What are the effects of soil treatment procedures (sterilization by γ-irradiation and solvent-assisted spiking) on DDE bioaccumulation by earthworms?
Language English Country Great Britain, England Media print-electronic
Document type Journal Article
PubMed
30292157
DOI
10.1016/j.envpol.2018.09.111
PII: S0269-7491(18)32733-7
Knihovny.cz E-resources
- Keywords
- Bioaccumulation, DRIFT-S, Eisenia andrei, Soil organic matter, sterilization,
- MeSH
- Dichlorodiphenyl Dichloroethylene analysis MeSH
- Hydrophobic and Hydrophilic Interactions MeSH
- Soil Pollutants analysis MeSH
- Oligochaeta metabolism MeSH
- Organic Chemicals isolation & purification MeSH
- Soil chemistry MeSH
- Solvents isolation & purification MeSH
- Sterilization methods MeSH
- Gamma Rays MeSH
- Environmental Pollution analysis MeSH
- Animals MeSH
- Check Tag
- Animals MeSH
- Publication type
- Journal Article MeSH
- Names of Substances
- Dichlorodiphenyl Dichloroethylene MeSH
- Soil Pollutants MeSH
- Organic Chemicals MeSH
- Soil MeSH
- Solvents MeSH
Ionizing γ-irradiation and solvent-assisted spiking are frequently applied to eliminate microbial activity and to induce hydrophobic organic compounds (HOCs) into soil, respectively, when studying the accumulation of chemicals in terrestrial organisms. However, the side-effects that may arise from these treatments on soil-HOC interaction and, subsequently, the kinetics and extents of bioaccumulation are not thoroughly understood. To this end, the accumulation of 1,1-dichloro-2,2-bis(p-chlorophenyl)etylene (p,p'-DDE) by Eisenia andrei was studied in sterilized or unsterilized and freshly spiked (FS) or historically contaminated (HC) soils in parallel with an analysis of aliphatic and hydrophilic soil organic matter (SOM) moieties using mid-infrared diffuse reflectance spectroscopy (DRIFT-S). Irradiation did not impart significant changes on spectral SOM descriptors. In contrast, earthworm inhabitation increased the relative presence of aliphatic moieties to a greater extent than hydrophilic ones, reaching or exceeding pre-treatment levels. Overall, effects on SOM chemistry can be ranked as earthworms > spiking > irradiation. Corresponding changes at the bioaccumulation level were observed for the FS soil (i.e., a 27% reduction in bioaccumulation upon sterilization) but not for the HC soil. This implies that in contrast to the interactions between aged p,p'-DDE and sterilized HC soil, the interactions established between freshly added p,p'-DDE and sterilized FS soil were altered by γ-irradiation-induced secondary effects alone or in combination with earthworm inhabitation. Thus, although the soil treatment processes studied here should not drastically impact compound bioaccumulation, they should be considered in mechanistic studies where the qualitative and quantitative aspects of compound-soil (organic matter)-earthworm interactions are at the centre of attention.
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