Many state water quality standards were established in the
early years of the Clean Water Act (CWA) when a key goal of the 1972 CWA was
“to eliminate pollutant discharge to navigable waters by 1985.” Unfortunately,
this admirable goal sometimes has resulted in required pollutant load
reductions (e.g., TMDLs) that are based on unattainable water quality standards
that reflect the environmental euphoria of the 1970s and 1980s. In my view, it
is wise to consider if we should continue to develop water quality management
plans focused on achievement of those goals, or if it is better to develop
realistic goals and set attainable water quality standards.
From a pragmatic perspective, working toward unattainable water
quality standards diminishes our ability to achieve widespread buy-in on pollutant
load controls. I see this reaction to water
pollutant control now in North Carolina, where unattainable standards are
leading to a backlash against pollutant reduction, due primarily to extremely high
costs of compliance with a TMDL.
Unfortunately, this perspective may be given
further support by long lag times between implementation of nonpoint source
controls and observable water quality improvements, leading to skepticism that
the required pollutant load reductions will have any effect.
For example, Falls Reservoir in North Carolina has a TMDL
mandating a 77% reduction in phosphorus loading to attain the 40 ug/l
chlorophyll a water quality criterion. Given the preponderance of
nonpoint sources of phosphorus in the Falls Reservoir watershed, a 77%
phosphorus load reduction is not feasible; even if it were, the cost of
attainment almost certainly will far exceed the benefits derived for designated
use. Given that situation, Falls Reservoir is in need of a Use Attainability
Analysis (which determines if a designated use is technologically and economically
feasible) or new site-specific nutrient criteria.
I believe that realistic and achievable water quality
standards, with designated use (e.g., recreational fishing) improvements that
is causally-linked to attainment of water quality criteria (e.g., chlorophyll a),
are needed to gain widespread support for pollutant controls for water quality
improvements. In Falls Reservoir, the backlash against the high cost of
phosphorus load reductions has resulted in a state-sponsored plan for in-lake
artificial mixing (using SolarBees). This is a waste of money, as whole-lake
mixing is not feasible due to the large size of Falls Reservoir, and in-lake
mixing will have little effect on nutrient concentrations. While I do not
believe that water column mixing in Falls Reservoir is
scientifically-defensible, I do understand that local and state elected
officials may feel desperate enough to embrace even ineffective “solutions” in
the hope of reducing pollutant control costs for their constituents.
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