TMDLs
Section 303(d) of the Clean Water Act (CWA) requires states
to submit a list (303(d) List)
of surface waters that do not meet applicable water quality standards
(impaired waters) for which implementation of technology-based effluent
limitations alone do not ensure attainment of applicable water quality
standards. The list of impaired waters includes priority rankings for
establishment of Total Maximum Daily Loads (TMDLs) for these waters.
Once the impaired waters are identified, Section 303(d)
requires that the states establish
total daily maximum loads (TMDLs) that will
meet water quality standards for each listed water, considering seasonal
variations and a margin of safety (MOS) that accounts for uncertainty. TMDLs
establish the maximum amount of a pollutant that a water body can assimilate
without causing exceedances of water quality standards.
A TMDL is a tool for reducing water pollution in impaired
waters. A TMDL calculates the amount of a pollutant that the waterbody can
receive and still meet applicable water quality standards. Basically, a TMDL
is the sum of the allowable loads of a single pollutant from all contributing
point and nonpoint sources with a margin of safety (MOS) that accounts for
uncertainty. The TMDL also addresses reductions needed to meet water quality
standards and allocates those reductions among the point and nonpoint sources
in the watershed. As such, development of TMDLs is an important step toward
restoring our waters to their designated uses.
TMDLs are developed for the most critical environmental
conditions, i.e., stream flow, temperature, weather conditions, etc., using
data compiled in a particular geographic area or watershed from reliable
sources. Scientifically accepted mathematical methods that represent what is
happening in nature are used to develop the TMDL. A GIS (geographic
information system) format may also be used to provide the framework for the
model’s information, particularly land use distributions. Data and information
may include the relative contribution of different kinds of activities like
point and nonpoint sources of pollutants. All of this information is then used
to propose a TMDL that is appropriate for the specific water body.
A TMDL will include loads from point sources (such as
municipal and industrial wastewater treatment facilities) and nonpoint sources
(such as direct runoff from agricultural lands, urban areas, forested lands,
etc.) in the watershed. TMDLs will look at impacts on waterbodies from many
kinds of contamination, will consider seasonal variations, and will account
for background levels of pollutants (those levels occurring in nature). TMDLs
compare current loads and proposed loads with expected levels of reduction to
achieve the water quality standards.
Settlement of a lawsuit filed against EPA Region 4 in 1998
(1998 Consent Decree)
established a schedule for TMDL development in Alabama. The schedule is based
on Alabama’s 1996 §303(d) list, which included 115 waterbodies. The schedule
requires that all 115 waterbodies be addressed by November 5, 2003 either by
developing TMDLs or by delisting waters that can be shown to be fully
supporting their designated uses. A list of TMDLs that Alabama has targeted
for development over the next two years has been submitted to EPA (TMDL
Schedule ).
- 1998 Consent Decree Completion Dates:

The Clean Water
Act and EPA’s implementing regulations provide for stakeholder involvement in
the TMDL development. The public may
participate in the TMDL development and implementation process through
watershed organizations such as the Alabama
Clean Water Partnership. Also, anyone is
welcome to comment on a TMDL during the public notice period for the TMDL. A
30-day public notice period will be held following the publication for each TMDL. Any comments received during the
public notice period will become a part of the TMDL administrative record,
and will be considered by ADEM prior to finalizing the TMDL report.
Following the public review and comment period and any
necessary revisions, the states are required to submit their TMDLs to EPA for
approval (EPA
Approved TMDLs) and, once EPA approves them, are to
incorporate them into their permitting and watershed management programs. EPA
must approve or disapprove state TMDLs within 30 days of final submission (TMDLs
Waiting EPA Approval ). If EPA disapproves a state TMDL, EPA must
establish the TMDL.
Implementation of TMDLs refers to any combination of
regulatory, non-regulatory, or incentive-based actions that attain the
necessary reduction in pollutant loading. Non-regulatory or incentive-based
actions may include development and implementation of Best Management
Practices (BMPs), pollution prevention activities, and habitat preservation or
restoration. Regulatory actions may include issuance or revision of wastewater
and stormwater permits to include permit conditions consistent with the TMDL.
These permit conditions may be numeric effluent limitations or narrative
requirements based on BMPs needed to achieve the necessary pollutant load
reduction.
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