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Reproduction in Domestic Animals

Reproduction in Domestic Animals

Reproduction in Domestic Animals

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Dietary Pollutants as Risk Factors <strong>in</strong> <strong>Reproduction</strong> 19effects at least equivalent to, and sometimes higher than,those <strong>in</strong>duced by much higher doses adm<strong>in</strong>istered overshort periods of time (Borman et al. 2000).Individual variation <strong>in</strong> exposureIn species as diverse as sheep (Rh<strong>in</strong>d et al. 2005b) and<strong>in</strong>sects from lake sediments (Kovats and Ciborowski1989) differences <strong>in</strong> tissue concentrations of variouspollutants of at least 10-fold between <strong>in</strong>dividuals fromthe same source are commonly observed. Similar environmentalvariation was reported <strong>in</strong> soil samples (foodcontam<strong>in</strong>ant and <strong>in</strong>vertebrate habitat) collected fromwith<strong>in</strong> experimental plots (Rh<strong>in</strong>d et al. 2002). Thisfurther complicates the prediction of responses of<strong>in</strong>dividual animals to pollutant exposure.In summary, there seems to be little doubt that thediet is a major source of exposure to pollutants <strong>in</strong> manyvertebrate species and while the effects on tissueconcentrations are greatest <strong>in</strong> carnivores near to thetop of the food cha<strong>in</strong>, significant tissue accumulationcan occur <strong>in</strong> herbivores. However, the relative contributionsof other factors such as uptake from thesurround<strong>in</strong>g media (air, water, soil or sediment) are lessclear and, <strong>in</strong> certa<strong>in</strong> circumstances and species, thesesources may be more important than dietary ones,particularly <strong>in</strong> small, soil-, sediment-, or water-dwell<strong>in</strong>gspecies.What Risk is Associated with Pollutants <strong>in</strong>Food?S<strong>in</strong>ce many studies of effects of pollutants on reproductivefunction frequently <strong>in</strong>volve transient, unusuallyhigh levels of exposure of wild or laboratory species ofanimals to a s<strong>in</strong>gle chemical, it is sometimes concludedthat normal, low, levels of exposure to pollutants areof no biological consequence. This argument is re<strong>in</strong>forcedby the fact that environmental concentrationsof some, but not all, pollutants are decl<strong>in</strong><strong>in</strong>g (Darnerudet al. 2001; Norstrom 2002), as are milk (Solomonand Weiss 2002) and tissue concentrations (Noakeset al. 2006). In fact, even tissue concentrations thatare at or near to background environmental concentrationsmay exert biological effects, particularly whenthey act <strong>in</strong> conjunction with a mixture of otherchemicals; ‘real-world’ exposure normally <strong>in</strong>volvesprolonged exposure to a mixture of compounds at lowconcentrations. Effects of such exposure patterns havebeen demonstrated by long-term studies of sheepma<strong>in</strong>ta<strong>in</strong>ed throughout their breed<strong>in</strong>g lives on pasturesfertilized with either conventional <strong>in</strong>organic fertilizeror sewage sludge. The latter conta<strong>in</strong>s large amounts ofboth <strong>in</strong>organic and organic pollutants, relative toenvironmental levels (Smith 1996; Stevens et al. 2003)and, when applied to pasture as a fertilizer, results <strong>in</strong>very small <strong>in</strong>creases <strong>in</strong> environmental levels of thesechemicals (Rh<strong>in</strong>d et al. 2002) and <strong>in</strong> the tissue levelsof sheep graz<strong>in</strong>g the pasture (Rh<strong>in</strong>d et al. 2005a,b,2007b). However, these small <strong>in</strong>creases are associatedwith disruption of reproductive and other functions(Erhard and Rh<strong>in</strong>d 2004; Paul et al. 2005; Fowleret al. 2008).Such studies clearly demonstrate that pollutants <strong>in</strong>feed can represent a risk to reproductive function but donot allow the quantification of that risk with respect toeither <strong>in</strong>dividual chemicals or <strong>in</strong>dividual animals. Thatwould require determ<strong>in</strong>ation of dose response relationshipsbetween the concentrations of each chemical, <strong>in</strong>each relevant tissue or organ and for each observedchange <strong>in</strong> structure or function. It is possible to achievethis, empirically, for a small number of <strong>in</strong>dividualchemicals but, at present, virtually impossible to do sofor the thousands of chemicals to which animals areexposed. Understand<strong>in</strong>g of mixture effects, will require<strong>in</strong>tegration of the observations from the wide range ofempirical approaches that are available us<strong>in</strong>g powerfulpredictive computer models (Suk et al. 2002).ConclusionsThere is no doubt that exposure to pollutants canadversely affect reproductive function <strong>in</strong> animals andthat food is likely to be the most important route ofexposure for many or most species, particularly forthose near the top of the food cha<strong>in</strong>. However,assessment of the risk is complicated by the fact that<strong>in</strong> the ‘real world’ food conta<strong>in</strong>s many different classesof pollutants, each at low and variable concentrations,and exposure to them occurs throughout life, <strong>in</strong>clud<strong>in</strong>gdur<strong>in</strong>g developmental stages which are particularlysensitive to their effects. In short, dietary pollutantsrepresent a significant risk factor for reproduction,under certa<strong>in</strong> circumstances, but precise quantificationof these risks for <strong>in</strong>dividuals is extremely difficult withcurrent knowledge.ReferencesAlbro PW, Lavenhar SR, 1989: Metabolism of di-(2-ethylhexyl)phthalate. Drug Metab Rev 21, 13–34.Anway MD, Sk<strong>in</strong>ner MK, 2006: Epigenetic transgenerationalactions of endocr<strong>in</strong>e disruptors. Endocr<strong>in</strong>ology 147, S43–S49.Bachour G, Fail<strong>in</strong>g K, Elmadfa SG, Brunn H, 1998: Speciesand organ dependence of PCB contam<strong>in</strong>ation <strong>in</strong> fish, foxes,roe deer, and humans. Arch Environ Contam Toxicol 35,666–673.Barr DB, Bishop A, Needham LL, 2007: Concentrtions ofxenobiotic chemicals <strong>in</strong> the maternal-fetal unit. ReprodToxicol 23, 260–266.Batty J, Leavitt RA, Biondot N, Pol<strong>in</strong> D, 1990: Anecotoxicological study of a population of the white footedmouse (Peromyscus leucopus) <strong>in</strong>habit<strong>in</strong>g a polychlor<strong>in</strong>atedbiphenyls-contam<strong>in</strong>ated area. Arch Environ Contam Toxicol19, 283–290.Beketov MA, Liess M, 2005: Acute contam<strong>in</strong>ation withesfenvalerate and food limitation: chronic effects on themayfly, Cloeon dipterum. Environ Toxicol Chem 24, 1281–1286.Bemis JC, Seegal RF, 1999: Polychlor<strong>in</strong>ated biphenyls andmethylmercury act synergistically to reduce rat bra<strong>in</strong> dopam<strong>in</strong>econtent <strong>in</strong> vitro. Environ Health Perspect 107, 879–885.Bøgh IB, Christensen P, Dantzer V, Groot M, Thøfner ICN,Rasmussen RK, Schmidt M, Greve T, 2001: Endocr<strong>in</strong>edisrupt<strong>in</strong>g compounds: effect of octylphenol on reproductionover three generations. Theriogenol 55, 131–150.Ó 2008 Macaulay Land Use Research Institute

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