An emission reduction credit (ERC) is a
credit granted upon request by an emission source who voluntarily
reduces emissions beyond required levels of control. An ERC represents
the legal ability to emit regulated pollutants in an amount equal
to the quantity specified when the ERC was granted. ERCs may be
sold, leased, banked for future use, or traded in accordance with
applicable regulations established by SWCAA. ERCs are intended to
provide an incentive for reducing emissions below required levels,
and to establish a framework to promote a market based approach
to air pollution control.
The Washington Clean Air Act (RCW 70.94.850)
authorizes local Air Authorities to implement an emission credits
banking program. Local Air Authorities who choose to implement an
emission credits banking program are required to operate a credit
bank for the purpose of administering approved emission reduction
credits.
SWCAA has adopted regulations for implementation
of its emission credits banking program. These regulations comprise
three sections of SWCAA's "General Regulations for Air Pollution
Sources" (SWCAA 400). SWCAA 400-130 "Use of Emission Reduction
Credits" governs the use of ERCs. SWCAA 400-131 "Deposit
of Emission Reduction Credits Into Bank" governs the issuance
of ERCs. SWCAA 400-136 "Maintenance of Emission Reduction Credits
in Bank" governs the maintenance of the ERC bank.
The owner or operator of any source which
reduces its actual emissions rate for any contaminant regulated
by state or federal law or regulations established to implement
such laws may apply to SWCAA for an ERC. Any application for an
emission reduction credit must be stated as an allowable limit in
weight of contaminant per unit time for the emissions unit involved.
An ERC application must be made within 180 days after the emission
reduction has been accomplished. An ERC will be granted based upon
conditions set forth in SWCAA 400-131(3). Approval of an ERC application
will result in the issuance of a Regulatory Order to assure that
the emissions from the source will not exceed the allowable emission
rates claimed in the ERC application, and provide for issuance of
a certificate of ERC.
SWCAA has established a credit bank to administer
ERCs granted to emission sources under SWCAA 400-131. The owner
of any ERC shall maintain the ability to use said ERCs through deposit
in the credit bank. Any ERC deposited in the credit bank is subject
to annual registration fees or operating permit fees as appropriate
for the emission source in question. If the owner of any ERC fails
to maintain or renew the applicable registration fees 6 months beyond
the due date, then the ERCs revert to SWCAA. ERCs deposited in the
credit bank are discounted 10% to allow for minor emissions increases
in nonattainment areas by minor sources. SWCAA maintains a log of
ERC transactions which accurately reflects the amount and nature
of credits contained in the bank.
An ERC may be used to satisfy the requirements
for authorization of a bubble under SWCAA 400-120, as a part of
a determination of "net emissions increase," as an offsetting
reduction to satisfy the requirements for new source review per
SWCAA 400-111, 400-112, SWCAA 400-113(3) or SWCAA 400-113(6), or
to satisfy requirements for PSD review per SWCAA 400-113(4). Use
of an ERC will be granted based on conditions as set forth in SWCAA
400-130(3). An ERC may be sold or otherwise transferred to another
owner as set forth in SWCAA 400-130(4). Whenever an ERC is used,
the certificate of ERC must be surrendered to SWCAA. An amended
certificate will be returned to the owner if only a portion of the
ERC is used. An unused ERC and any unused portion thereof expires
five years after the date the emission reduction was accomplished.
In the mid to late 1980's, the Longview
area was a secondary nonattainment status for TSP and the Vancouver
area was nonattainment status for CO and ozone. At that time, new
or modified industrial sources with emissions greater than one ton/year
in a nonattainment area needed to obtain emissions offsets at a
ratio of 1.3 to 1.0 (i.e., a 100 ton source would have to get 130
tons of offsets) pursuant to federal Clean Air Act requirements.
The objectives of the offset policy were to promote more cost-effective
pollution control through the use of market mechanisms and to allow
for economic growth within areas in which the ambient air quality
standards were being exceeded.
In order to provide an easily available
mechanism for growth for new or modified sources in the nonattainment
areas of SWCAA jurisdiction, in 1986 SWCAA adopted new general regulations
that included provisions for a emission credit bank for VOCs and
PM and conditions for issuance of emission credits for sources that
emitted greater than 1 ton/year of those pollutants. The beginning
balance of the private and public VOC bank was established with
emission credits from the December 1982 shutdown of Carborundum,
a silicon carbide processing facility in Vancouver. The Port of
Vancouver purchased the Carborundum property (in 1986), requested,
and was granted 100 tons/year of PM and VOC emission credits to
be able to attract new business to the Port. The remainder of the
Carborundum credits were assigned to SWCAA (400 tons per year PM
and 140 tons per year VOC) for attracting new businesses or providing
for existing business expansions.
In addition to the Carborundum credits,
the SWCAA Board of Directors adopted two resolutions that added
emission credits to the bank. Resolution 1988-3 adopted on July
19, 1988 allocated 1,120 kg/day VOCs, 70% of VOC emissions determined
to be excess in the State Implementation Plan at that time, to the
bank. Amended Resolution 1989-3 adopted on January 24, 1989 amended
emissions to the bank to 972 kg/day, 30% of VOC emissions determined
to be excess in the State Implementation Plan at that time.
In September of 1993, the SWCAA General
Regulations (SWCAA 400) were revised to be consistent with federal
and state of Oregon rules for nonattainment areas which only require
an offset of 1.1 to 1.0 and only for new sources of 100 tons or
greater or modified sources with an increase of 40 tons or greater
instead of the previous 1.3 to 1.0 and 1 ton increase threshold.
Most, if not all, public credit banking transactions performed by
SWCAA prior to these regulation changes were for quantities less
than 40 tons per year. Therefore, those types of sources that had
requested and received emission credits prior to 1993 no longer
are required to go through this process for quantities less than
those described above.
Private CO and NOx credit banks have also
been established with requests for credits from several industries
due to shutdowns or modifications.
Neither the SWCAA credit bank nor credit
program have been approved by the US Environmental Protection Agency
(EPA). Each year when the Washington Department of Ecology (WDOE)
and SWCAA submit the general regulations to the EPA for update as
part of the Washington State Implementation Plan (SIP), the rules
for the emission credit bank are rejected by EPA. This is due to
the fact that the WDOE and SWCAA rules for emission banking did
not conform to the EPA guidelines when they were established in
1986 (i.e., Carborundum credits were banked 4 years after actual
emission reduction) nor current regulations (i.e., the 10 year expiration
date does not compare with the 5 year expiration date of federal
rules). Therefore, the credits established under the bank are not
federally recognized or approvable for large sources and cannot
be used for satisfying federal programs such as prevention of significant
deterioration (PSD), offsets, or new source review.
The Vancouver Ozone Maintenance Plan/Redesignation
Request (approved by EPA on April 30, 1997) for the Portland/Vancouver
ozone nonattainment area did not account for credits in the SWCAA
VOC bank in the emission inventory in the plan. This was an unintentional
oversight rather than a deliberate action, however, there would
have been an issue of federal enforceability and time periods to
reconcile as part of proposing use of these credits. (The private
NOx and CO ERCs were accounted for in the Ozone and CO Maintenance
Plans due to the fact that 1992 actual emissions were used in the
Maintenance Plans and all the current CO and NOx bank credits were
accounted for in those emissions; i.e., the shutdowns occurred after
1992.) The proposed Ozone Maintenance Plan/Redesignation Request
does include a growth margin for new or modified sources, however,
this margin does not provide for use of any existing or future credits.
Since the Ozone Maintenance Plan/Redesignation Request has this
growth margin for industrial sources, emission reduction credits
are not needed until the growth margin is used up and the rules
require offsets once again. Since SWCAA rarely has new major sources,
this may not occur until after the full 10 year Maintenance Plan
time period. If a major source did need offsets, they currently
would not be able to use the VOC credits in the existing banks since
they are not federally enforceable. Also, even if the SWCAA credit
bank gets approved by EPA, there is only enough VOC credits in the
public VOC bank for one new major source to use.
SWCAA General Regulations (SWCAA 400) were
again revised in April 1999 which eliminated the public banks, retained
the private banks, and revised the rules to be consistent with federal
rules; i.e., credits expire in 5 years from date emission reductions
accomplished.
As of April 2006, the current balance in
the banks are as follows:
| Public VOC bank |
Dissolved |
| Private VOC bank |
0 tons/yr. |
| Public PM bank |
Dissolved |
| Private PM bank |
0 tons/yr. |
| Public CO bank |
Dissolved |
| Private CO bank |
0 tons/yr. |
| Public NOx bank |
Dissolved |
| Private NOx bank |
0 tons/yr. |
Submit the revised SWCAA 400 rules to EPA
for approval and inclusion in the SIP. Therefore, if offsets become
required again, the private credits can be used for federal programs.
Otherwise, there may not be a need for the banks if one could only
use credits that had been approved in the SIP.
Revise rules to allow the ability for future
interstate emission trading. Other states and agencies will have
to revise their own rules to accommodate interstate trading issues;
other states and agencies have not shown great interest however.
The Oregon Department of Environmental Quality has stated they could
approve an interstate transfer on a case-by-case basis using a source-specific
SIP revision.
1. No PM
credits have ever been issued by SWCAA and the entire amount from
Carborundum expired
in July of 1996.
2. No CO
or NOx public credits have ever been issued by SWCAA nor has there
ever been public CO or NOx credits
available.
10/19/2006
|