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Effects of Biosolids on Water Quality
Title: Effects of Biosolids on Water Quality
Principle Investigators: William H. McDowell, Tamara Chestnut
With increasing population density in the state of NH, production
of biosolids (solid waste including sludge from municipal sewage
treatment, food processing wastes, and sludge generated by treatment
of paper mill wastes) has increased dramatically. At the same time
that generation has increased, options for disposal have diminished
and disposal costs have increased. One option for disposal of this
waste stream is use of biosolids as a soil amendment to re-vegetate
abandoned gravel pits. Abandoned gravel pits are numerous in New
Hampshire, and lack of vegetation decreases property values adjacent
to a site as well as providing a threat to water quality.
The proposed research will examine the impacts of gravel pit restoration
with biosolids on groundwater quality. A field demonstration site
has been established at a former gravel pit in Hooksett, NH. Current
use of the site involves periodic application of biosolids, growth
of a cover crop for several years to create a soil cover, and then
removal of the created topsoil for use by the town of Hooksett in
management of public lands and road rights-of-way. Matching funds
will be provided by the state of NH and a private organization, the
New England Biosolids and Residuals Association (NEBRA).
Previous research from this project in 1996 has shown that nitrate
(NO3) concentrations in soil solution are high at some sites, but
groundwater appears to be relatively unaffected by biosolids applications
(2 - 4 mg/L NO3). The primary goal of the project is to demonstrate
whether adherence to Best Management Practices (BMPs) is sufficient
to protect groundwater from contamination with NO3 and other forms
of dissolved nitrogen, and identify possible ways to improve BMPs.
Funding from the WRRC will be used to 1) increase sample frequency
to provide better temporal resolution in groundwater chemistry; 2)
install several recording pressure transducers that monitor changes
in groundwater table in response to rain events, and 3) assess impacts
of biosolids application on trace metal levels in groundwater.
Flow injection analysis will be used to measure ammonium (phenol
hypochlorite method) and nitrate (Cd Cu reduction method). Dissolved
organic nitrogen (DON) will be measured as the difference between
total dissolved N (using high temperature catalytic oxidation and
chemiluminescent NO detection (Merriam et al. 1996) and inorganic
nitrogen. Trace metals will be measured using inductively couple
plasma emission spectroscopy (ICP). Analyses will be conducted in
the WRRC's Water Quality Analysis Lab with the exception of trace
metal analysis, which will be conducted in the Plant and Soil Testing
lab at UNH.
View the final report to NH DES and
NH State Legislature (.pdf file)

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