New Publication:
Increasing Precision of Turbidity-based Suspended Sediment
Concentration and Load Estimates.

Turbidity is an effective tool
for estimating and monitoring suspended sediments in aquatic
systems. Turbidity can be measured in situ remotely and at fine
temporal scales as a surrogate for suspended sediment
concentration (SSC), providing opportunity for a more complete
record of SSC than is possible with physical sampling
approaches. However, there is variability in turbidity-based SSC
estimates and in sediment loadings calculated from those
estimates. This study investigated the potential to improve
turbidity-based SSC, and by extension the resulting sediment
loading estimates, by incorporating hydrologic variables that
can be monitored remotely and continuously (typically 15-min
intervals) into the SSC estimation procedure. On the Roanoke
River in southwestern Virginia, hydrologic stage, turbidity, and
other water-quality parameters were monitored with in situ
instrumentation; suspended sediments were sampled manually
during elevated turbidity events; samples were analyzed for SSC
and physical properties including particle-size distribution and
organic C content; and rainfall was quantified by geologic
source area. The study identified physical properties of the
suspended-sediment samples that contribute to SSC estimation
variance and hydrologic variables that explained variability of
those physical properties.
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New Publication:
Effects of Groundwater-Flow Paths on Nitrate Concentrations Across
Two Riparian Forest Corridors.

Groundwater levels, apparent age, and chemistry
from field sites and groundwater-flow modeling of hypothetical
aquifers collectively indicate that groundwater-flow paths
contribute to differences in nitrate concentrations across
riparian corridors. At sites in Virginia (one coastal and one
Piedmont), lowland forested wetlands separate upland fields from
nearby surface waters (an estuary and a stream). At the coastal
site, nitrate concentrations near the water table decreased from
more than 10 mg⁄ l beneath fields to 2 mg ⁄ l beneath a riparian
forest buffer because recharge through the buffer forced water
with concentrations greater than 5 mg⁄l to flow deeper beneath
the buffer. Diurnal changes in groundwater levels up to 0.25
meters at the coastal site reflect flow from the water table
into unsaturated soil where roots remove water and nitrate
dissolved in it. Decreases in aquifer thickness caused by
declines in the water table and decreases in horizontal
hydraulic gradients from the uplands to the wetlands indicate
that more than 95% of the groundwater discharged to the
wetlands. Such discharge through organic soil can reduce nitrate
concentrations by denitrification. Model simulations are
consistent with field results, showing downward flow approaching
toe slopes and surface waters to which groundwater discharges.
These effects show the importance of buffer placement over use
of fixed-width, streamside buffers to control nitrate
concentrations.
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