This was printed today in the
Raleigh News & Observer as an Op-Ed piece. This is our scientific
perspective on a contentious debate currently occurring in the North Carolina
legislature. Oversimplifying but still reasonably accurate, this debate pits an
upstream pro-development community against a downstream environmental
community. From a science and regulatory perspective, it raises issues
concerning watershed pollutant reduction activities and/or in-lake treatment
techniques to attain water quality goals. It also implicitly addresses the TMDL
issue of “pollutants” (e.g., phosphorus and nitrogen) versus “pollution” (e.g.,
actions within a waterbody to improve water quality).
Kenneth H. Reckhow, Professor Emeritus, Nicholas School of the
Environment, Duke University
Michael D. Aitken, Professor and Chair, Department of
Environmental Sciences and Engineering, Gillings
School of Global Public Health, University of North Carolina at Chapel Hill
Even at the planning stages for the two large Corps of
Engineers reservoirs (Jordan Lake and Falls Lake) in the Triangle area, water
scientists in North Carolina understood that they would have great difficulty
complying with water quality standards. This has proven to be true, as both
reservoirs are in violation of the North Carolina water quality standard for
chlorophyll a and are now subject to substantial reductions in nutrient
(phosphorus and nitrogen) loading. Achieving compliance with this water quality
standard is estimated to cost hundreds of millions of dollars, so it is
understandable that questions are being raised about the wisdom and
effectiveness of costly nutrient control measures.
All states are mandated by the federal government to set
water quality standards for their surface water bodies, which North Carolina
has done, and they conduct water quality monitoring programs to assess
compliance with standards. If a water body is found to be out of compliance,
which is the case for both Jordan and Falls Lakes, then the state must develop
a plan (often in the form of a Total Maximum Daily Load, or TMDL) that
describes what management actions will be implemented to achieve compliance. These
TMDL plans have been developed for Jordan and Falls Lakes and are in the early
stages of implementation by the watershed jurisdictions.
It has recently been suggested that the nutrient management
actions implemented in the Jordan Lake watershed are having no discernible
impact on Jordan Lake. In the minds of some individuals, this conclusion leads
to the recommendation to abandon the Jordan Lake Rules (the agreed-upon plan to
implement nutrient control measures in the watershed) and instead implement
in-lake technologies to improve water quality in Jordan Lake. There are at
least two fundamental errors in these perspectives.
First, even if all required nutrient management actions were
implemented on the day that the Jordan Rules were approved, it would take years
for a large water body like Jordan Lake to respond to reductions in pollutant
inputs. The actual implementation of pollutant controls, which includes time to
put management actions in place, requires additional time for the impact of
these actions to be observable in the lake. One of us (Reckhow) recently
chaired the National Academy of Sciences review of the Chesapeake Bay water
quality program. A point emphasized in this review was that the public needs to
be patient concerning the time required for improvements in water quality in
the Bay. For example, people should not expect that implementation of stormwater
detention basins in their neighborhoods would quickly result in observable
water quality improvements in the Bay. We cautioned that several years, even a
decade, might be necessary to see the improvements. However, we also recognized
that if the jurisdictions in the Chesapeake watershed maintained their nutrient
management implementation schedule, ultimately they would see the improvements
that they expected.
Second, there are no technologies, new or old, that can
provide any meaningful level of cleanup of algae in a lake the size of Jordan. In-lake
techniques to improve water quality, such as harvesting, aeration, and algaecides,
can be effective in ponds (or, at best, in small lakes), but they are not
intended for large waterbodies. Further, there is no evidence that these
techniques will result in compliance with the chlorophyll a criterion in
Jordan Lake.
We are both engineers with great faith that many of today’s
problems can be solved through technology. But we do not subscribe to blind
faith in technology to correct preventable problems. A first principle of
responsible stewardship for any public water supply is to protect the watershed. There are viable, proven means of reducing inputs
of nutrients and other pollutants to reservoirs that are embodied in the Jordan
and Falls Lake Rules. These inputs will only increase as the affected
communities and municipalities grow if appropriate watershed management plans
are not in place. And, standard engineering practice before implementing any
proposed new technology is to evaluate it thoroughly, in context and at a
relevant scale, especially when the consequences of failure have implications
for public health.
The nutrient management plans for Falls and Jordan Lakes
have been based on sound scientific analysis and active stakeholder
involvement. For Falls Lake, to further ensure that a deliberative process
continues, a careful re-examination and refinement of the modeling and
assessment that resulted in the Falls Lake Rules is in progress. In our view,
this adaptive management approach is a far more prudent strategy for effective
management of lakes than is the hasty and ill-conceived abandonment of the
Jordan Lake Rules that is currently under consideration by the General Assembly.
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