Bedoukian   RussellIPM   RussellIPM   Piezoelectric Micro-Sprayer


Home
Animal Taxa
Plant Taxa
Semiochemicals
Floral Compounds
Semiochemical Detail
Semiochemicals & Taxa
Synthesis
Control
Invasive spp.
References

Abstract

Guide

Alphascents
Pherobio
InsectScience
E-Econex
Counterpart-Semiochemicals
Print
Email to a Friend
Kindly Donate for The Pherobase

« Previous AbstractImpact of indoor surface material on perceived air quality    Next AbstractCharacterizing the chemical and sensory profiles of traditional American meads »

Environ Sci Technol


Title:Long-term fate of a pulse arsenic input to a eutrophic lake
Author(s):Senn DB; Gawel JE; Jay JA; Hemond HF; Durant JL;
Address:"Department of Environmental Health, Harvard School of Public Health, Boston, Massachusetts, USA. dbsenn@alum.mit.edu"
Journal Title:Environ Sci Technol
Year:2007
Volume:41
Issue:9
Page Number:3062 - 3068
DOI: 10.1021/es062444m
ISSN/ISBN:0013-936X (Print) 0013-936X (Linking)
Abstract:"The long-term fate of a 30-year-old pulse arsenic input to a eutrophic lake was studied to determine if As has become effectively trapped in sediments or remains in active exchange with the water column. Legacy As was readily mobilized from sediments of Spy Pond (Arlington, MA), a eutrophic kettle-hole lake that was treated with 1000s kg As in the 1960s to manage excessive aquatic macrophyte growth. Arsenic was mobilized from hypolimnetic sediments during bottom-water anoxia in spring, summer, and fall, and As accumulated to maximum concentrations of 2100 nM. Mobilization of As from epilimnetic sediments was the largest source of As to the water column on a mass basis (145 mol), despite the fact that the epilimnion remains oxic year-round. Sediment cores revealed that surficial sediments contained As at 30-50 times background levels and suggested that there is contemporary As loading to hypolimnetic sediments (590 mol y(-1)). Mass balance estimates indicate that <5% of the contemporary As load comes from external inputs and that the remainder can be explained by mobilization and redistribution of legacy As, both through the water column and by vertical migration of dissolved As within sediments. These findings demonstrate that, decades after As inputs cease, As in contaminated sediments may remain labile and be mobilized to both anoxic and oxic water columns and accumulate to levels near the sediment surface and in the water column that may pose ongoing risks to ecological health"
Keywords:"Arsenic/*analysis Eutrophication Fresh Water/analysis Geologic Sediments/*analysis Massachusetts Water Pollutants, Chemical/*analysis;"
Notes:"MedlineSenn, David B Gawel, James E Jay, Jennifer A Hemond, Harold F Durant, John L eng 5P42ES04675-06/ES/NIEHS NIH HHS/ Research Support, N.I.H., Extramural Research Support, Non-U.S. Gov't 2007/06/02 Environ Sci Technol. 2007 May 1; 41(9):3062-8. doi: 10.1021/es062444m"

 
Back to top
 
Citation: El-Sayed AM 2024. The Pherobase: Database of Pheromones and Semiochemicals. <http://www.pherobase.com>.
© 2003-2024 The Pherobase - Extensive Database of Pheromones and Semiochemicals. Ashraf M. El-Sayed.
Page created on 19-12-2024