Biomarkers in terrestrial invertebrates for ecotoxicological soil risk assessment.
This review has served to present the most recent information on a selected series of biomarker studies undertaken on soil invertebrates during two extensive European-funded scientific consortia, BIOPRINT and BIOPRINT-II. The goals were to develop and validate methods for the analysis of markers of stress in a range of soil-dwelling organisms. We have discussed the potential and limitations of the following invertebrate biomarkers for soil risk assessment purposes: heat shock proteins, histological and ultrastructural markers, metallothioneins and metal-binding proteins, esterases, lysosomal integrity, and the novel biomarker histidine. The hsp response in soil invertebrates is especially suitable to indicate the effects of exposure to comparatively low concentrations for a range of toxicants and can be regarded as a biomarker of general stress. The application of MTs and other metal-binding proteins as biomarkers for exposure in soil invertebrates has been well described, and new methods are being developed for analyzing MT induction both at the protein and molecular level, and reliable and reproducible methods are now available. (Cd)-MT is well characterized for the springtails and its MT concentration is a useful biomarker for exposure as well as for effect. For snails, (Cd)-MT can accumulate in the midgut gland over extended periods of time and therefore its concentration is a biomarker not only for recent intoxication but also for events of cadmium exposure that snails may have experienced a long time before the measurement took place. Cellular and histological alterations can be regarded as reflecting the "health" state of a cell, which may be a measure for the presence of toxicants. Histopathological work on terrestrial invertebrates, however, is still scarce. Isozymes have been poorly studied in soil invertebrates despite their promising role as potential biomarkers in aquatic organisms. Among the large diversity of isozymes, the most well studied are esterases that are frequently used a biomarkers of exposure to various classes of pesticides. Many other isozymes offer potentials for biomarker research, such as glucosephosphate isomerase and phosphoglucomutase, both enzymes necessary for the glycolytic pathway. The lysosomal system has been identified as a particular target for the toxic effects of xenobiotics, although it has yet a limited application in soil invertebrates. This marker is nonspecific, responding equally sensitively to organic or inorganic contamination; however, if used in combination with an earthworm immnunocompetence assay such as total immunoactivity of the coelomocytes, then it is possible to be more specific as to the likely nature of contamination. Free histidine was positively correlated with increasing copper exposure and total copper burden in earthworms from a semifield study. Histidine may thus act as a biomarker of exposure. The transient responses and confounding factors of biomarkers obscure a proper interpretation of biomarker responses under field conditions. These factors are still very poorly understood and require more study. For risk assessment purposes it is recommended that the aforementioned biomarkers may show promise when included in a suite of biomarkers among different soil invertebrate species. It is recommended that a risk assessment protocol draw upon ranking of biomarker responses on a defined scale. It is also hoped that the problems outlined in this review will aid the direction of future research on soil invertebrate biomarkers.
Kammenga
J E
JE
Laboratory of Nematology, Wageningen University, Binnenhaven 10, 6709 PD Wageningen, The Netherlands.
Dallinger
R
R
Donker
M H
MH
Köhler
H R
HR
Simonsen
V
V
Triebskorn
R
R
Weeks
J M
JM
D000818:Animals; D015415:Biomarkers / Q000032:analysis*; D004463:Ecology; D004784:Environmental Monitoring / Q000379:methods*; D006360:Heat-Shock Proteins / Q000032:analysis; D007448:Invertebrates / Q000737:chemistry / Q000502:physiology*; D007527:Isoenzymes / Q000032:analysis; D008247:Lysosomes; D008668:Metallothionein / Q000032:analysis; D018570:Risk Assessment; D012680:Sensitivity and Specificity; D012989:Soil Pollutants / Q000009:adverse effects* / Q000032:analysis
D015415:Biomarkers; D006360:Heat-Shock Proteins; D007527:Isoenzymes; D012989:Soil Pollutants; D008668:Metallothionein