Page 767 - Veterinary Toxicology, Basic and Clinical Principles, 3rd Edition
P. 767

726 SECTION | X Avian and Aquatic Toxicology




  VetBooks.ir  regurgitation, pallor, dark or bright green diarrhea, paresis,  allows it to penetrate the blood brain barrier, where the
                                                                majority of toxic effects are expressed. Selenium can
             seizures, and sudden death. In acute cases, corrosive
                                                                modify the toxicity of MeHg by forming nontoxic
             lesions in the GI tract leading to associated disturbances,
             and injury to the liver, kidneys, and pancreas may be  mercury selenium complexes, preventing the attachment
             observed. In chronic cases, erythrocyte abnormalities and  of mercury with sulfhydryl groups of enzymes and other
             anemia may be commonly observed due to oxidative dam-  bioligands (Sugiura et al., 1976), when the average molar
             age to the erythrocyte hemoglobin and cell membrane pro-  ratio Hg:Se is approximately 1.0 1.5 and total mercury
             teins (Luttgen et al., 1990). Common findings on gross  concentrations exceeded about 50 μg/g as reported in
             examination of birds that have died from zinc toxicosis  eagles, loons and marine or freshwater fishes (Luten
             include greenish, mucoid feces in the ileum, colon, or clo-  et al., 1980; Scheuhammer et al., 2008).
             aca and wasting of pectoral muscles. Microscopically, pan-  Clinical signs due to mercury intoxication are similar
             creas may reveal severe apoptosis, loss of acinar structure,  in multiple species of birds and are characterized by
             necrosis of individual acinar cells, and interstitial fibrosis  reduced food intake, emaciation, weakness in wings and
             (Wight et al., 1986). Hemosiderosis in the liver, accompa-  legs, with difficulty flying, walking, and standing.
             nied by hepatic biliary retention and multifocal, necrotizing  Reproductively, MeHg exposure leads to shell-less eggs,
             hepatitis, may be observed. In GI, hemorrhagic enteritis,  decrease in mean egg weight, early embryonic mortality
             hemorrhagic ventriculitis, and ventricular koilin degenera-  and an increase in unfertilized eggs. Most important path-
             tion are noted (Puschner et al., 1999).            ological findings in birds are atrophy of fat deposits, mus-
                Diagnosis of zinc intoxication can be challenging.  cles, demyelination and necrosis of nerves in the
             History of exposure (e.g., exposure to a new cage, feeding  peripheral and central nervous system, and necrosis of
             and/or watering utensils, or metallic toys), radiographic  renal tubular epithelium.
             imaging, measurement of zinc in plasma/serum (live   The diagnosis of mercury intoxication should not be
             birds) and liver / kidney (dead birds) and histopathology  based on tissue concentrations of mercury alone but nec-
             can aid diagnosis. For most psittacines, a physiologic,  essarily address corresponding selenium concentrations,
             nontoxic zinc concentration in serum or plasma is 2 ppm  the presence or absence of compatible clinical signs and
             (0.2 mg/dL) or less. However physiologic concentrations  necropsy findings. There are no successful treatment
             are slightly higher of up to 3.5 ppm (0.35 mg/dL) for  approaches reported in birds to reverse damage due to
             cockatoos and up to 2.5 ppm (0.25 mg/dL) for eclectus  mercury intoxication. Feeding uncontaminated food and
             parrots (Puschner et al., 1999). Postmortem, liver zinc  water is the most practical approach. Selenium and vita-
             concentrations exceeding 100 ppm are toxic.        min E supplementation can additionally be utilized to
                If a radio-dense zinc object is identified by radiogra-  reduce the toxic potential of mercury before the appear-
             phy, removal of the zinc source results in the rapid  ance of expected signs.
             decline of body concentrations. If immediate removal is
             not possible or delays are expected, reducing the further  Iron
             absorption of zinc in the GI tract may be achieved by
             administering antacids such as calcium carbonate (Van  Increased hepatic iron storage or iron storage disease (ISD)
             der Merwe and Tawde, 2009 ). Chelation of zinc is possi-  is a serious condition noted in captive birds especially in
             ble with CaNa 2 EDTA, although its efficacy and safety in  some species belonging to families Paradiseadae (birds-of-
             the treatment of zinc intoxication in birds have not been  paradise), Ramphastidae (toucans), and Sturnidae (star-
             evaluated.                                         lings) (Pavone et al., 2014). Avian species that have been
                                                                evolved to tolerate relatively low iron content in their diet
                                                                have very efficient iron absorption and do not downregu-
             Mercury
                                                                late their iron absorption when body stores are saturated or
             Mercury exists in nature in different forms ranging from  on feeding of high-iron containing diets (Klasing et al.,
             inorganic elemental forms to complex organic forms. One  2012). Many commercial diets intended for captive birds
             of the most toxic forms is methylercury (MeHg) which is  have been formulated using the nutritional requirements of
             the major source of intoxication in fish-eating birds such  poultry and are not optimal for the low-iron tolerating spe-
             as loons, mergansers, and bald eagles. Consumption of  cies. In addition, the use of animal byproducts significantly
             MeHg-containing diets at environmentally realistic con-  affects the nutritional interactions and bioavailability of
             centrations has been demonstrated to cause behavioral,  iron. Absorption of iron from animal byproducts (heme-
             neurological, hormonal, and reproductive changes in  based iron sources) may be three times higher than that
             birds, fish, and mammals (Scheuhammer et al., 2007).  from nonheme products containing equivalent iron concen-
             MeHg is metabolized and excreted more slowly than  trations. Thus excessive dietary iron, nutritional interac-
             other organomercurials. The lipophilic nature of MeHg  tions increasing the bioavailability and genetically or
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