Project
Proposals for 2006-2007 DWRC Undergraduate Internships
EIGHT as of
1. Measuring
groundwater discharge to the Inland Bays (posted
2. Sustainable
Mosquito Control for Stormwater Ponds (posted
3. Lewes Citizen Monitoring Program, Broadkill
Watershed Tributary Team, and Delaware NEMO Program (posted
4. Water Uptake and Sulfur Metabolism in Plants
–
5. Influence of land use and management on runoff and
water quality patterns in the Cool Run tributary watershed, Newark, Delaware. (posted
6. Baseline assessment of water quality and
identification of sources of pollution for the Noxontown Pond, Middletown,
Delaware. (posted
7. Influences of riparian and wetland areas on
runoff and stream chemistry patterns across catchment scales (posted
8. Baseline assessment of water quality in relation
to salt marsh breeding birds at Woodland Beech, Delaware (posted
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1. Measuring groundwater discharge to the
Inland Bays (posted
Interested in this internship?
Contact Dr. Bill Ullman ullman@udel.edu, (302) 645-4302 FAX:
(302) 645-4007,
Or Doug Miller dmiller@udel.edu
for more information.
Project description:
This DWRC undergraduate
student intern will work with Dr. Ullman and Dr. Miller to determine rates of
submarine groundwater discharge to shallow sub-tidal areas of the Inland Bays
using thermal and salinity data. The
student should have some background in hydrology, oceanography, or
environmental sciences and good mathematical and computer skills.
We will use simple samplers to look at temperature and salinity
gradients at Oak Orchard on the north side of
The student will
also have the opportunity to collect other types of samples to relate these
groundwater discharge measurements to biological and chemical processes
occurring at the sites of discharge.
Housing: The student would be eligible for dormitory
housing at
2. Sustainable
Mosquito Control for Stormwater Ponds
Interested in this internship?
Contact Dr. Jack B. Gingrich gingrich@udel.edu, (302) 831-1308,
University of
Introduction
Stormwater ponds (BMP’s) have been shown to be an important breeding habitat for mosquitoes, including both nuisance species and West Nile (WN) virus vectors (Gingrich et al., 2006). Moreover, over the past two years, important new information has been developed by Gingrich et al. (unpublished Annual Report to DELDOT, 2005) that distinguishes among types of ponds that produce mosquitoes in large numbers and those that do not. Detention ponds, especially extended detention ponds, often do not drain within the 72-hour period that they were designed for. Instead they often take 10-14 days or longer to dry out, which is more than ample time for a brood of mosquitoes to emerge. When they do dry out, wet mud around the periphery of these ponds become the targets for oviposition by floodwater mosquitoes of the Aedes group of mosquitoes, which include several potential WN vector species. Also, certain categories of retention ponds, especially shaded ponds with shallow perimeters, become breeding sites for numerous mosquito species, including Culex and Aedes group members. These ponds develop heavy and dense vegetation that in turn provide good protection and food sources for larval mosquitoes.
Although it appears that detention ponds may be limited in the future, shallow retention ponds appear to be here to stay, for a number of reasons. For those ponds that are likely to breed high numbers of mosquitoes on a yearly basis, the choice is to continually apply pesticides, or find an alternative solution to reduce mosquito abundance. It would be preferable to find a low-impact, sustainable method to reduce mosquito abundance that takes account of what we know about mosquito biology and behavior.
In 2005, we found that our aluminum phosphate treatment,
designed to limit availability of phosphates, may be differentially curtailing
development by several of our most important
Proposed Tests for
2006
As a result, the following approaches are proposed for 2006:
1) Reduce the amount of orthophosphate using aluminum sulfate (alum) to prevent the growth of algae and bacteria;
2) Measure bacteria levels, phosphate levels, and chlorophyll A levels to determine how and what alum addition is impacting. We would use at least 10 ponds in each of two groups, controls and alum treatments.
3) Measure abundance of mosquitoes in at least 10 ponds treated with alum and 10 left as controls.
4) Measure impacts of alum treatments in the lab on mosquito development using treatment levels comparable to what is used in the field, as well as a 2X and 4X concentration.
5) Identify and count mosquito species in each field and lab study. Determine proportions of vector and non-vector species in each pond.
Specifically, the following measurements would be taken on a biweekly basis from June to September:
1) Number and species of larvae per dip based on 20 dips per subsite, with 5 subsites per pond
2) Numbers and types of invertebrate predators (based on numbers per 20 dips)
3) Percent shade reduction by vegetation (lux read at water surface)
4) Three dominant vegetation types at the subsites and the percent of surface occupied
5) pH
6) Conductivity
7) Temperature
8) Orthophosphate concentration
9) Chlorophyll a concentration
10) Total bacteria per subsite based on slides stained for epifluorescence microscopy.
Expected Results
Data would be entered into an automated Access database, with all the information from 9 biweekly site collections plus all field site characteristics included. Success of the treatment method would be evaluated based on mosquito abundance reduction, ease of treatment, and overall cost to implement the treatment. Lab results and field results are expected to back each other up and support the use of alum to reduce mosquito development, particularly of important nuisance and vector species, without adversely impacting the overall levels of non-vector species and predators. Controls and treatment groups would be analyzed by stepwise multiple regression and paired t-tests. Results will be presented in both tables and graphs. Also, descriptive statistics (mean larvae per dip) and standard errors will be used in depicting graphs to be compared.
References
Gingrich, J.B., R.D.
Anderson, G. M. Williams, L.L. O’Connor, and K.H. Harkins. 2006. Stormwater ponds, constructed wetlands,
and other BMP’s as potential breeding sites for
Peck, G.W. and W.E. Walton. 2006. Effect of bacterial quality and density on growth and whole body stoichiometry on Culex quinquefasciatus and Cx. tarsalis (Diptera: Culicidae). J. Med. Entomol. 43(1): 25-33.
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3. Lewes
Citizen Monitoring Program, Broadkill Watershed Tributary Team, and
We have opportunities for internships with our Citizen Monitoring Program, Broadkill Watershed Tributary Team, and Delaware NEMO Program for students having interest in outreach education and some applied research while living down at the beach. We could probably find them student housing in a UD dorm.
Please contact Joe Farrell jfarrell@udel.edu to discuss. (302) 645-4250
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4. Water
Uptake and Sulfur Metabolism in Plants –
Interested in this internship?
Contact Dr. Cyril Broderick cbroderi@desu.edu (302) 857-6416,
Water remains a critical resource for all life, and its bulk is in the external environment. Its availability and use in organisms is however critical to all living systems. Plants are a group of organisms that rely on the availability of water from watersheds, dams, and a variety of different sources, and most metabolically active plant organs maintain water contents of around 90 percent of their total weight. Water is hence intrinsically important to all plants. Sulfur is also of particular interest, because it is regarded as the fourth most abundant among required elements in plants. The question is: Would sulfur supply or deficiency affect plant growth and water uptake in plants, especially fast-growing horticultural species? Methods proposed would be based on hydroponic sand culture and microscopic analysis of changes in plant tissue structure, texture, growth and development. Data would include measures of changes in mass, osmosis, turgor, plasmolysis, as well as data on physical changes in membranes and tissues of the plant organs studied. Preliminary studies conducted with Abelmoschus/Hibiscus esculentus (okra) are encouraging. In addition to okra, several species of the Mustard family (Cruciferae) and Nightshade family (Solanaceae) shall be used in the study.
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The following two internships are proposed by a team of 3
UD advisors. These (and #7) require some
field monitoring and some GIS work and are part of bigger projects.
5. (#1 of 2) Influence of land use and management on runoff and water quality
patterns in the Cool Run tributary watershed,
Interested in this internship?
Contact Dr. Shreeram Inamdar inamdar@udel.edu (302) 831- 8877
Or the co-advisors:
Dr. J. Thomas Sims jtsims@udel.edu (302) 831-2698
Jenny McDermott mott@udel.edu (302) 831-1389
The Cool Run creek a tributary of the White Clay creek
drains two different portions of the
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6. (#2 of 2) Baseline assessment of water quality and identification of
sources of pollution for the Noxontown Pond,
Interested in this internship?
Contact Dr. Shreeram Inamdar inamdar@udel.edu (302) 831- 8877
Or the co-advisors:
Dr. J. Thomas Sims jtsims@udel.edu (302) 831-2698
Jenny McDermott mott@udel.edu (302) 831-1389
The Noxontown Pond located on
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7.
Influences of riparian and wetland areas on runoff and stream chemistry
patterns across catchment scales
(posted 3/15/06) This requires some field monitoring and some GIS
work and is part of a bigger project.
Interested in this internship?
Contact Dr. Shreeram Inamdar inamdar@udel.edu (302) 831- 8877
How does runoff chemistry vary with increasing catchment
size? How do hydrologic flow paths shift
with increase in catchment size? Does the change in areal extent and spatial
distribution of wetland/riparian areas with catchment size influence stream
chemistry? These are some of the important questions that are at the forefront
of research in hydrologic sciences. We
will study these questions across three catchments of 1, 10, and 150 ha area in
the Fair Hill preserve in
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8. Baseline
assessment of water quality in relation to salt marsh breeding birds at
Woodland Beech,
Interested in this internship?
Contact Dr. Greg Shriver gshriver@udel.edu (302) 831-1300
Contact Dr. Shreeram Inamdar inamdar@udel.edu (302) 831- 8877
As part of a breeding ecology study of tidal marsh passerine
birds, this project will provide the initial assessment of water chemistry
within the breeding areas for two obligate marsh species. The internship would provide avian sampling
experience, including mist-netting, color banding, nest
searching, and avian inventories as well as an opportunity to establish the
baseline assessment of water chemistry in relation to avian breeding
ecology. Basic water chemistry data (DO,
pH, salinity) will be collected at permanent sites throughout the tidal wetland
during the breeding season (May-August).
We will also collect water level depth using peizometers
(shallow ground water wells). All
sampling locations will be permanently marked using GPS and integrated into a
multi-layer GIS for spatial analyses.