7 research outputs found

    Selected Hydrogeologic and Water-quality Data from Jones Beach Island, Long Island, New York

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    A data-collection site was instrumented on Jones Beach Island, a barrier island south of Long Island, N.Y., to study local freshwater/ saltwater relations in the shallow ground-water system. A geologic test boring revealed about 88 feet of well-sorted glacial outwash sand above about 15 feet of Gardiners Clay, which directly overlies silty sand of the Magothy Formation. Tidal effects on water levels in Great South Bay, the upper glacial aquifer, and the Magothy aquifer were observed and quantified with a tidal gage in the bay and analog water-level recorders in the wells.Chloride concentrations in the upper Magothy aquifer were higher than expected--about 270 mg/L (milligrams per liter), and those in the upper glacial aquifer were 17,000 to 19,000 mg/L, about the same as in Great South Bay. Estimates of pressure and freshwater equivalent heads indicate that, at the data-collection site, freshwater is discharging upward from the Magothy aquifer into the salty upper glacial aquifer, but dilution by this freshwater is undetectable. The reason for the elevated chloride concentration in the Magothy aquifer cannot be determined from available hydrogeologic information

    Urbanization and recharge in the vicinity of East Meadow Brook, Nassau County, New York.

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    Shipping list no.: 97-0078-P."Prepared in cooperation with the Nassau County Department of Health"--Cover.Includes bibliographical references (p. 38-39).Mode of access: Internet

    Stratigraphy and hydrologic conditions at the Brookhaven National Laboratory and vicinity, Suffolk County, New York, 1994-97 /

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    "Prepared in cooperation with the Brookhaven National Laboratory, and U.S. Department of Energy."Includes bibliographical references (p. 46-48).Mode of access: Internet

    Urbanization and recharge in the vicinity of East Meadow Brook, Nassau County, New York.

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    Shipping list no.: 97-0289-P.Includes bibliographical references (p. 34-35).Mode of access: Internet

    Estimates of nitrogen loads entering Long Island Sound from ground water and streams on Long Island, New York, 1985-96 /

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    Shipping list no.: 2001-0276-P."Prepared in cooperation with New York State Department of Environmental Conservation and U.S. Environmental Protection Agency."Includes bibliographical references (p. 28-29).Mode of access: Internet

    Selected hydrogeologic and water-quality data from Jones Beach Island, Long Island, New York /

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    Shipping list no.: 95-0079-P.Cover title: Hydrogeology of Jones Beach, Long Island, New York, with selected water-quality data.Includes bibliographical references (p. 20-21).Mode of access: Internet

    The Peconic River: Concerns associated with different risk evaluations for fish consumption

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    Risk evaluation and assessment have been used as tools to regulate and manage the risks to consumers of eating self-caught fish that have high levels of contaminants. Armed with these risk assessments, health agencies issue consumption advisories, and in some cases, close some waters to fishing. Recently, regulatory agencies have used contaminant levels in fish as a benchmark for remedial action on contaminated sites, using human health risk assessment as the justification. The US Environmental Protection Agency's new surface water criterion for mercury is based on mercury levels in fish tissue. When multiple regulatory agencies have jurisdiction over the same waters or remediation site there is the potential for differing risk evaluations. Using the Peconic River on Long Island, New York as a case study, the paper examines how and why county, state, and federal health risk evaluations for fish contaminated with mercury differed. While the same risk methodology was applied by all agencies, the assessments were conducted for different purposes, applied different consumption and fish biomass assumptions, and arrived at different conclusions. The risk evaluations invoked to design fish consumption advisories use mercury levels currently in fish, and are designed to prevent current exposure. However, the risk assessments that provide a basis for remediation consider many different pathways of exposure (not just ingestion), and deal with long-term exposure. The risk evaluations, and recommendations promulgated by those agencies, differ because they have different goals, use different assumptions, and often fail to communicate among agencies. It is suggested that it is valuable to have these different levels of risk evaluations to adequately address health issues. However, there are policy implications, which include making the distinctions between the types of risk assessments, their methods and assumptions, and the rationale for these assumptions. Further, assessors and managers should involve all interested stakeholders (including regulators and state health officials) in discussions about the use of risk, the assumptions of risk assessment, and the goals of those evaluations. The difficulties in the case of the Peconic were not due to differences in the original data, but rather in the goals and type of risk assessments performed. If all deliberations had been transparent during all phases of the decision-making and management process, the conflicts within the minds of the public, regulators and other agencies might have been avoided. This case study suggests that more reliability, circumspection and transparency should be built into the process where multiple agencies and multiple objectives are involved.
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