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Brominated Flame Retardants and Perfluorinated Chemicals Chapter | 52  699




  VetBooks.ir  TABLE 52.3 Polybrominated Diphenyl Ether Levels in Domestic, Pet, and Wild Animals


                                                           Total PBDE
                            Sample
               Animal
                                                                                       (years)
                                                           Concentration     Unit      Age      References
               Household    Serum                          4.3 6 1.5 (3.5)   ng/mL     1.25 5   Dye et al. (2007)
               cat a
                            Serum                          10.5 6 3.5 (5.9)  ng/mL     8 15     Dye et al. (2007)
                            Serum                          12.7 6 3.9 (6.2)  ng/mL     10 18    Dye et al. (2007)
               Captive giant  Liver, Kidney, brain, gonad,  38.4 2158        ng/g lw   NA       Hu et al. (2008)
               and red panda  muscle, adipose tissues
               Cow          Fat tissue                     1300 2700         pg/g lw   NA       Kierkegaard et al.
                                                                                                (2009)
               Cow          Milk                           1100 2600         pg/g lw   NA       Kierkegaard et al.
                                                                                                (2009)
               Moose        Liver                          0.24 26 (PBDE-47)  ng/g lw           De Wit et al.
                                                           0.26 34 (PBDE-99)                    (2010)


               Arctic fox   Subcutaneous adipose tissue    26.3              ng/g lw   NA       De Wit et al.
                                                                                                (2010)
               Arctic fox   Abdominal adipose tissue       31.6              ng/g lw   NA       De Wit et al.
                                                                                                (2010)
               California sea  Blubber                     569 24,343        ng/g lw   NA       Stapleton et al.
               lion                                                                             (2006)
               Polar bear   Adipose tissue                 4.6 11            ng/g lw            Muir et al. (2006)
               California sea  Liver                       2,423 (n 5 6)     ng/g lw            Kannan et al.
               otter                                                                            (2008)
               Silver perch  Whole fish                    337 (n 5 2)       ng/g lw            Sajwan et al.
                                                                                                (2008)
               NA, not available.
               a
                Total PBDE concentrations in parentheses indicate median; lw, lipid weight.

             2007). Because of these differential reports, the role of  elimination. Influx transporters further increase the T 4
             hypothyroxinemia with regard to the behavioral effects of  uptake and metabolism, whereas efflux transporters elimi-
             PBDEs is unclear. However, the mechanisms by which  nate T 4 or its conjugates from the liver into either serum or
             PBDEs or other BFRs disrupt TH homeostasis are shown in  thebile(Fig. 52.4). Recent studies indicate that PBDE 47
             Fig. 52.4. BFRs as well as their contaminants enter the cir-  (2,2 ,4,4 -tetrabromodiphenyl ether) inhibited iodine uptake
                                                                      0
                                                                   0
             culatory system from the gastrointestinal tract. T 4 is synthe-  suggesting its effects on TH synthesis (Wu et al., 2016).
             sized and released into circulation by the thyroid gland. In  Given the key role of TH in development, BFR-induced
             circulation, BFRs (parent compound as well as metabolites)  perturbations in TH homeostasis might play a role in the
             can displace T 4 from serum binding proteins such as TTR.  outcome of adverse effects associated with BFR exposure.
             The resulting free T 4 will be subjected to hepatic metabo-  Studies indicate that a commercial pentabrominated
             lism and elimination. The reductions in circulating T 4 levels  mixture (DE-71), when administered during develop-
             increase TSH production via reduced negative feedback on  ment, did not alter maternal or male offspring body
             the hypothalamic pituitary axis, which induces increased  weights. However, female offspring were smaller com-
             synthesis and secretion of T 4 by the thyroid gland. BFRs  pared to controls from PND 35 to 60. Exposure to DE-
             bound toTTR alongwithT 4 will reach target organs  71 also resulted in accumulation of PBDE congeners in
             including the brain, in which they can bind to the TH recep-  various tissues including brain, suggesting that PBDEs
             tor to elicit a biological/toxicological response. In the liver,  cross the blood placenta and blood brain barriers,
             BFRs activate nuclear receptors, initiating transcription of  causing subtle changes in some parameters of neurobe-
             xenobiotic metabolizing enzymes for T 4 metabolism and  havior and dramatic changes in circulating TH levels,
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