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Journal ArticleDOI

Trophic magnification factors: Considerations of ecology, ecosystems, and study design

TLDR
Empirical TMFs are likely to be useful for understanding the food web biomagnification potential of chemicals, but may be less useful in species- and site-specific risk assessments, where the goal is to predict absolute contaminant concentrations in organisms in relation to threshold levels.
Abstract
Recent reviews by researchers from academia, industry, and government have revealed that the criteria used by the Stockholm Convention on persistent organic pollutants under the United Nations Environment Programme are not always able to identify the actual bioaccumulative capacity of some substances, by use of chemical properties such as the octanol–water partitioning coefficient. Trophic magnification factors (TMFs) were suggested as a more reliable tool for bioaccumulation assessment of chemicals that have been in commerce long enough to be quantitatively measured in environmental samples. TMFs are increasingly used to quantify biomagnification and represent the average diet-to-consumer transfer of a chemical through food webs. They differ from biomagnification factors, which apply to individual species and can be highly variable between predator–prey combinations. The TMF is calculated from the slope of a regression between the chemical concentration and trophic level of organisms in the food web. The trophic level can be determined from stable N isotope ratios (δ15N). In this article, we give the background for the development of TMFs, identify and discuss impacts of ecosystem and ecological variables on their values, and discuss challenges and uncertainties associated with contaminant measurements and the use of δ15N for trophic level estimations. Recommendations are provided for experimental design, data treatment, and statistical analyses, including advice for users on reporting and interpreting TMF data. Interspecies intrinsic ecological and organismal properties such as thermoregulation, reproductive status, migration, and age, particularly among species at higher trophic levels with high contaminant concentrations, can influence the TMF (i.e., regression slope). Following recommendations herein for study design, empirical TMFs are likely to be useful for understanding the food web biomagnification potential of chemicals, where the target is to definitively identify if chemicals biomagnify (i.e., TMF > or < 1). TMFs may be less useful in species- and site-specific risk assessments, where the goal is to predict absolute contaminant concentrations in organisms in relation to threshold levels. Integr Environ Assess Manag 2012;8:64–84. © 2011 SETAC

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Citations
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Journal ArticleDOI

Biomagnification of Mercury in Aquatic Food Webs: A Worldwide Meta-Analysis

TL;DR: In this article, a simple linear regression between log10 transformed mercury (Hg) concentration and stable nitrogen isotope values (δ15N), hereafter called trophic magnification slope (TMS), was used to represent the overall degree of Hg biomagnification.
Journal ArticleDOI

Per- and polyfluoroalkyl substances in the environment

TL;DR: In this article, the per-and polyfluoroalkyl substances (PFAS) have been found to be ubiquitous environmental contaminants, present from the far Arctic reaches of the planet to urban rainwater.
Journal ArticleDOI

Tracing organophosphorus and brominated flame retardants and plasticizers in an estuarine food web.

TL;DR: The relative high PFR levels in several fish species suggest high emissions and substantial exposure of organisms to PFRs in the Western Scheldt.
Journal ArticleDOI

Occurrence, bioaccumulation, and trophic magnification of pharmaceutically active compounds in Taihu Lake, China.

TL;DR: The occurrence, bioaccumulation, and trophic magnification of pharmaceutically active compounds, (PhACs) including antibiotics, non-steroidal anti-inflammatory drugs, a non-selective β-adrenoceptor blocker, an antiepileptic drug, and steroid estrogens, were investigated in Taihu Lake, China.
Journal ArticleDOI

Mercury biomagnification through food webs is affected by physical and chemical characteristics of lakes.

TL;DR: The results show that the magnitude of MeHg biomagnification through lake food webs is related to the chemical and physical characteristics of the systems, but the underlying mechanisms warrant further investigation.
References
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Journal ArticleDOI

Using stable isotopes to estimate trophic position: models, methods, and assumptions

TL;DR: In this article, the authors developed and discussed methods for generating an isotopic baseline and evaluate the assump- tions required to estimate the trophic position of consumers using stable isotopes in multiple ecosystem studies.
Journal ArticleDOI

Stable isotopes in ecosystem studies

TL;DR: The use of stable isotopes to solve biogeochemical problems in ecosystem analysis is increasing rapidly because stable isotope data can contribute both source-sink (tracer) and process information: the elements C, N, S, H, and all have more than one isotope, and isotopic compositions of natural materials can be measured with great precision with a mass spectrometer as mentioned in this paper.
Journal ArticleDOI

Food Web Complexity and Species Diversity

TL;DR: It is suggested that local animal species diversity is related to the number of predators in the system and their efficiency in preventing single species from monopolizing some important, limiting, requisite in the marine rocky intertidal.
Journal ArticleDOI

Variation in trophic shift for stable isotope ratios of carbon, nitrogen, and sulfur

TL;DR: For example, this article found that the trophic shift for C was lower for consumers acidified prior to analysis than for unacidified samples ( +0.5 + 0.13%o rather than 0.0%o, as commonly assumed).
Journal ArticleDOI

Getting to the fat of the matter: models, methods and assumptions for dealing with lipids in stable isotope analyses

TL;DR: The results indicate that lipid extraction or normalization is most important when lipid content is variable among consumers of interest or between consumers and end members, and when differences in δ13C between end members is <10–12‰.
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