
ARB Ag Advisory Committee
for Air Quality
CAPCOA Agricultural Sources
Clearinghouse
SB 700 TABLE OF CONTENTS
Introduction
I. Defining "Agricultural Source"
a. Confined Animal Facilities
b. Internal Combustion Engines
c. Sources Subject to Title V
1) Potential to Emit
2) Point vs. Fugitive Emissions
3) Contiguous Property
4) Common Ownership or Control
d. Sources Otherwise Subject to Regulation by Air Districts
II. Removing the Permit Exemption
III. Establishing Specific Permitting & Exemption Requirements
a. Sources Subject to Federal Permitting Requirements
1) New Source Review
i. Best Available Control Technology (BACT)
ii. Emission Reduction Credits (ERCs) and Offset Requirements
2) Title V
b. Sources Whose Actual Emissions Equal or Exceed 50% of the Major Source
Threshold
1) Calculating "actual" emissions for the threshold
2) How existing agricultural sources are affected
3) How new agricultural sources are affected
4) How existing prohibitory rules may apply
5) The findings a district board must make to exempt larger sources
c. Sources Whose Actual Emissions are Less than 50% of the Major Source
Threshold
1) How existing agricultural sources are affected
2) How new agricultural sources are affected
3) How existing prohibitory rules may apply
4) The findings a district board must make to permit smaller sources
d. Sources Whose Emissions are de minimis
e. Sources that Implement all Listed Mitigations
f. Summary and Timing
IV. Emission Control in Federal Nonattainment Areas for PM10
a. Serious PM Nonattainment Areas
b. Moderate PM Nonattainment Areas
c. Best Available Control Measures (BACM)
d. Best Available Retrofit Control Technology (BARCT)
e. Precursor Emissions
f. Procedures for Regulating Engines
V. Permits & Emissions Mitigation for "Large" CAFs
a. Defining "Large" CAF
b. Permit Requirements and Schedule for "Large" CAFs
c. Emissions Mitigation for "Large" CAFs
d. Procedures to Assess Other Impacts of Rulemaking
e. Areas that Attain the federal Ozone Standard
VI. Mitigation Clearinghouse
Appendices
Appendix A
- Text of Senate Bill 700
Appendix B
- Flow Diagrams of SB 700 Requirements
B-1
All "Agricultural Sources" [Adobe pdf file]
B-2
Confined Animal Facilities (CAFs) [Adobe pdf file]
Appendix C
- Air District Attainment Designations & Thresholds
Appendix D
- Maps of Air District & Air Basin Boundaries
D-1
Map of Air Districts [Adobe pdf file]
D-2
Map of Air Basins [Adobe pdf file]
Appendix E
- Glossary of Terms
Appendix F
- Summary of Rule Development Requirements for Air Districts

Senate Bill 700 (Florez): Agriculture &
Air Quality
Summary & Implementation
Introduction
On September 22, 2003, Governor Davis signed into law Senate Bill 700,
authored by Senator Florez. The bill amended air pollution control requirements
in the California Health and Safety Code to include requirements for
agricultural sources of air pollution.
Agricultural sources of air pollution were the focus of the bill for two main
reasons. First, California law had previously exempted these sources from
requirements to obtain air permits. This resulted in a conflict between state
and federal law, and California faced sanctions if it failed [to] correct the
problem. Had the bill not been signed, new and expanding businesses in the state
would have faced significant and costly hurdles to obtain air permits required
under federal law, and the state would have lost billions of dollars in federal
transportation funding.
There was another reason for the bill to focus on air pollution resulting
from agricultural activities, however. In some parts of the state, air quality
is very bad and agricultural activities are significant contributors to the
problem. Poor air quality harms public health; it causes and/or exacerbates
asthma, respiratory illnesses, heart and lung disease, and early mortality.
Children and the elderly are especially vulnerable. Parts of California, such as
the San Joaquin Valley and the South Coast, have some of the highest asthma
rates in the nation. Senate Bill 700 was intended to address the agricultural
contribution to these problems while recognizing that the problems are not the
same, nor is the contribution of agricultural sources, in all the regions of the
state. [Back to
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The bill does six main things: (1) It defines "agricultural source" in
state law; (2) It removes the restriction from state law that prevented
air districts from requiring permits for agricultural sources; (3) It
establishes specific permitting and exemption requirements for agricultural
sources; (4) It requires emission control regulations in areas that do
not attain National Ambient Air Quality Standards for PM10; (5) It
requires permits and emissions mitigation for Confined Animal Facilities (CAFs)
that are defined by ARB as "large" (based on a review of current scientific data
about emissions from CAFs and the impact of those emissions on attainment of
ambient air standards); and (6) It requires CAPCOA to compile a
clearinghouse of information about available emissions control and mitigation
for agricultural activities. It is important to note that the bill did not
remove the exemption for agricultural operations from the general odor-nuisance
provisions of the Health and Safety Code.
What follows is a summary of the requirements of SB 700 in each of these six
areas, including a discussion of how the air districts (and in some cases ARB)
interpret these requirements, and how we believe they can be implemented. A copy
of SB 700 is included in Appendix A. Appendix B provides flow diagrams of the
requirements of the bill.
[Back to TOC]
I. Defining "agricultural source"
The bill generally defines "agricultural source" as a source, or group of
sources, used in the production of crops or the raising of fowl or animals
located on contiguous property and under common ownership or control. The bill
specifically lists four categories of emissions sources that are part of the
agricultural source: (a) Confined Animal Facilities; (b) internal combustion
engines, including portable and off-road engines; (c) sources subject to
requirements under Title V of the 1990 Amendments to the Federal Clean Air Act;
and (d) sources of emissions that are otherwise subject to district regulation
under the Health & Safety Code or the federal Clean Air Act.
a) Confined Animal Facilities (CAFs)
The bill defines "confined animal facility" to include essentially any type
of confinement for animals or fowl that restricts them to a specific area, and
involves feeding the animals by any method other than grazing. This
specifically includes barns, pens, corrals, and coops, but should be
interpreted broadly. The definition also specifically lists other markers of
CAFs, including feed storage, milking parlors, and systems to collect, store,
treat, and distribute liquid or solid manure from the confined animals.
b) Internal Combustion Engines
The bill includes in the "agricultural source" any internal combustion
engine that is used in the production of crops or the raising of animals or
fowl. It specifically includes portable engines and offroad engines, unless
the engines are "used to propel implements of husbandry." That means these
engines are specifically subject to the air permit requirements of the bill
(see Item #3, below, for further explanation of these requirements).
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The ARB currently implements a registration program for portable equipment
and engines that opt to register in the state program are relieved of the
obligation to obtain local permits. The ARB registration program currently
excludes agricultural engines by regulation. In order to open the program to
agricultural engines, ARB would have to amend its rule, which would, among
other things, require a finding that the engines would be subject to the same
degree of emissions control as required under local permit programs, including
the requirements of SB 700. Such a finding would have to be made at a public
hearing.
ARB staff and CAPCOA further believe that before an agricultural engine
could be registered with the state, the district in which that engine resides
would have to take formal action allowing state registration in lieu of local
permits.
c) Sources subject to Title V
Title V is the federal Operating Permits Program. It applies to "major
stationary sources" and is intended to consolidate all air pollution control
and compliance requirements into a single document. Sources are considered
"major" on the basis of their potential to emit federally regulated air
pollutants. The amount of emissions that is considered "major" depends on the
magnitude of the air quality problem in a given area. In areas that meet
federal standards, for example, a "major" source is one that has the potential
to emit 100 tons per year of a regulated air pollutant, or 10 tons per year of
a single Hazardous Air Pollutant, or 25 tons per year of a combination of two
or more Hazardous Air Pollutants. A listing with the threshold for "major" in
each air district is included in Appendix C. Appendix C also identifies
current federally "regulated air pollutants." [Back
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1) Potential to Emit
A source’s "potential to emit" is generally considered to be the maximum
amount it can emit, considering physical and other enforceable limitations.
In traditional air pollution terms, it means that if a factory is physically
capable of running three shifts, seven days a week, that it must be assumed
to do so unless there is some enforceable restriction that prevents that
from occurring. Some air districts have established a regulatory framework
to bridge the gap between "potential" and "actual" emissions. Where that
framework exists, it may help an agricultural source to determine whether or
not it needs to have a permit under Title V. CAPCOA also has a subcommittee
that works on Title V implementation issues. This subcommittee is developing
materials to assist sources in determining whether they are subject to Title
V, and districts will be working with U.S. EPA to identify what additional
mechanisms may be available and/or needed to bridge the gap between
"potential" and "actual" emissions at agricultural operations.
2) Point vs. Fugitive Emissions
Some air pollutants are emitted directly through a chimney, pipe, vent,
or stack, or they can be reasonably collected and passed through some exit
point. These kinds of "point" emissions are counted towards a source’s
potential to emit. Other emissions can’t be collected, like dust that is
created when a vehicle travels on an unpaved road or when a field is tilled.
These emissions are called "fugitive" and they are only counted towards a
source’s potential to emit if federal regulations list them; the current
list includes about two dozen heavy industrial categories of sources, as
well as any emission of Hazardous Air Pollutants. For the most part,
fugitive emissions at agricultural operations have not been federally
listed, so they are not counted where federal requirements, like Title V,
are concerned. There are some gray areas, however, and fugitive emissions do
need to be considered for other state and local air requirements. [Back to
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3) Contiguous Property
The simplest definition of "contiguous" is when two property parcels are
actually touching at a boundary. There are other situations that the courts
have determined to be "contiguous" for the purposes of determining what
emitting activities are part of the source. Some examples include parcels
that are divided by roadways, or which are separated by some distance but
are functionally interconnected. Generally, the courts have ruled that
artificial separations between related activities do not create separate
sources.
4) Common Ownership or Control
Property is under "common ownership or control" if the same person owns
both parcels or operations. Contractual agreements between two parties can
also constitute "common ownership or control." This is another area that has
been defined over time by court rulings.
d) Sources otherwise subject to district regulation
The federal Clean Air Act and the California Health & Safety Code give air
districts broad authority to regulate non-mobile sources of air pollution.
This includes traditional stationary sources of air pollution (like factories,
stationary engines, or fuel dispensing), but also things like dust emitted
from travel over unpaved roads, open fires to reduce vegetation in forests,
range lands, or crop fields, and small, ubiquitous sources of pollution like
woodstoves and water heaters. In the case of agricultural operations,
equipment or activities like gasoline or diesel fuel storage or dispensing,
degreasers for machine parts, storage silos, and on-the-farm operations for
manufacturing feed would be considered "otherwise subject to district
regulation." This is not a complete list, however.
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II. Removing the Permit Exemption
The bill eliminated the permit exemption language in the Health & Safety Code
in its entirety. This allows California law and implementing regulations to
conform with federal law and implementing regulations, which do not exempt
agricultural sources of air emissions. As a result, agricultural sources may now
be required to obtain air permits from the local air district with jurisdiction.
The bill sets up some more specific guidance and requirements, but ultimately it
will be up to individual air districts to determine how to implement the bill,
and local air quality and source contribution may affect permitting requirements
in a given district. The air districts are working together to identify common
approaches and promote consistency across the state, but different regions have
substantially different air quality needs, and this will affect both the
thresholds of applicability (see Appendix C), and types of emission mitigation
measures that are required (see Sections IV and V). [Back to TOC]
III. Establishing specific Permitting and Exemption
requirements
The bill addresses general air permits for agricultural sources in five
groups: (a) Sources subject to federal permitting requirements; (b) Sources
whose actual emissions equal or exceed 50% of the major source threshold; (c)
Sources whose actual emissions are less than 50% of the major source threshold;
(d) Sources that are de minimis; and (e) Sources that implement all listed
mitigations. Each of these areas is discussed below. [Back to TOC]
a) Sources subject to Federal Permitting requirements
The bill requires districts to ensure compliance with federal requirements
for permits under Title I and Title V of the federal Clean Air Act, consistent
with those requirements. Title I permits are required for new "major sources,"
or for existing "major sources" that are undertaking "major modifications",
before the source begins construction. The Act requires that sources
subject to this "New Source Review" use the best measures to reduce or
mitigate emissions from the new or modified operation. The source may also be
required to provide emission reductions to offset the emission increases
associated with the new or modified operation. As described in Section I (c)
above, Title V permits are required for existing "major sources."
1) New Source Review (NSR):
SB 700 requires "any agricultural source
that is required to obtain a permit pursuant to Title I … to obtain a permit
in a manner consistent with the federal requirements." The bill also
specifies that this be done through district regulations. This section
applies to new major sources and major modifications, which are defined in
the federal regulations based on an area’s attainment status. However, once
a source triggers NSR, the applicable requirements will be determined by the
district’s federally approved local NSR rule, unless the district develops a
new rule and that rule is submitted for federal approval. In areas where the
NSR thresholds are high, and new, large agricultural operations are not
common, there may be sufficient time for the district to adopt a new rule to
implement SB 700 permitting requirements. In areas where the threshold is
lower, and where it is likely that new agricultural operations will reach
NSR thresholds sooner, the district will probably not have sufficient time
to develop a new, federally approvable rule, and will therefore have to use
its existing program.
Agricultural sources that were in existence prior to January 1, 2004 and
are now being permitted will be considered "grandfathered" under NSR, which
means they are not subject to this review until they are modified. Existing
Agricultural sources that undertake a modification and new agricultural
sources which initiate construction or installation after January 1, 2004,
may be subject NSR if their emissions reach the applicable thresholds for a
"major source" and "major modification" (see Appendix C). The timeline for
submitting permit applications, and the specific requirements that apply
will be determined by the applicable regulations of the local air district.
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i) Best Available Control Technology (BACT): Generally speaking, "BACT"
is the best technology or practice for reducing emissions from a source,
that is either technologically feasible and cost-effective, OR it has been
achieved in practice at other similar sources. Typically, this is a
top-down review of technology and practices, where the most effective
reduction strategy is considered first and is required if it has been
achieved in practice at another similar source. If it has not been
achieved in practice, the strategy will be required if it is feasible and
cost-effective for the source. If the most effective strategy is not
feasible or cost-effective, the next most effective strategy is
considered. Each air district has a definition in its regulations for "BACT"
and that definition will govern the specifics of the control requirement
and the process by which the requirement is determined and costs are
considered. Many districts also have guidance materials available to
assist in this process, and there are also compilations, or
clearinghouses, of BACT determinations that can be consulted.
ii) Emission Reduction Credits (ERCs) and Offset requirements: Sources that are subject to federal NSR are required to offset the
emissions they increase by providing emission reductions. This is
generally done with emission reduction credits, or ERCs. There are very
strict federal requirements for the "quality" of ERCs that can be used to
offset emissions increases under NSR. The emission reductions must be (1)
real, (2) permanent, (3) quantifiable, (4) enforceable, and (5) surplus.
Over time, EPA policies and court determinations have established fairly
rigorous definitions and tests for each of these terms. [Back to TOC]
For certain agricultural operations, it is difficult to demonstrate
that emission reductions are real, permanent, quantifiable, enforceable,
and surplus – as those terms are defined by EPA and case law. Under
SB 700, the air districts are prohibited from requiring offsets for
sources for which the above demonstration cannot be made. These sources
may include, for example, crop farm fugitive dust, agricultural burning,
and non-equipment operations at CAFs. When it becomes possible to
demonstrate that emissions (increases and reductions) are real, permanent,
quantifiable, enforceable, and surplus, ERCs may be granted and offsets
required. A program to allow this would have to include a regulation that
is approved by EPA and incorporated into the State Implementation Plan
(SIP). Such regulations specify appropriate quantification methodologies,
and other provisions that ensure the reduction meet all the applicable
tests, and the regulatory process allows for public review and comment.
To date, California air districts have not succeeded in gaining EPA
approval to issue ERCs for agricultural activities. This has been the case
even for reductions from on-the-farm equipment that is similar to
traditional stationary sources. Therefore, ERCs will not be granted, nor
will offsets be required for agricultural sources until the local district
has adopted the needed regulations, and EPA has approved those regulations
and incorporated them into the SIP. [Back to TOC]
The local regulation that implements federal Title I review for
agricultural sources will need to specify the offsetting requirements for
sources subject to federal NSR. For an air district to provide exemptions
from this requirement, they must have EPA approval and may need to make
certain adjustments in their SIP-approved NSR regulations, until a
SIP-approved rule enabling the district to grant ERCs for agricultural
sources is in place.
2) Title V: SB 700 does not change the applicability criteria or
timelines associated with Title V permitting. Applicable federal regulations
and air districts’ federally approved Title V programs establish the
requirements and timelines for Title V applications and permits. For
instance, fugitive emissions will generally not have to be included when
determining Title V applicability (see Section I (c) above). Title V permit
applications will not be due until January 1, 2005, unless the air district
establishes an earlier submittal date.
Once a source is subject to Title V, all emission sources have to be
included in the Title V permit, unless the source has been listed as
"insignificant" on a federally approved list. The air districts will provide
application forms and guidelines to help with the application process. When
a complete application is submitted to the local district, the district
drafts the permit, which is then subject to public comment and review by
U.S. EPA. The permit becomes final only after EPA approves it. A Title V
permit is valid for five years, subject to the conditions specified in the
permit and in the local Title V program regulations. It must be reopened and
revised when certain significant changes occur; these are outlined in the
local Title V regulations as well.
The Title V regulations also specify timelines for permit actions. All
Title V permits have to be issued within three years, with one third issued
each year. [Back to TOC]
b) Sources whose actual emissions equal or exceed 50% of the major source
threshold:
The bill requires air districts to issue permits to sources that reach or
exceed this "50%" threshold, unless the district board makes certain findings;
Appendix C lists both thresholds ("major" and "50%") for each air district.
The bill specifies that the threshold is based on "actual" emissions, which is
different from "potential to emit." It also specifies that "fugitive dust" is
excluded from the calculation of "actual" emissions. Examples of "fugitive
dust" would include the particulate matter (dust) created when soil is
disturbed by vehicle traffic, or during operations like discing and
harvesting. Although fugitive dust is excluded when calculating emissions for
this threshold, other types of fugitive emissions are not excluded.
1) Calculating "actual" emissions for the "50%" threshold:
It is easier to
calculate actual emissions for existing sources, because usually there are
historical records of activity that can be used to estimate emissions. For
example, records of fuel use can be used to calculate combustion emissions
from an engine, and the number and type of fuel tanks would be used to
calculate evaporative emissions of reactive organic gases. Emissions are
calculated on an annual basis, which helps account for some seasonal variation
in activity. If there is significant variation from one year to the next, the
highest emission level is used because that level has been shown to be part of
a reasonably foreseeable operating scenario. To compare emissions to the
threshold, emissions of a pollutant (e.g., particulate matter) from all
equipment and activities are added together and compared to the threshold for
that pollutant. This is done for each pollutant. If the total emissions of any
pollutant reach the "50% threshold, then a permit is required. Once a permit
is required, all pollutants may be covered in that permit, not only the
pollutant which exceeded the threshold.
New sources do not have historical records. For local permitting
requirements, districts generally use an estimate based on a conservative but
reasonable scenario using information they have about similar operations. If
this information is either not available or is deemed not to apply in a
particular case, actual emissions are the same as the source’s potential to
emit. [Back to TOC]
2) How existing agricultural sources are affected: Beginning January 1,
2004, existing sources with actual emissions (including fugitive emissions
other than fugitive dust) at or above one half the major source thresholds,
for any single pollutant, will be subject to local permitting requirements,
unless the local rule specifically exempts them. Some districts have rules
that specifically exempt agricultural operations, others relied on the
exemption in state law without specifically restating it. In order to comply
with SB 700, any district with permitting rules that currently exempt
agricultural sources will have to change the rules, or adopt a new rule for
permitting agricultural sources with actual emissions at or above the 50%
threshold.
The bill does not provide any grace period to locate existing sources,
estimate their emissions, or provide application materials. Nor does it
provide a grace period for sources that self-identify to submit an
application. Most districts, however, have a process to permit sources that
previously enjoyed an exemption but are no longer able to use it. When an
exemption is lost, most districts will establish a reasonable grace period for
applications to be submitted. They publish notices (and use other mechanisms)
to alert affected sources that the exemption is lost and the grace period in
effect. The sources that apply and receive permits are not reviewed as "new"
sources, rather as sources with a "loss of exemption." This means that BACT
and offsets are not required, but the source may be subject to emission
reduction requirements under other local prohibitory rules (see paragraph (4),
below). Sources that fail to submit applications during the grace period may
face enforcement action.
Once a source has been issued a permit, the activities at the source have
to comply with the conditions of the permit or the source may face enforcement
action. Permits are generally valid for a one year term and are renewed
annually. If the source proposes an operational or physical change that
constitutes a "modification" under the applicable district rules, or under
Title I (see Section III (a) (1), above), the change would require a
pre-construction permit. The local district can help clarify whether a change
constitutes a "modification."
The requirement for existing sources to obtain a local permit is separate
from the requirement to obtain a Title V permit. Air districts have separate
programs for local and federal permits. This is primarily because local
permits cannot substitute for federal permits, and permits issued under Title
V are subject to additional restrictions and processes, which makes changing
them more difficult. Although the permits and processes are separate, some
districts may be able (consistent with applicable regulations) to coordinate
the application process for local and Title V permits to avoid duplication.
Title V is discussed in Section III (a) (2), above. [Back to TOC]
3) How new agricultural sources are affected: Effective January 1, 2004,
new agricultural sources with actual emissions at or above the "50%" threshold
will be subject to permits. If the source also triggers federal NSR, the
source will be required to use BACT, and possibly provide offsets (see Section
III (a) (1), above). Some districts are required under the California Clean
Air Act to have additional, local NSR provisions. Most districts in this
situation have a consolidated rule for federal and local NSR. In these
districts, a new agricultural source that reaches the "50%" threshold may be
subject to local NSR requirements, including new source emission controls and
possibly offsets, as determined by the local rules. The applicability of NSR
and the timelines for application submittal and processing will be determined
under the local rules. In most air districts, the sources will have to obtain
permits before initiating construction or installation.
If neither federal nor local NSR applies, the source would not be subject
to new source emission controls or offsets, but there may be emission control
requirements under other local prohibitory rules (see paragraph 4, below).
Permits will not be required for new agricultural sources when actual
emissions are expected to be less than one-half the major source threshold,
unless the district board has made certain findings in a public hearing (see
paragraph (c) (4), below).
4) How existing prohibitory rules may apply: Local air districts have
rules other than permitting rules. The rules are adopted to directly reduce
the air pollution emitted from a specified group of sources to which a
particular rule applies, whether the source is new or already existing. These
rules generally prohibit emission of one or more pollutants above the levels
in the rule, or under certain conditions, or they prohibit the operation of a
source without the use of specified controls, fuels, or other emission
reduction techniques. For this reason, they are called "prohibitory" rules. An
example would be the prohibition against operating a gasoline dispensing
system that pumps more than a specified amount of gas each month without
approved vapor recovery equipment. Another example would be a prohibition
against releasing particulate matter emissions in such a way that the
emissions plume exceeds a specified opacity limit.
Prohibitory rules apply to both new and existing sources. Sometimes they
have different requirements for different classes of sources, such as older
sources or sources that only experience limit use, but not always. Some of
these already existing prohibitory rules may specifically exempt or exclude
agricultural operations, but many do not. For example, in some districts,
prohibitory rules apply only to sources that require permits. If a prohibitory
rule does not specifically exempt agricultural operations, and an agricultural
source has equipment, or employs a practice, that is otherwise within the
scope of the rule, then the rule applies and the source will have to comply
with it. If the source will need additional time to comply, the source can
apply for a temporary "variance" from the requirement. Variance requests are
heard by the district’s Hearing Board and before one can be granted, the
Hearing Board must make certain findings that are specified in state law.
Variances are granted for a finite period, and variances cannot be granted to
avoid the requirement to obtain a permit. [Back to
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Air districts have been reviewing their existing prohibitory rules to
identify rules that will apply to agricultural sources, now that the permit
exemption has been removed. A district may find that some of these rules need
to be amended, either to add or remove exemptions for agricultural sources, or
to revise requirements. Any changes to a prohibitory rule have to be made
through a public hearing and approved by the district’s governing board.
Almost all prohibitory rules are also included in the SIP, and therefore
undergo a federal review as well. This means that changes can take
considerable time and resources. Each district will determine which, if any,
existing prohibitory rules should be changed, based on the way the local rules
are written, the impacts of changing or not changing a rule, and the resources
available. If a district plans to change a rule to exempt agricultural
sources, the source may be able to obtain a variance from those requirements
until the change is effective. If, on the other hand, a district plans to
change a rule to include agricultural sources, the sources can participate in
the rule development process and the rule, once changed, would provide a
reasonable compliance period. Good communication between the district and the
potentially affected sources will help clarify how existing prohibitory rules
apply. [Back to
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5) The findings a district board must make to exempt larger sources: After
reviewing local air quality problems, and the nature and contribution of
agricultural sources to those problems, a district may determine that it does
not need to permit some of the agricultural sources that exceed the "50%"
threshold. The district cannot exempt sources from federal permitting under
Title I and Title V, however, so the group of sources to which this might
apply are those that have potential emissions smaller
than the major source threshold, and actual emission larger than
half that level. Although the bill does not specifically require regulatory
action, such an exemption would have to be included in whatever rule governs
the permitting of agricultural sources in order for it to have effect. The
bill does specify that before it exempts any of these sources, the district
board must make specific findings, in a public hearing. The findings are
listed below, and all three of the findings must be made before an exemption
can be granted. However, the findings do not need to be made for each source
individually; it can be made for a group of sources all at once, provided that
the findings apply to all sources within the group. [Back to
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The source is required to obtain a permit under another provision of the
bill because it is a large Confined Animal Facility (see Sections I(a) and
V). This means that other types of agricultural sources (i.e., field or tree
crops) that exceed the "50%" threshold cannot be exempted from permits.
Further, any large CAF that would be exempted under this provision must have
a permit as required for large CAFs, so this provision does not provide an
exemption from permits altogether.
The permit is unnecessary to impose or enforce reductions in emissions
that cause or contribute to the violation of a state or federal ambient air
quality standard. This essentially means that the district board must find
that there are no emission reduction requirements that apply to the source
(or group of sources), and that none need be imposed in order to reach
attainment of air quality state and federal ambient standards.
Alternatively, the district board could find that requirements do apply, or
may need to be imposed, but that a permit is not necessary to impose or
enforce these requirements.
The requirement to obtain a permit would impose a burden on the source
(or group of sources) that is significantly more burdensome than the burden
faced by other similar sources that are required to obtain permits. Similar,
in this case, could mean that the magnitude and types of emissions are the
same, the types of equipment used are the same, and/or certain business
aspects (such as whether the source meets the criteria to be considered a
"small business") are the same. Once the "similar" sources are identified,
in order to make the finding, the district board would have to compare the
resources needed for the sources to obtain a permit, and show that the
burden is significantly greater for the agricultural source(s).
[Back to
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c) Sources whose actual emissions are less than 50% of the major source
threshold:
The bill directs air districts to exempt from permits those agricultural
sources that are below the "50%" threshold (see Appendix C for thresholds),
unless the district board makes certain findings. For this provision, the bill
specifies that "actual" emissions be the basis for applicability, and that
"fugitive dust" be excluded from applicability calculations (for more detail
on this, see the explanations in Section III (b), above).
1) How existing agricultural sources are affected: A source that can
show, using historical data and/or an analysis of reasonably foreseeable
operating scenarios that its emissions will not exceed the "50%" threshold
does not need to apply for a permit, as long as its potential to emit does
not reach the threshold for "major source" (see Section I (c)). The
exemption only applies for as long as the actual emissions and potential
emissions remain below their respective thresholds, however (actual : "50%",
and potential : major source). It is important to note that even if the
actual emissions remain below the "50%" threshold, the sources potential to
emit (i.e., capacity) may exceed "major source" thresholds. Some districts
have existing regulatory frameworks to address this discrepancy, but if the
district does not, then a Title V permit would be required and a local
permit would not.
Once physical or operational changes result in actual emissions above the
"50%" threshold, the source must apply for a local permit, and local NSR may
apply to the changes. The changes may also cause the potential to emit to
exceed "major source" thresholds, in which case Title V permits would be
required and federal NSR may apply to the changes as well.
2) How new agricultural sources are affected: As explained in Section
III(b), above, it is more difficult to establish "actual" emission levels
for a new source, and in some cases this means that "actual" and "potential"
are the same. Any new source that demonstrates its emissions are below the
applicable thresholds will not be required to obtain permits. Again, because
the local "50%" threshold is based on actual emissions, and the federal
"major source" threshold is based on potential to emit, they function
separately and it is possible to be exempt from one but not exempt from the
other. [Back to TOC]
3) How existing prohibitory rules may apply: A more complete
discussion of prohibitory rules is provided in Section III (b) (4), above.
The important consideration for sources exempt from permits is that some
prohibitory rules apply even if permits are not required. In fact,
unless the rule states otherwise, it generally applies regardless of whether
the source is also required to obtain a permit. Local districts are working
to identify prohibitory rules that will now apply to agricultural sources.
It is important that lists of these rules be made available to the
agricultural community, but sources should also check with their local
district to make sure they know what their requirements are.
4) The findings a district board must make to permit smaller sources:
After reviewing local air quality problems, and the nature and contribution
of agricultural sources to those problems, a district may determine that it
needs to permit some of the agricultural sources that are below the "50%"
threshold. Before it can do this, the district board must make certain
findings in a public hearing. Although the bill does not specifically
require the threshold change to be incorporated in a rule, for practical
reasons permitting thresholds are generally incorporated into the permitting
rule. The bill does specify that all of the following findings be made,
however:
The source is not subject to other permit requirements for large
Confined Animal Facilities as specified in other provisions of the bill
(see Sections I (a) and V). This means that district board may set lower
permitting thresholds for agricultural sources that do not involve
confined animals (such as field and tree crops); it may also set lower
thresholds for CAF operations that are not defined as "large" by the state
Air Resources Board (again, see Section V).
The permit is necessary to impose or enforce reductions of air
pollutants that cause or contribute to a violation of a state or federal
ambient air quality standard. To make this finding, the district board
would have to show that a permit is necessary to enforce the emission
reduction requirements of existing rules, or that a permit is necessary to
help the district develop or enforce new emission reduction requirements.
In either case, the emission reduction requirements must address emissions
that cause or contribute to a violation of state or federal ambient air
quality standard.
The requirement to obtain a permit would not impose a burden that is
significantly larger than the burden placed on other similar sources that
are required to obtain permits. Similar, in this case, could mean that the
magnitude and types of emissions are the same, the types of equipment used
are the same, and/or certain business aspects (such as whether the source
meets the criteria to be considered a "small business") are the same. Once
the "similar" sources are identified, in order to make the finding, the
district board would have to compare the resources needed for the sources
to obtain a permit, and show that the burden is not significantly greater
for the agricultural source(s). [Back to TOC]
d) Sources whose emissions are de minimis
The bill allows districts to exempt from permits and other requirements of
the bill any agricultural sources whose emissions of nitrogen oxides, volatile
orgranic compounds, and particulates are each less than one ton per year. The
bill does not specify the basis for evaluating the emissions. In order to be
consistent with other exemption criteria, the districts believe this
determination should be based on actual emissions. The bill also does not
specify that the exemption be included in a regulation, but it does require a
public hearing to make the finding that emissions are de minimis. For
practical reasons, a district choosing to allow this exemption is likely to
implement it through the applicable permitting rule.
e) Sources that implement all listed mitigations
The bill allows districts to adopt a rule that exempts from permits and
other requirements any source that mitigates its emissions from all of the
types of activities and equipment listed in the bill. This list includes:
Removing all internal combustion engines used in the production of crops
or the raising of fowl or animals (except an engine that is used to propel
implements of husbandry) at the source, and replacing them with engines that
meet or exceed the most stringent standards adopted by the state board and
the U.S. EPA.
Reducing or mitigating emissions from all agricultural activities,
including (but not limited to) tilling, discing, cultivation, the raising of
livestock and fowl, and similar activities, to a level that the district
determines does not cause or contribute to a violation of a state or federal
ambient air quality standard, a toxic air contaminant standard, or other air
limitation.
Reducing or mitigating all emissions from any farm equipment,
underground petroleum fuel tanks, or other similar equipment used in
agricultural activities to a level that the district determines does not
cause or contribute to a violation of a state or federal ambient air quality
standard, a toxic air contaminant standard, or other air limitation.
The bill specifically states that this exemption must be adopted as a
program, which means it is a regulatory action. Because the bill also states
that nothing in the bill can relieve a source of the requirement to obtain
federal permits, this exemption does not apply to federal NSR or to Title V.
[Back to TOC]
f) Summary and Timing
The primary considerations for most sources to determine their
permitting requirements will be how their emissions (actual and potential)
compare to permitting thresholds (local and federal). The schematic below
shows how SB 700 sets forth basic permitting requirements. This does not
include the exemptions for de minimis or fully mitigated emissions. It also
does not include the permit requirements that apply specifically to Confined
Animal Facilities. Most importantly, it does not reflect the discretion
districts have to set other thresholds under SB 700 as well as under federal
and state statutes, except by marking with an asterisk (see * in chart
below) the circumstances where that is possible. It is also important to
remember that thresholds will vary from district to district based on the
attainment status of the district, and NSR thresholds are different.


* Note: districts have certain
discretion to set or alter permitting thresholds requirements,
consistent with state and federal statutes; this discretion is discussed
in more detail in the preceding text.

As stated previously, the bill does not specify timing for general
permitting; while there are no deadlines, there is also no grace period. In
cases where local rules need to be amended, or new rules adopted in order to
implement the general permitting requirements of SB 700, the district should
move expeditiously with the necessary rule adoption.
Within the framework of applicable local rules, new sources and
modifications to existing sources need permits before construction.
Existing sources that require Title V permits have one year to submit their
application and the district has a maximum of three years to process all
applications submitted, under the federal Title V program. Air Districts
intend to expedite their review to the degree feasible, however districts may
adopt rules to require Title V applications sooner, so they can begin
processing them in a timely manner. For existing sources that do not need
federal permits, the district may adopt a schedule for them to apply under a
loss-of-exemption status which can shield them from enforcement action for
failure to have a permit. If no loss-of-exemption schedule is adopted,
existing sources should file applications as soon as they can, to minimize the
potential for enforcement. Districts will process permit applications
according to their local rules and procedures. [Back to
TOC]
IV. Emissions control in federal nonattainment areas for
PM10
The bill requires a district to adopt by regulation a set of measures to
reduce emissions from agricultural sources, if the district does not meet any of
the federal ambient air quality standards for particulate matter. The
requirement applies in areas that have been designated as "serious" or
"moderate" nonattainment by January 1, 2004. The San Joaquin Valley APCD and the
South Coast AQMD were both designated "serious" as of that date. Imperial County
APCD, the Mojave Desert AQMD, and Sacramento County are designated "moderate"
nonattainment. The Great Basin AQMD (with Inyo, Mono, and Alpine counties) has
three sub-regions that are designated "moderate" nonattainment and one
sub-region that is designated "serious." The situation there is unique in that
the air quality is heavily influenced by episodic wind-blown dust from dry lake
beds. [Back to TOC]
a) Serious PM Nonattainment Areas
The bill establishes requirements for the local district to adopt a
regulatory program, including the degree of emissions mitigation it must
contain, the schedule for program adoption, and procedural requirements to
ensure that standards for agricultural engines are commensurate with engine
standards for other source categories. For emissions mitigation and the
adoption schedule, the bill states the following:
Each district that is designated as a serious federal nonattainment area
for an applicable ambient air quality standard for particulate matter as of
January 1, 2004, shall adopt, implement, and submit for inclusion in the state
implementation plan, a rule or regulation requiring best available control
measures (BACM) for sources for which those measures are applicable and best
available retrofit control technology (BARCT) for sources for which that
technology is applicable for agricultural practices, including, but not
limited to, tilling, discing, cultivation, and raising of animals, and for
fugitive emissions from those agricultural practices, in a manner similar to
other source categories but the earliest feasible date, but not later than
January 1, 2006. The rule or regulation shall also include BACM and BARCT to
reduce precursor emissions in a manner commensurate to other source categories
that the district shows cause or contribute to a violation of an ambient air
quality standard. Each district that is subject to this subdivision shall
comply with the following schedule with respect to the rule or regulation
imposing BACM or BARCT:
On or before September 1, 2004, notice and hold at least one public
workshop for the purpose of accepting public testimony on the proposed rule
or regulation.
On or before July 1, 2005, adopt the final rule or regulation at a
noticed public hearing.
On or before January 1, 2006, commence implementation of the rule or
regulation.
b) Moderate PM Nonattainment Areas
By the earliest feasible date, but no later than January 1, 2007, each
district that is designated a moderate nonattainment area for an applicable
ambient air quality standard for particulate matter as of January 1, 2004,
shall adopt and implement control measures necessary to reduce emissions from
agricultural practices, including but not limited to, tilling discing,
cultivation, and raising of animals, and from fugitive emissions in a manner
similar to other source categories from the activities by the earliest
feasible date. Control measures adopted and implemented pursuant to this
section shall also be implemented by the district to reduce precursor
emissions in a manner commensurate to other source categories that the
district shows cause or contribute to a violation of an ambient air quality
standard.
A district is not required to implement the above control measures if it
determines in a public hearing that agricultural practices do not
significantly cause or contribute to a violation of state or federal
standards. [Back to TOC]
c) Best Available Control Measures (BACM)
Air pollution control programs address both traditional and non-traditional
types of sources. Traditional types of sources generally include industrial
and commercial operations where the pollution is emitted from an exhaust pipe
or stack, or the entire area is in some way enclosed so that emissions can be
collected and treated. In other words, the emissions are generally not
"fugitive", although fugitive emissions also occur at traditional sources and
are subject to mitigation strategies. Non-traditional types of sources would
include such agricultural activities as discing, tilling, and travel on
unpaved roads, where the pollutant of concern is the fugitive dust emitted
when the soil is disturbed. Certain activities associated with raising animals
would also be considered non-traditional. The concept of "Best Available
Control Measures" or "BACM" was developed to characterize a higher standard of
mitigation from non-traditional sources in areas with serious particulate
nonattainment problems. The term is defined in federal regulations, and in
order for a mitigation measure to be approved as "BACM" by EPA, it must meet
several specific tests. Both the San Joaquin Valley and the South Coast air
districts have developed rules to implement BACM, including requirements for
minimizing dust at construction sites, the planting and stabilizing of exposed
soils, and enclosing storage of dry materials, as well as other mitigation
strategies. These rules are also being updated under SB 700 and other
requirements.
d) Best Available Retrofit Control Technology (BARCT)
This is term characterizes a standard of emissions control from existing,
traditional sources. Under federal air pollution programs for traditional
sources, different levels of control are expected of new sources (best
available) and existing sources (reasonably available), with the understanding
that there are more options available at greater cost-effectiveness when a
source is being designed, than there are after it is built, especially if it
was built a long time ago. California law established an intermediate level of
control that is the "best available" for "retrofit" to existing sources,
recognizing that the state’s air pollution problems may demand more effective
pollution control than what is usually considered "reasonably available."
Local air districts have adopted many rules to implement BARCT, including
particulate control efficiency standards and limitations on exhaust pollutants
such as nitrogen oxides, or technology-based requirements that dictate the use
of particular control device or something that is equally effective.
e) Precursor Emissions
This section of the bill specifically requires that "precursor" emissions
be controlled. Emissions are considered "precursor" if they react with other
pollutants to form the pollutant of concern. For example, ozone is a pollutant
of concern but it is rarely emitted directly; nitrogen oxides react with many
organic gases to form ozone in the presence of sunlight. So the air districts
regulate the nitrogen oxides and the organic gases to reduce the formation of
ozone. Nitrogen oxides also react with ammonia to form fine particles, and
several size fractions of particles in the air are considered pollutants of
concern, so nitrogen oxides and ammonia are "precursor" pollutants to
particulate matter. Other commonly emitted pollutants can react to form
particulate matter as well, such as sulfur compounds and certain organic
gases, and these would also be considered "precursor" pollutants for
particulate matter. The local district use emissions inventory information,
meteorology, and computer models to determine which pollutants need to be
reduced by how much in order for the air quality to improve. [Back to TOC]
f) Procedures for Regulating Engines
The bill contains provisions designed to ensure that engines at
agricultural operations are regulated in the same way that engines are
regulated when they are associated with other types of operations. The
district has to evaluate certain aspects of the regulation and ensure that
these aspects are "commensurate" or "similar" to regulations for engines at
other sources. The aspects to be considered include:
Engine size and duration of use
Degree of emissions control
Cost effectiveness of emissions control
The bill also requires that the district prioritize the adoption of control
measures under this section to ensure that the most cost effective measures
are adopted first, unless the district finds a different order is necessary. A
different order can be justified if it is needed for reasons of
enforceability, technological feasibility, or the willingness of the public to
accept the measure, or if the different order of adoption is needed to
expeditiously attain or maintain attainment of an ambient air quality
standard. [Back to TOC]
V. Permits & Emissions Mitigation for large CAFs
Confined Animal Facilities, whether defined as "large" or not, are subject to
the general permitting thresholds and requirements described in Section III,
including permits for existing sources [and] permits for new or modified sources. SB
700 sets out additional requirements for "large" Confined Animal Facilities,
however, and those additional requirements are described below.
Basically, the bill requires the state Air Resources Board to establish a
definition for "large" CAFs. It requires districts to adopt rules that require
"large" CAFs to obtain permits and to implement emissions mitigation. The degree
of mitigation required is based on the district’s federal classification for
ozone attainment. Districts that attain the federal ozone standards may be
excused from adopting these rules if they make a showing that agricultural
sources in the district are not causing or contributing to a violation of a
state or federal ambient air quality standard.
a) Defining "large" CAF
SB 700 requires ARB to review all available scientific information,
including but not limited to emissions factors for CAFs, and the effect of
those facilities on air quality in the basin and other relevant scientific
information, and develop a definition for the source category of "large" CAF.
The definition must be adopted in a public hearing, and the hearing must occur
on or before July 1, 2005.
This means the ARB has to consider the emissions from CAFs and how those
emissions affect attainment and maintenance of ambient air quality standards
in air basins. An air basin is an area, usually large, where the air mixes and
generally stays, although there is transport of pollution between air basins.
Air districts are grouped into air basins for the purpose of planning and
implementing plans to reach attainment; there are 14 air basins in California.
In considering the relationship between emissions from CAFs and air quality in
the air basin, ARB may find that CAFs play a different role in the air quality
problem in different air basins.
The bill does not specify what basis should be used for the definition of
"large" CAF. The definition of "large" could be based on tons of emissions or
numbers of animals, or some other factor that the ARB determines is
representative of the impact of the CAFs on air quality. The definition could,
like the definition of "major source," vary between air districts, or between
air basins, to reflect the differing severity of the air quality problems in
the region. If this type of definition is used, the thresholds are likely to
be lower in areas with more severe problems, and higher in areas where the air
quality is better. On the other hand, ARB could follow the hazardous air
pollutant model and choose a single definition for the entire state.
If the definition established by ARB includes CAFs whose emissions are less
than one half the major source threshold in the district, the district may
permit them only if it makes specified findings with respect to need and
burden (see Section III (b) (5), above). [Back to
TOC]
b) Permit Requirements and Schedule for "large" CAFs
The bill requires air districts to adopt a regulation that requires any CAF
that meets the definition of "large" established by the ARB to obtain a permit
from the district. The districts must adopt the regulation and submit
it for inclusion into the SIP by July 1, 2006, unless the district is
designated "attainment" for the federal ozone standard. The regulation must do
all of the following:
These are fairly standard rule elements. In plain language, they mean the
district will adopt a regulation that specifies how mitigation requirements
will be determined, and how permits will be required, submitted, reviewed,
issued, and complied with. This process specifically provides for input by
people who will be affected by the regulation, or who are interested in what
it does, and it further allows people to review and comment on draft permits.
Finally, the bill requires that permits be reviewed periodically after they
have been issued, and that the mitigation measures in them be adjusted to
reflect improvements in technology or procedures, or other changes that affect
feasibility.
c) Emissions Mitigation for "large" CAFs
The bill establishes a procedure to require emissions mitigation for
"large" CAFs. Rather than establish a single rule that requires the same set
of mitigation measures for all the facilities in the category, however, it
provides for a more tailored, case-by-case review. Under this approach, the
owner or operator reviews the operation and proposes a strategy to reduce
emissions "to the extent feasible." The bill provides some benchmarks for how
high the standard is, based on the air quality in the area. It also provides
for a clearinghouse of information on available mitigation measures (see
Section VI, below) that an owner or operator can refer to for ideas.
The bill specifies that in areas with "extreme" or "severe" ozone problems
(i.e., the San Joaquin Valley, the South Coast, and the Sacramento region), a
"best available" for existing sources is the degree of mitigation required.
This standard of mitigation is reviewed in Section IV (d), above. In areas
with "serious" or "moderate" ozone problems (see Appendix C), the mitigation
should include measures that are "reasonably available." The primary
difference between the two levels is the extent to which measures have already
been demonstrated in practice, and the cost of implementing the measures. No
specific standard of control is required in areas that attain the federal
ozone standard, although it is reasonable to infer that the standard would not
have to be higher than "reasonably available" unless otherwise determined by
the local district.
When a proposed plan is submitted to the district, the district reviews the
plan and determines if it includes the required degree of mitigation. In doing
this, the district will consider measures listed in the clearinghouse,
measures identified in other plans, the size and nature of the facility, any
unique circumstances that may affect feasibility and cost, and other
appropriate factors. If the plan does not seem to include the required degree
of mitigation, the owner or operator will have an opportunity to provide
additional data and/or mitigation, and the district may identify specific
measures that need to be included. Before the final plan is approved as part
of the CAF’s permit, there is an opportunity for the public to review and
comment on the plan. If the owner or operator disagrees with the final
decision of the district, an appeal can be brought before the district’s
hearing board. [Back to TOC]
d) Procedures to Assess Other Impacts of Rulemaking:
The bill specifies procedures for the air districts to follow to evaluate
and "make a good faith effort" to minimize the adverse impacts of rulemaking
activities. The district has to consider:
the number and type of sources affected
the nature and quantity of emissions
the potential for reductions in emissions
the range of probable costs
the availability and cost-effectiveness of alternatives
the technical and practical feasibility
additional information that is submitted to the district board
Before the regulation can be approved, the district’s governing board has
to review the staff’s evaluation of adverse impacts and the efforts made to
minimize them, in a public hearing.
e) Areas that Attain the federal Ozone Standard
The bill recognizes that areas that are designated "attainment" for the
federal ozone standard face different circumstances than those that do not
attain the standard. It does not require these districts to submit their rules
for approval into the SIP, because the SIP is a compilation of rules adopted
for the purpose of reaching attainment.
The bill also allows areas that already attain the federal ozone standard
to make a demonstration that "large" CAFs do not cause or contribute to a
violation of an ambient air quality standard, and therefore it is not
necessary to adopt the regulation to permit them and mitigate their emissions.
This demonstration is likely to include a review of ambient air quality data
(including the nature and timing of elevated pollutant levels), and analysis
of the local emissions inventory (including identification of the major
contributors to elevated pollutant levels). Areas that may be able to make
this demonstration include areas where elevated pollutant levels are the
result of overwhelming transport from other regions, mountain areas where
there are no "large" CAFs, or areas where violations of ambient standards are
limited to the particulate standards and are clearly caused by wintertime
combustion of wood for residential heating. This is not a complete list,
however, and other areas may be able to make the demonstration as well.
Air districts with similar air quality and emission inventories may be able
to collaborate on a demonstration to share their resources, and the ARB has
agreed to work with these districts in developing the demonstration.
[Back to TOC]
VI. Mitigation Clearinghouse
The bill calls for a clearinghouse of mitigation measures or strategies
available for agricultural sources. It assigns the task of creating and
maintaining the clearinghouse to the California Air Pollution Control Officers
Association, or CAPCOA, with a deadline of January 1, 2005. The bill lists
several specific areas that should be included in the clearinghouse, as follows:
Operations that create fugitive dust emissions, including but not
limited to, discing, tilling, material handling and storage, and travel on
unpaved roads.
Confined animal facilities.
Internal combustion engines used in agricultural operations.
Other equipment, operations, or activities associated with the growing of
crops or the raising of fowl or animals, that emit, or cause to be emitted,
any regulated air pollutant, or any precursor to any air pollutant.
The clearinghouse is intended to assist in the development of the rules and
plans required in the bill. It can also be used by permitting agencies when a
new agricultural source triggers New Source Review, or by anyone running an
agricultural operation who wishes to minimize air pollution in order to be a
good neighbor.
[Back to TOC]

Source: CAPCOA Web Site - http://www.capcoa.org/sb_700.htm
Info at ARB web site:
http://www.arb.ca.gov/planning/agriculture/agriculture.htm
The San Joaquin Valley Unified Air
Pollution Control District:
www.valleyair.org/
Current focus is on the San Joaquin Valley as they have some of the largest Ag
operations in California and an "extreme category" air pollution
problem -
agricultural activities are
significant contributors to the problem. The SJVUAPCD covers eight counties including San Joaquin,
Stanislaus, Merced, Madera, Fresno, Kings, Tulare and the valley portion of
Kern.
