Toxicity of nano-zero valent iron to freshwater and marine organisms.

We tested whether three commercial forms (uncoated, organic coating, and iron oxide coating) of nano zero-valent iron (nZVI) are toxic to freshwater and marine organisms, specifically three species of marine phytoplankton, one species of freshwater phytoplankton, and a freshwater zooplankton species...

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Main Authors: Arturo A Keller, Kendra Garner, Robert J Miller, Hunter S Lenihan
Format: Article
Language:English
Published: Public Library of Science (PLoS) 2012-01-01
Series:PLoS ONE
Online Access:http://europepmc.org/articles/PMC3431385?pdf=render
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spelling doaj-2e657c64aa694c52af03d60f4dfd05682020-11-25T02:42:27ZengPublic Library of Science (PLoS)PLoS ONE1932-62032012-01-0178e4398310.1371/journal.pone.0043983Toxicity of nano-zero valent iron to freshwater and marine organisms.Arturo A KellerKendra GarnerRobert J MillerHunter S LenihanWe tested whether three commercial forms (uncoated, organic coating, and iron oxide coating) of nano zero-valent iron (nZVI) are toxic to freshwater and marine organisms, specifically three species of marine phytoplankton, one species of freshwater phytoplankton, and a freshwater zooplankton species (Daphnia magna), because these organisms may be exposed downstream of where nZVI is applied to remediate polluted soil. The aggregation and reactivity of the three types of nZVI varied considerably, which was reflected in their toxicity. Since levels of Fe(2+) and Fe(3+) increase as the nZVI react, we also evaluated their toxicity independently. All four phytoplankton species displayed decreasing population growth rates, and Daphnia magna showed increasing mortality, in response to increasing levels of nZVI, and to a lesser degree with increasing Fe(2+) and Fe(3+). All forms of nZVI aggregated in soil and water, especially in the presence of a high concentration of calcium ions in groundwater, thus reducing their transports through the environment. However, uncoated nZVI aggregated extremely rapidly, thus vastly reducing the probability of environmental transport and potential for toxicity. This information can be used to design a risk management strategy to arrest the transport of injected nZVI beyond the intended remediation area, by injecting inert calcium salts as a barrier to transport.http://europepmc.org/articles/PMC3431385?pdf=render
collection DOAJ
language English
format Article
sources DOAJ
author Arturo A Keller
Kendra Garner
Robert J Miller
Hunter S Lenihan
spellingShingle Arturo A Keller
Kendra Garner
Robert J Miller
Hunter S Lenihan
Toxicity of nano-zero valent iron to freshwater and marine organisms.
PLoS ONE
author_facet Arturo A Keller
Kendra Garner
Robert J Miller
Hunter S Lenihan
author_sort Arturo A Keller
title Toxicity of nano-zero valent iron to freshwater and marine organisms.
title_short Toxicity of nano-zero valent iron to freshwater and marine organisms.
title_full Toxicity of nano-zero valent iron to freshwater and marine organisms.
title_fullStr Toxicity of nano-zero valent iron to freshwater and marine organisms.
title_full_unstemmed Toxicity of nano-zero valent iron to freshwater and marine organisms.
title_sort toxicity of nano-zero valent iron to freshwater and marine organisms.
publisher Public Library of Science (PLoS)
series PLoS ONE
issn 1932-6203
publishDate 2012-01-01
description We tested whether three commercial forms (uncoated, organic coating, and iron oxide coating) of nano zero-valent iron (nZVI) are toxic to freshwater and marine organisms, specifically three species of marine phytoplankton, one species of freshwater phytoplankton, and a freshwater zooplankton species (Daphnia magna), because these organisms may be exposed downstream of where nZVI is applied to remediate polluted soil. The aggregation and reactivity of the three types of nZVI varied considerably, which was reflected in their toxicity. Since levels of Fe(2+) and Fe(3+) increase as the nZVI react, we also evaluated their toxicity independently. All four phytoplankton species displayed decreasing population growth rates, and Daphnia magna showed increasing mortality, in response to increasing levels of nZVI, and to a lesser degree with increasing Fe(2+) and Fe(3+). All forms of nZVI aggregated in soil and water, especially in the presence of a high concentration of calcium ions in groundwater, thus reducing their transports through the environment. However, uncoated nZVI aggregated extremely rapidly, thus vastly reducing the probability of environmental transport and potential for toxicity. This information can be used to design a risk management strategy to arrest the transport of injected nZVI beyond the intended remediation area, by injecting inert calcium salts as a barrier to transport.
url http://europepmc.org/articles/PMC3431385?pdf=render
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