Melcher_Project Description

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Jack Melcher
UEP-232
Assignment #6
Relating impervious areas in eastern Massachusetts to declines in
water quality as indicated by shellfish bed closings and barren
eelgrass habitats.
Background
As the urbanized area of eastern Massachusetts has expanded, ever more roadways
and parking lots have been installed. Industrial operations, land use activities, fallout of air
pollutants, roadway usage and other activities contribute to the loading of particulates on
urban roadways. These materials are then carried into receiving waters by storm runoff
where they constitute a substantial portion of the overall water pollution problems of
cities. Although many pollutants are contained in stormwater, many are difficult or
expensive to test for in environmental concentrations. The presence of excessive nutrients
such as phosphorus and nitrogen, for example, is much more easily gauged by its effect on
ecosystems. Over-enriched waters will exhibit excess algae growth, decreasing water
clarity and potentially producing dangerous neurotoxins. The cloudiness of the water
blocks light from reaching the eelgrass, eliminating habitat. Shellfish beds must be closed
when harmful algal blooms will make shellfish poisonous to humans.
Objectives

Are watersheds with a high percentage of impervious area less likely to have
approved shellfish beds?

Are watersheds with a high percentage of impervious area less likely to have intact
eelgrass habitats?
Methodology
This study will focus on the area of coastal Massachusetts between Cape Ann and
the Merrimack River. There are very small basins such Walker Creek, Saginese Creek, and
Labor in Vain Creek; small river basins such as the Parker River, Rowley River, Essex River,
Walker Creek; and the medium-sized Ipswich River in this area. Watershed delineation
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Jack Melcher
UEP-232
Assignment #6
tools that I have not learned yet will be used to draw basins. Impervious area obtained
through remote sensing will be obtained from MassGIS. It is possible that I will want to
investigate habitat impacts by land use as well as simply impervious area. I could come up
with a weighting system that assumes certain land uses that may not have large impervious
areas (such as agricultural areas or golf courses), may have impacts on water quality. I
would love to show areas by census block that have a majority wastewater treatment
through on-site septic systems, but I was not able to find this information in my
Assignment #3.
Overlay tools will be used to highlight near-coastal areas that have potentially been
impacted from anthropogenic changes to water quality. MassGIS maps shellfish suitability
areas delineating potential habitat areas for a variety of shellfish: American Oyster
Bay Scallop, Blue Mussel, European Oyster, Ocean Quahog, Quahog, Razor Clam, Sea Scallop,
Soft-shelled Clam, and Surf Clam. Out of these potential shellfish areas I can highlight areas
that have been designated as approved or prohibited by the Division of Marine Fisheries.
The most useful near-coastal area will be estuaries and bays that are served by distinct
river basins.
Data Sources
Data Layer
Available
from
Scale of source data
Vintage of source
data
Designated shellfish
growing areas
MassGIS
1:5,000
Sep. 2009
Shellfish suitability areas
MassGIS
???
Nov. 2008
DEP Eelgrass
MassGIS
1:20,000
2001
Impervious surface
MassGIS
1-meter pixels
2005
Digital Elevation Model
(5K)
MassGIS
1:5,000
???
Land Use 2005
MassGIS
1-acre minimum
mapping unit
2005
The limiting factor for very small watersheds may be the DEM, in the very flat coastal plain.
Also, manmade diversions (such as storm sewers) will not be included, so all analysis
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Jack Melcher
UEP-232
Assignment #6
should be on a somewhat large scale. As I encountered in Assignment #5, Land Use
polygons are sometimes large, but now I know that tools are available to clip them as is
necessary.
Works Cited
Bowen, J. L, and I. Valiela. "The ecological effects of urbanization of coastal watersheds:
historical increases in nitrogen loads and eutrophication of Waquoit Bay estuaries."
Canadian Journal of Fisheries and Aquatic Science, 2001.
Historical changes in land use on coastal watersheds have increased rates of land-derived
nitrogen loading to estuaries and altered their biogeochemistry and food webs. We used
information on human populations and land uses within the watershed of Waquoit Bay,
Cape Cod, Massachusetts, U.S.A., to model how nitrogen loads derived from atmospheric
deposition, fertilizer use, and wastewater disposal have changed since the 1930s. Nitrogen
loading into Waquoit Bay more than doubled between 1938 and 1990. The predominant
source of nitrogen added to the bay changed from atmospheric deposition to wastewater
disposal during the 1980s, reflecting the increasing urbanization of Cape Cod. Larger
nitrogen loads increased nitrogen concentrations in the water, altering the assemblage of
primary producers and resulting in eutrophication of the estuary. Biomass of
phytoplankton and macroalgae increased, and areal cover of eelgrass (Zostera marina)
decreased, with increasing nitrogen load. An increase in nitrogen load from 15 to 30 kg
N.ha(-1).year(-1) virtually eliminated eelgrass meadows. Land-use changes prompted by
urban sprawl can therefore be linked to marked changes in water quality and
eutrophication of receiving waters.
Impact of Urban Sprawl on Water Quality in Eastern Massachusetts, USA
Jun Tu, Zong-Guo Xia, Keith C. Clarke, Allan Frei
Environ Manage (2007) 40:183–200
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Jack Melcher
UEP-232
Assignment #6
A study of water quality, land use, and population variations over the past three decades
was conducted in eastern Massachusetts to examine the impact of urban sprawl on water
quality using geographic information system and statistical analyses. Since 1970, eastern
Massachusetts has experienced pronounced urban sprawl, which has a substantial impact
on water quality. High spatial correlations are found between water quality indicators
(especially specific conductance, dissolved ions, including Ca, Mg, Na, and Cl, and dissolved
solid) and urban sprawl indicators. Urbanized watersheds with high population density,
high percentage of developed land use, and low per capita developed land use tended to
have high concentrations of water pollutants. The impact of urban sprawl also shows clear
spatial difference between suburban areas and central cities: The central cities experienced
lower increases over time in specific conductance concentration, compared to suburban
and rural areas. The impact of urban sprawl on water quality is attributed to the combined
effects of population and land-use change. Per capita developed land use is a very
important indicator for studying the impact of urban sprawl and improving land use and
watershed management, because inclusion of this indicator can better explain the temporal
and spatial variations of more water quality parameters than using individual land use
or/and population density.
Jump Run Creek Shellfish Restoration Project
White, NM. Journal of Shellfish Research. v. 19. no. 1. 2000. p. 473 - 476.
The objective of this multi-agency project is to 1) quantify the effects of land use change on
shellfish closures and 2) assess techniques that can be used mitigate those impacts. This
report is based on preliminary analyses conducted over the last 18 months. The project
focuses on the 320-ha watershed in Carteret County, North Carolina, that is the drainage
for Jump Run Creek. Bacterial data from 1970 through 1998 indicate increased loading
since 1974, which is when closure management began. Recent grab sample data from the
tributaries indicate high levels of bacteria during storm events and moderate levels during
dry weather. The majority of the lending is coming from the portion of the watershed
draining an older, medium density neighborhood (single family houses and a trailer park. A
door-to-door survey found two malfunctioning septic systems, more than 100 pets, and the
presence of wildlife. Change analysis of land use/land cover shows hydrologic
modifications were instituted in the 1970s. Dye studies confirm that water moves through
the watershed in hours, indicating that lime for bacterial mortality is insignificant. Future
analyses include ground water sampling, automated storm water monitoring, and DNA
tracking of fecal sources. Planned mitigation practices will include riparian buffer
restoration, stormwater wetland, bio-retention, pent filters, and education. Locations and
sizing of practices will be determined through GIS-based hydrologic analysis of the
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Jack Melcher
UEP-232
Assignment #6
watershed in conjunction with a community-design/educational approach involving
neighborhood citizens.
S. R. Carpenter, N. F. Caraco, D. L. Correll, R. W. Howarth, A. N. Sharpley, V. H. Smith
(1998) NONPOINT POLLUTION OF SURFACE WATERS WITH PHOSPHORUS AND
NITROGEN. Ecological Applications: Vol. 8, No. 3, pp. 559-568.
doi: 10.1890/1051-0761(1998)008[0559:NPOSWW]2.0.CO;2
Agriculture and urban activities are major sources of phosphorus and nitrogen to aquatic
ecosystems. Atmospheric deposition further contributes as a source of N. These nonpoint inputs
of nutrients are difficult to measure and regulate because they derive from activities dispersed
over wide areas of land and are variable in time due to effects of weather. In aquatic ecosystems,
these nutrients cause diverse problems such as toxic algal blooms, loss of oxygen, fish kills, loss
of biodiversity (including species important for commerce and recreation), loss of aquatic plant
beds and coral reefs, and other problems. Nutrient enrichment seriously degrades aquatic
ecosystems and impairs the use of water for drinking, industry, agriculture, recreation, and other
purposes.
Based on our review of the scientific literature, we are certain that (1) eutrophication is a
widespread problem in rivers, lakes, estuaries, and coastal oceans, caused by over-enrichment
with P and N; (2) nonpoint pollution, a major source of P and N to surface waters of the United
States, results primarily from agriculture and urban activity, including industry; (3) inputs of P
and N to agriculture in the form of fertilizers exceed outputs in produce in the United States and
many other nations; (4) nutrient flows to aquatic ecosystems are directly related to animal
stocking densities, and under high livestock densities, manure production exceeds the needs of
crops to which the manure is applied; (5) excess fertilization and manure production cause a P
surplus to accumulate in soil, some of which is transported to aquatic ecosystems; and (6) excess
fertilization and manure production on agricultural lands create surplus N, which is mobile in
many soils and often leaches to downstream aquatic ecosystems, and which can also volatilize to
the atmosphere, redepositing elsewhere and eventually reaching aquatic ecosystems.
If current practices continue, nonpoint pollution of surface waters is virtually certain to increase
in the future. Such an outcome is not inevitable, however, because a number of technologies,
land use practices, and conservation measures are capable of decreasing the flow of nonpoint P
and N into surface waters.
From our review of the available scientific information, we are confident that: (1) nonpoint
pollution of surface waters with P and N could be reduced by reducing surplus nutrient flows in
agricultural systems and processes, reducing agricultural and urban runoff by diverse methods,
and reducing N emissions from fossil fuel burning; and (2) eutrophication can be reversed by
decreasing input rates of P and N to aquatic ecosystems, but rates of recovery are highly variable
among water bodies. Often, the eutrophic state is persistent, and recovery is slow.
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