» Articles » PMID: 24202850

The Threshold Problem in Ecotoxicology

Overview
Journal Ecotoxicology
Date 2013 Nov 9
PMID 24202850
Citations 4
Authors
Affiliations
Soon will be listed here.
Abstract

The most commonly used threshold in environmental toxicology is the LC50 (or modifications thereof) where 50% of the organisms die or are otherwise affected at a certain concentration of a chemical for a particular time of exposure under specified environmental conditions. Most commonly, this particular threshold is derived from single species laboratory tests low in environmental realism. If the field of ecotoxicology truly examines the effects of chemicals on ecosystems (i.e., complex multivariate systems), serious consideration must be given to thresholds other than those now commonly used in the field of environmental toxicology. Attributes at the community and ecosystem level of organization are not demonstrated at lower levels of biological organization, for example, energy flow and nutrient spiralling. Key issues are whether extrapolation is possible from one threshold to another within a level of biological organization and from one level of biological organization to another for thresholds that do not exist at many levels. Thresholds may be artefacts of testing procedures and may not exist in natural systems. Nevertheless, society must make management decisions about risk with available methods, including those designed to identify some point or threshold below which no deleterious effects are observed. However, these methods and their assumptions deserve more explicit and systematic examination than they have received thus far.

Citing Articles

Zinc, among a 'cocktail' of metal pollutants, is responsible for the absence of the terrestrial isopod Porcellio scaber from the vicinity of a primary smelting works.

Hopkin S, Hames C Ecotoxicology. 2013; 3(1):68-78.

PMID: 24201867 DOI: 10.1007/BF00121389.


Finding biomarkers is getting easier.

Bradley B Ecotoxicology. 2012; 21(3):631-6.

PMID: 22410950 DOI: 10.1007/s10646-011-0848-1.


Survival data analyses in ecotoxicology: critical effect concentrations, methods and models. What should we use?.

Forfait-Dubuc C, Charles S, Billoir E, Delignette-Muller M Ecotoxicology. 2012; 21(4):1072-83.

PMID: 22302371 DOI: 10.1007/s10646-012-0860-0.


Measuring the avoidance behaviour shown by the snail Hydrobia ulvae exposed to sediment with a known contamination gradient.

Araujo C, Blasco J, Moreno-Garrido I Ecotoxicology. 2011; 21(3):750-8.

PMID: 22161126 DOI: 10.1007/s10646-011-0835-6.

References
1.
Roberts L . Does the Ozone Hole Threaten Antarctic Life?: Early evidence is just coming in; so far, the answer is far from clear and investigators are divided. Science. 1989; 244(4902):288-9. DOI: 10.1126/science.244.4902.288. View

2.
Niederlehner B, Cairns Jr J . Effects of ammonia on periphytic communities. Environ Pollut. 1990; 66(3):207-21. DOI: 10.1016/0269-7491(90)90002-t. View

3.
Niederlehner B, Pontasch K, Pratt J, Cairns Jr J . Field evaluation of predictions of environmental effects from a multispecies-microcosm toxicity test. Arch Environ Contam Toxicol. 1990; 19(1):62-71. DOI: 10.1007/BF01059813. View

4.
Anderson J, Toohey D, Brune W . Free Radicals Within the Antarctic Vortex: The Role of CFCs in Antarctic Ozone Loss. Science. 1991; 251(4989):39-46. DOI: 10.1126/science.251.4989.39. View

5.
MacMahon J, Phillips D, Robinson J, Schimpf D . Levels of biological organization: an organism-centered approach. Bioscience. 1978; 28(11):700-4. View