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Evaluating the effect of the Clean Air Act on lake and stream
chemistry in the northeastern US
Project Summary
Objectives
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The proposed research is part of the University of Maine’s program
to address scientific uncertainty relating to surface water and
watershed acidification. Our goals and methods are hierarchical,
ranging from site-specific data to regional statistical surveys.
The objectives are to:
-
determine
the changes and trends in aquatic chemistry for defined
sub-populations and sites that are known to be susceptible to
acidification or recovery,
-
evaluate the
relationships between surface water and precipitation chemistry
using site specific deposition data, and regional NADP data, and
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characterize the effectiveness of
the Clean Air Act (and amendments) in meeting its goals of
reducing acidification of surface waters and improving
biologically-relevant chemistry in the northeastern US.
Approach -
The schedule of tasks ranges from weekly to annual. We will
evaluate chemistry on a weekly basis year-round at the small
watershed-scale at BBWM, weekly during the spring melt period at
RLTM lakes outlets, quarterly in LTM and RLTM lakes, and during an
annual index period for the HELM and TIME lakes. The specific
tasks are to:
-
examine the
patterns of acidification and recovery in the experimental
watershed project at the Bear Brook Watershed in Maine (BBWM),
originally part of the EPA Watershed Manipulation Project,
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continue the
17 year chemistry record for selected lakes in Maine which were
part of the original EPA Long Term Monitoring Program (LTM),
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expand the
scope of LTM using the EPA Regionalized Long Term Monitoring
Lakes which have a broader distribution of chemistry to match
the regional chemical characteristics,
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provide an
estimate of seasonal chemical extremes that occur in these RLTM
lakes,
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re-sample a
subset of the high elevation lakes, surveys of which in 1986-88
revealed the most acidified lakes in Maine, and
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provide a statistical regional
estimate of chemical changes using lakes in the EPA Temporally
Integrated Monitoring of Ecosystems (TIME) program in New
England and the Adirondack region.
The annual
schedule and scope of work is summarized below:
|
|
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Jan |
Feb |
Mar |
Apr |
Mar |
Jun |
# samp. |
|
TIME lakes
(75x1) |
x |
x |
|
|
|
|
|
|
|
|
|
|
75 |
|
RLTM: |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
spring outlets
(9x5) |
|
|
|
|
|
|
|
|
x |
x |
|
|
45 |
|
drainage
lakes (9x3) |
x |
x |
|
x |
x |
|
|
|
|
x |
x |
|
27 |
|
seepage
lakes (3x3) |
x |
|
|
x |
|
|
|
|
|
|
x |
|
9 |
|
LTM lakes
(3x1) |
|
|
|
|
x |
|
|
|
|
|
|
|
3 |
|
HELM lakes
(20x1) |
|
|
|
x |
|
|
|
|
|
|
|
|
20 |
|
BBWM streams
(2x50) |
weekly
sampling -> |
|
|
|
|
|
|
|
|
|
100 |
|
Annual report |
|
|
|
|
|
|
|
|
|
x |
|
|
279 |
These project components provide a statistical
framework for inferring regional chemical patterns using TIME
and RLTM. The long term records of LTM, RLTM, HELM and BBWM
provide seasonal and annual variability data that defines long
term response.
Expected Results - This information is fundamental for federal agencies to meet the
Congressional mandate in the Clean Air Act Amendments (CAAA) to
ascertain trends in ecological response, and to determine the
effectiveness of the CAAA in influencing these trends. The highly
appropriate combination of site-specific data within the regional
context will provide for the recognition and understanding of
declining SO4, base cation depletion, and changes in
N-saturation or DOC contributions to acid-base status.
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