicable only for nitrogen dioxide, sulfur dioxide, sulfates, and lead (particulate). For those areas with some air quality data for the prior three years, the screening procedure will be applied for a pollutant only if the maximum concentrations of that pollutant in the area did not exceed 75 percent of the state standard(s).
Pollutant Screening Parameters Screening Values
Nitrogen Dioxide (a) Basin Population 1,000,000 people
(b) Total Annual NO x Emissions 40,000 tons/yr
in Air Basin
(c) Total Annual Point Source 2,100 tons/yr
NO x Emissions in County
Sulfur Dioxide (a) Total Annual Point Source SO x 1,700 tons/yr
Emissions in County
(b) Maximum Annual SO x Emissions 900 tons/yr
from Single Facility in County
Sulfates (a) Total Annual SO x Emissions in 19,000 tons/yr
Air Basin
(b) Total Annual Point Source SO x 1,700 tons/yr
Emissions in County
(c) Maximum Annual SO x Emissions 900 tons/yr
from Single Facility in County
Lead (a) County Population 600,000 people
(b) Maximum Annual Lead 0.5 tons/yr
Emissions from Single Facility in
County
For an area to which these values are applied, the local values of the applicable screening parameters will be compared to the respective screening values. The area will be presumed to be attainment if none of the applicable screening parameters for a pollutant exceed the associated screening values.
s 70500. Transport Identification.
(a) Purpose.
This regulation identifies the areas in which transported air pollutants from upwind areas cause or contribute to a violation of the state ambient air quality standard for ozone and the areas of origin of the transported pollutants. All areas identified in the table are air basins except as otherwise specifically described and defined.
(b) Definitions.
(1) "California Coastal Waters" includes the area between the California coastline and a line starting at the California-Oregon border at the Pacific Ocean; thence to 42.0 degrees North, 125.5 degrees West; thence to 41.0 degrees North, 125.5 degrees West; thence to 40.0 degrees North, 125.5 degrees West; thence to 39.0 degrees North, 125.0 degrees West; thence to 38.0 degrees North, 124.5 degrees West; thence to 37.0 degrees North, 123.5 degrees West; thence to 36.0 degrees North, 122.5 degrees West; thence to 35.0 degrees North, 121.5 degrees West; thence to 34.0 degrees North, 120.5 degrees West; thence to 33.0 degrees North, 119.5 degrees West; thence to 32.5 degrees North, 118.5 degrees West; and ending at the California-Mexican border at the Pacific Ocean.
(2) "Upper Sacramento Valley" includes the Colusa, Butte, Glenn, Tehama, and Shasta County Air Pollution Control Districts, and that area of the Feather River Air Quality Management District, which is north of a line connecting the northern border of Yolo County to the southwestern tip of Yuba County, and continuing along the southern Yuba County border to Placer County.
(3) "Broader Sacramento Area" includes the Sacramento Metropolitan Air Quality Management District; the Yolo-Solano Air Pollution Control District; the portions of the El Dorado County Air Pollution Control District included in 1990 U.S. Census Tracts 306.01, 307, 308.01, 308.02, 308.03, 308.04, 309.01, 309.02, 310, 311, 312, 315.01, and 315.02; and the portions of the Placer County Air Pollution Control District included in 1990 U.S. Census Tracts 203, 204, 205, 206.01, 206.02, 206.03, 207.01, 207.02, 207.03, 208, 209, 210.01, 210.02, 211.01, 211.02, 212, 213.01, 213.02, 214, 215.01, 215.02, 216, 218.01, and 218.02; and that area of the Feather River Air Quality Management District which is south of a line connecting the northern border of Yolo County to the southwestern tip of Yuba County, and continuing along the southern Yuba County border to Placer County.
(c) Transport Identification Table
OZONE IMPACTED
BY TRANSPORT: AREAS OF ORIGIN OF TRANSPORT:
1. North Central Coast San Francisco Bay Area
San Joaquin Valley
2. South Central Coast South Coast
California Coastal Waters
San Joaquin Valley
San Francisco Bay Area
3. South Coast South Central Coast
4. San Diego South Coast
Mexico
5. Upper Sacramento Valley Broader Sacramento Area
6. Broader Sacramento Area San Francisco Bay Area
San Joaquin Valley
7. San Joaquin Valley San Francisco Bay Area
Broader Sacramento Area
8. Great Basin Valleys San Joaquin Valley
9. Southeast Desert South Coast
San Joaquin Valley
Mexico
10. San Francisco Bay Area Broader Sacramento Area
11. Mountain Counties Broader Sacramento Area
San Joaquin Valley
San Francisco Bay Area
12. Salton Sea South Coast
Mexico
13. North Coast San Francisco Bay Area
Note: Authority cited: Sections 39600, 39601 and 39610(a), Health and Safety Code. Reference: Section 39610(a), Health and Safety Code.
s 70600. Emission Control Requirements.
(a) Definitions
For the purpose of sections 70600 and 70601, the following definitions shall apply:
(1) "all feasible measures" means air pollution control measures, including but not limited to emissions standards and limitations, applicable to all air pollution source categories under a district's authority that are based on the maximum degree of reductions achievable for emissions of ozone precursors, taking into account technological, social, environmental, energy and economic factors, including cost-effectiveness.
(2) "ozone precursors" means oxides of nitrogen and reactive organic gases.
(b) Specific Requirements
Districts within the areas of origin of transported air pollutants, as identified in section 70500(c), shall include sufficient emission control measures in their attainment plans for ozone adopted pursuant to part 3, chapter 10 (commencing with section 40910) of division 26 of the Health and Safety Code, to mitigate the impact of pollution sources within their jurisdictions on ozone concentrations in downwind areas commensurate with the level of contribution. An upwind district shall comply with the transport mitigation planning and implementation requirements set forth in this section regardless of its attainment status, unless the upwind district complies with the requirements of section 70601. At a minimum, the attainment/transport mitigation plans for districts within the air basins or areas specified below shall conform to the following requirements:
(1) Broader Sacramento Area (as defined in section 70500(b)(3)) shall:
(A) require the adoption and implementation of all feasible measures as expeditiously as practicable.
(B) require the adoption and implementation of best available retrofit control technology, as defined in Health and Safety Code section 40406, on all existing stationary sources of ozone precursor emissions as expeditiously as practicable.
(C) require the implementation, by December 31, 2004, of a stationary source permitting program designed to achieve no net increase in the emissions of ozone precursors from new or modified stationary sources that emit or have the potential to emit 10 tons or greater per year of an ozone precursor.
(D) include measures sufficient to attain the state ambient air quality standard for ozone by the earliest practicable date within the Upper Sacramento Valley and that portion of the Mountain Counties Air Basin north of the Calaveras-Tuolumne County border and south of the Sierra-Plumas County border, except as provided in Health and Safety Code section 41503(d), during air pollution episodes which the state board has determined meet the following conditions:
(i) are likely to produce a violation of the state ozone standard in the Upper Sacramento Valley or that portion of the Mountain Counties Air Basin north of the Calaveras-Tuolumne County border and south of the Sierra-Plumas County border;
(ii) are dominated by overwhelming pollutant transport from the Broader Sacramento Area; and
(iii) are not measurably affected by emissions of ozone precursors from sources located within the Upper Sacramento Valley or that portion of the Mountain Counties Air Basin north of the Calaveras-Tuolumne County border and south of the Sierra-Plumas County border.
(2) San Francisco Bay Area Air Basin shall:
(A) require the adoption and implementation of all feasible measures as expeditiously as practicable.
(B) require the adoption and implementation of best available retrofit control technology, as defined in Health and Safety Code section 40406, on all existing stationary sources of ozone precursor emissions as expeditiously as practicable.
(C) require the implementation, by December 31, 2004, of a stationary source permitting program designed to achieve no net increase in the emissions of ozone precursors from new or modified stationary sources that emit or have the potential to emit 10 tons or greater per year of an ozone precursor.
(D) include measures sufficient to attain the state ambient air quality standard for ozone by the earliest practicable date within the North Central Coast Air Basin, that portion of Solano County within the Broader Sacramento Area, that portion of Sonoma County within the North Coast Air Basin, and that portion of Stanislaus County west of Highway 33, except as provided in Health and Safety Code section 41503(d), during air pollution episodes which the state board has determined meet the following conditions:
(i) are likely to produce a violation of the state ozone standard in the North Central Coast Air Basin, or that portion of Solano County within the Broader Sacramento Area, or that portion of Sonoma County within the North Coast Air Basin, or that portion of Stanislaus County west of Highway 33;
(ii) are dominated by overwhelming pollutant transport from the San Francisco Bay Area Air Basin; and
(iii) are not measurably affected by emissions of ozone precursors from sources located within the North Central Coast Air Basin, or that portion of Solano County within the Broader Sacramento Area, or that portion of Sonoma County within the North Coast Air Basin, or that portion of Stanislaus County west of Highway 33.
(3) San Joaquin Valley Air Basin shall:
(A) require the adoption and implementation of all feasible measures as expeditiously as practicable.
(B) require the adoption and implementation of best available retrofit control technology, as defined in Health and Safety Code section 40406, on all existing stationary sources of ozone precursor emissions as expeditiously as practicable.
(C) include measures sufficient to attain the state ambient air quality standard for ozone by the earliest practicable date within the Mojave Desert Air Basin, the Great Basin Valleys Air Basin, and that portion of the Mountain Counties Air Basin south of the Amador-El Dorado County border, except as provided in Health and Safety Code section 41503(d), during air pollution episodes which the state board has determined meet the following conditions:
(i) are likely to produce a violation of the state ozone standard in the Mojave Desert Air Basin orthe Great Basin Valleys Air Basin, or that portion of the Mountain Counties Air Basin south of the Amador-El Dorado County border; (continued)