DDT degradation efficiency and ecotoxicological effects of two types of nano-sized zero-valent iron (nZVI) in water and soil
Language English Country Great Britain, England Media print-electronic
Document type Journal Article, Research Support, Non-U.S. Gov't
PubMed
26598990
DOI
10.1016/j.chemosphere.2015.10.122
PII: S0045-6535(15)30317-9
Knihovny.cz E-resources
- Keywords
- Aged pollutants, Chlorinated organic pollutants, DDT, Ecotoxicology, Nano-remediation, Nanoparticles,
- MeSH
- Water Pollutants, Chemical chemistry toxicity MeSH
- DDT chemistry toxicity MeSH
- Ecotoxicology MeSH
- Escherichia coli drug effects MeSH
- Hordeum drug effects MeSH
- Crustacea drug effects MeSH
- Oxygen metabolism MeSH
- Soil Pollutants chemistry toxicity MeSH
- Flax drug effects MeSH
- Oligochaeta drug effects MeSH
- Soil MeSH
- Environmental Restoration and Remediation MeSH
- Iron chemistry toxicity MeSH
- Animals MeSH
- Check Tag
- Animals MeSH
- Publication type
- Journal Article MeSH
- Research Support, Non-U.S. Gov't MeSH
- Names of Substances
- Water Pollutants, Chemical MeSH
- DDT MeSH
- Oxygen MeSH
- Soil Pollutants MeSH
- Soil MeSH
- Iron MeSH
Nano-scale zero-valent iron (nZVI) has been conceived for cost-efficient degradation of chlorinated pollutants in soil as an alternative to e.g permeable reactive barriers or excavation. Little is however known about its efficiency in degradation of the ubiquitous environmental pollutant DDT and its secondary effects on organisms. Here, two types of nZVI (type B made using precipitation with borohydride, and type T produced by gas phase reduction of iron oxides under H2) were compared for efficiency in degradation of DDT in water and in a historically (>45 years) contaminated soil (24 mg kg(-1) DDT). Further, the ecotoxicity of soil and water was tested on plants (barley and flax), earthworms (Eisenia fetida), ostracods (Heterocypris incongruens), and bacteria (Escherichia coli). Both types of nZVI effectively degraded DDT in water, but showed lower degradation of aged DDT in soil. Both types of nZVI had negative impact on the tested organisms, with nZVI-T giving least adverse effects. Negative effects were mostly due to oxidation of nZVI, resulting in O2 consumption and excess Fe(II) in water and soil.
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