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Toxicant use in the zoo environment.

Toxicants, such as insecticides, rodenticides, caging material, and cleaning agents, are used on a daily basis in zoos to provide a healthy environment. These products must be used carefully so that the zoo inhabitants are not inadvertently poisoned. Product labels should be read, directions followed, and warnings heeded. An understanding of the mechanisms of action of the products as well as their effects on different species will assist zoo personnel in diagnosis and treatment decisions should toxicosis occur. Information regarding the effects of toxicants in exotic species is limited and so much information must be extrapolated from information on domestic species.

Animals↗

Acute yellow phosphorus poisoning. "Smoking stool syndrome".

Three cases of acute phosphorus poisoning are reported. The source of this poison was a rodenticide, which may be in more common use presently because of the increasing resistance of rodents to warfarin derivatives. The safest method of managing poisoning from this highly toxic substance is prevention. Two of the patients had a history of previous medicine overdose.

Acute Disease↗

Residues depletion in egg after warfarin ingestion by laying hens.

Accidental ingestion of anticoagulant rodenticide bait by poultry rarely leads to clinical signs of poisoning, but represents a risk for the consumer because of potential residues in the laid eggs. An assay was conducted for a better risk assessment. Three groups of laying hens were given a single oral dose of 10, 30 or 90 mg warfarin/kg BW. Eggs were collected for 14 d, and warfarin was analyzed by reversed-phase high-performance liquid chromatography. Warfarin was present in the white for 3 to 4 d following anticoagulant ingestion, while concentration increased in the yolk until the 5th or 6th d, and then gradually decreased. At the end of experimentation, warfarin was still detected at below 100 ng/g in the yolk of eggs in each group.

Animals↗

Evolution of herbicide-resistant weeds.

The first generation of species-selective phenoxy herbicides went into use at the same time as modern antibiotics, chlorinated hydrocarbon insecticides and new fungicides and rodenticides. No resistance has appeared to the still widely used phenoxy herbicides. However, resistance has developed, in many isolated areas around the world, to s-triazine herbicides and, in a few small areas, to bipyridillium herbicides. The parameters of population genetics that govern herbicide resistance and those that govern resistance of microorganisms and fungi to other xenobiotics are the same: generations, selection pressure and fitness. Even though generation times are longer with plants, a sufficient number has passed for resistance to be apparent. The only special factor that controls the development of herbicide resistance in weeds is the spaced germination of seed throughout many seasons. The reason that resistance has not developed to the phenoxy herbicides is probably because of a low effective selection pressure; germination of susceptible seeds occurs late in the season after the herbicide is biodegraded. The highly persistent triazines, and the monthly used, highly ephemeral bipyridillium, paraquat, have exerted much stronger selection pressures. Different modes of tolerance and resistance seem to have evolved in the same species. Crop and herbicide rotation can considerably delay the possibility of resistance development until it is effectively precluded.

Adaptation, Biological↗

Superwarfarin poisoning: a report of two cases and review of the literature.

Superwarfarins are anticoagulant rodenticides similar to warfarin, but which have various substituted phenyl groups replacing the terminal methyl group, resulting in a fat-soluble, long-acting anticoagulant that is nearly 100 times more potent than the parent compound. Since their development, many accidental and intentional cases of consumption have been reported. We describe two cases of consumption, one related to unknown etiology, and the other related to utilization of the superwarfarin to potentiate a drug of abuse. The clinical manifestations including bleeding symptoms and abnormal coagulation assays are discussed. The differential diagnosis is quite broad, and includes all causes of vitamin K deficiency, factor deficiency or inhibitor, disseminated intravascular coagulation (DIC), and liver disease. Differentiating superwarfarin ingestion from the other causes can be quite difficult, but extremely important, as management requires prolonged administration of vitamin K. Other treatment options are discussed as well including, fresh frozen plasma (FFP), and recombinant factor VIIa. Finally, the significance of "lacing" drugs of abuse with superwarfarin to potentiate their effect is discussed, as well as the complications that could develop from such a habit.

4-Hydroxycoumarins↗

Poisoning as a result of barium styphnate explosion.

BACKGROUND: Acute barium poisoning is most often the result of accidental or suicidal ingestion of the rodenticide, barium carbonate. We describe a trauma patient whose condition was complicated by severe acute barium toxicity from an explosion of the propellant, barium styphnate. In addition to critical injuries, the patient manifested classic signs of barium toxicity including repeated profound hypokalemia, cardiac arrhythmias, respiratory failure, prolonged gastrointestinal dysfunction, paralysis, myoclonus, hypertension, and profound lactic acidosis. METHODS: The patient required lidocaine for ventricular bigeminy, massive infusions of potassium, prolonged ventilatory support, and parenteral nutrition to manage the effects of barium toxicity. RESULTS: He is the first reported case to demonstrate recurrent profound hypokalemia as an effect of blood transfusions. CONCLUSIONS: Considering the paucity of information concerning management of this life-threatening problem, the pathophysiology of barium toxicity, including the transfusion related hypokalemia, and its management is reviewed.

Accidents, Occupational↗

Methodological aspects of the determination of the acute inhalation toxicity of spray-can ingredients.

Spray-can ingredients, if liberated in confined spaces, are potential health hazards for man. Thus, appropriate inhalation toxicity studies have to be performed in accordance with internationally recognized guidelines, e.g. the US Environmental Protection Agency: Federal Insecticide, Fungicide and Rodenticide Act (FIFRA no. 81-3) or OECD no. 403. One of the essential requirements of such guidelines is that test animals (preferably rats) be exposed to a steady-state concentration in a dynamic inhalation chamber for at least 4 hours. This is not easy to achieve with vapours released from a pressurized spray-can. The method described here makes it possible to expose experimental animals in an inhalation chamber to a steady-state concentration of intermittently released spray jets of constant doses per jet. Animal experiments and theoretical considerations (computer simulations) have shown that the method presented allows an up-to-date determination of the acute inhalation toxicity of spray-can ingredients.

Administration, Inhalation↗

Warfarin resistance in a French strain of rats.

A warfarin-resistant strain and a warfarin-susceptible strain of wild rats (Rattus norvegicus) maintained in enclosures of the National Veterinary School of Lyon (France) were studied to determine the mechanism of the resistance to anticoagulant rodenticides. A low vitamin K epoxide reductase (VKOR) activity has been reported for many resistant rat strains. As recently suggested, mutations in the vitamin K epoxide reductase subunit 1 (VKORC1) gene are the genetic basis of anticoagulant resistance in wild populations of rats from various locations in Europe. Here we report, for our strain, one of the seven described mutations (Tyr139Phe) for VKORC1 in rats. In addition, a low expression of mRNA encoding VKORC1 gene is observed in resistant rats, which could explain their low VKOR activity. We calculated kinetic parameters of VKOR in the warfarin-resistant and warfarin-susceptible rats. The V(max) and the K(m) of the VKOR obtained in resistant rats were lowered by 57 and 77%, respectively, compared to those obtained in susceptible rats. As a consequence, the enzymatic efficiency (V(m)/K(m)) of the VKOR was similar between resistant and susceptible rats. This result could be a good explanation to the observation that no clinical signs of vitamin K deficiency was observed in the warfarin-resistant strain, while a low VKOR activity was found. VKOR activity in warfarin-resistant rats was poorly inhibited by warfarin (K(i) for warfarin is 29 microM and 0.72 microM for resistant and susceptible rats, respectively).

Animals↗

Uncalibrated modelling of conservative tracer and pesticide leaching to groundwater: comparison of potential Tier II exposure assessment models.

The Root Zone Water Quality Model (RZWQM) and Pesticide Root Zone Model (PRZM) are currently being considered by the Office of Pesticide Programs (OPP) in the United States Environmental Protection Agency (US EPA) for Tier II screening of pesticide leaching to groundwater (November 2005). The objective of the present research was to compare RZWQM and PRZM based on observed conservative tracer and pesticide pore water and soil concentrations collected in two unique groundwater leaching studies in North Carolina and Georgia. These two sites had been used previously by the Federal Insecticide, Fungicide and Rodenticide Act (FIFRA) Environmental Model Validation Task Force (EMVTF) in the validation of PRZM. As in the FIFRA EMVTF PRZM validation, 'cold' modelling using input parameters based on EPA guidelines/databases and 'site-specific' modelling using field-measured soil and hydraulic parameters were performed with a recently released version of RZWQM called RZWQM-NAWQA (National Water Quality Assessment). Model calibration was not performed for either the 'cold' or 'site-specific' modelling. The models were compared based on predicted pore water and soil concentrations of bromide and pesticides throughout the soil profile. Both models tended to predict faster movement through the soil profile than observed. Based on a quantitative normalised objective function (NOF), RZWQM-NAWQA generally outperformed or was equivalent to PRZM in simulating pore water and soil concentrations. Both models were more successful in predicting soil concentrations (i.e. NOF < 1.0 for site-specific data, which satisfies site-specific applicability) than they were at predicting pore water concentrations.

Environment↗

The use of plants for environmental monitoring and assessment.

This paper presents a critical review on phytotoxicity tests for environmental monitoring and assessment. Vascular macrophytes used in the laboratory testing are emphasized; algae are mentioned only for comparison. Several issues are discussed, including the rationale for and misconceptions about phytotoxicity tests, relation to regulation, status of phytotoxicity test protocols, advantages and disadvantages of phytotoxicity tests, and possible research directions. Aquatic and terrestrial macrophytes, along with algae, are essential components of ecosystems. Macrophytes are becoming more important for the monitoring and assessment of herbicides, effluents, and industrial chemicals. In the United States, Canada, and international organizations, phytotoxicity tests can be required for environmental monitoring and assessment in statutes such as Federal Insecticide, Fungicide, and Rodenticide Act; Toxic Substances Control Act; Water Quality Act; Canadian Pest Control Products Act; and Canadian Environmental Protection Act. Possible research directions for phytotoxicity tests are discussed relative to the role in regulations of industrial chemicals, effluents, hazardous waste sites, and pesticides.

Environmental Monitoring↗

Regulatory oversight of biochemical pesticides by the U.S. Environmental Protection Agency: health effects considerations.

The Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) enables the Office of Pesticide Programs (OPP) of the U.S. Environmental Protection Agency to ensure that pesticide use in commerce will not result in unreasonable adverse effects to humans and the environment. Currently, two classes of pesticides are recognized: conventional chemical pesticides and biological pesticides. The latter group is divided into biochemical and microbial pesticides. The recent resurgence of biochemical pesticides as effective pest control agents has increased the number of applications for experimental use permits and for product registration. The fundamental information and data necessary to evaluate such products by the Health Effects Division (HED) of OPP are discussed, as well as the criteria for the classification of a pesticide as a biochemical versus a conventional chemical pesticide. In accordance with the Agency's effort to encourage the development of pesticides less toxic to humans and the environment, the scientific basis for providing future regulatory relief and reduced data requirements for biochemical pesticides is discussed.

Animals↗

Aggregate exposures under the Food Quality Protection Act: An approach using chlorpyrifos.

The Food Quality Protection Act of 1996 (Public Law 104-170, August 3, 1996), which amended the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) and the Federal Food, Drug, and Cosmetic Act (FFDCA), requires that the EPA evaluate pesticide safety in light of potential aggregate exposures from both nondietary and dietary routes. As with any new legislation, there has been considerable discussion and challenges presented within the regulatory and scientific communities regarding the effective implementation of this act as it relates to the determination of aggregate exposures. This paper describes a novel methodology incorporating personal exposure factors, route-specific exposure measurements, and usage information to characterize potential aggregate exposures to a widely used pesticide, chlorpyrifos. A calendar model framework has been developed to describe potential multipathway exposures to individuals. The model assimilates information regarding the typical use patterns of chlorpyrifos-containing pesticides in concert with quantitative exposure and dose measurements to estimate the probability and magnitude of exposures to members of the U.S. population. Studies measuring 3,5,6-trichloropyridinol, the primary metabolite of chlorpyrifos, in the urine of individuals within the United States show that aggregate exposures derived from this approach are consistent with actual population-based exposures to chlorpyrifos. According to this assessment, potential health risks attributed to exposure to chlorpyrifos are low when compared to relevant toxicological end points.

Animals↗

Phosphine-induced oxidative stress in Hepa 1c1c7 cells.

Phosphine (PH3), from hydrolysis of metal phosphides, is an important insecticide (aluminum phosphide) and rodenticide (zinc phosphide) and is considered genotoxic and cytotoxic in mammals. This study tests the hypothesis that PH3-induced genotoxicity and cytotoxicity are associated with oxidative stress by examining liver (Hepa 1c1c7) cells for possible relationships among cell death, increases in reactive oxygen species (ROS) and lipid peroxidation, and elevated 8-hydroxyguanine (8-OH-Gua) in DNA. PH3 was generated from 0.5 mM magnesium phosphide (Mg3P2) to give 1 mM PH3 as the nominal and maximal concentration. This level causes 31% cell death at 6 h, measured by lactate dehydrogenase leakage, with appropriate dependence on concentration and time. The intracellular ROS level is elevated within 0.5 h following exposure to PH3, peaking at 235% of the control by about 1 h. Lipid peroxidation (measured as malondialdehyde plus 4-hydroxyalkenals) is increased up to 504% by PH3 at 6 h in a time-dependent manner. The level of 8-OH-Gua in DNA, a biomarker of mutagenic oxidative DNA damage analyzed by GC/MS, increases to 259% at 6 h after PH3 treatment. Antioxidants significantly attenuate the PH3-induced ROS formation, lipid peroxidation, 8-OH-Gua formation in DNA, and cell death, with the general order for effectiveness of GSH (5 mM) and D-mannitol (10 mM) (hydroxyl radical scavengers), then Tempol (2.5 mM) and sodium azide (3 mM) (superoxide anion and singlet oxygen scavengers, respectively). These studies support the hypothesis that PH3-induced mutagenic and cytotoxic effects are due to increased ROS levels, probably hydroxyl radicals, initiating oxidative damage.

8-Hydroxy-2'-Deoxyguanosine↗

Control of rickettsial diseases.

Prevention of rickettsial infections is aimed at individual control and epidemic measures (especially in epidemic typhus), vector and rodent control, milk pasteurization (in Q fever), chemoprophylaxis and immunoprophylaxis. In vector and rodent control, the main obstacle is the rise in resistance to insecticides and rodenticides. For this reason in vector control, apart from insecticides, enhancement of the natural immunity acquired by animals in response to tick infestation and vaccination with concealed tick antigens as well as the use of hormones, chemosterilants and genetic manipulation can also be considered. For short-term high-risk exposure, doxycycline may be an effective prophylaxis of illness but may not prevent infection with scrub typhus or spotted fever group rickettsiae. At present, for specific prevention by vaccination, only Q fever vaccines are available for common use. However, development of subunit vaccines, namely immunogenic rickettsial proteins, cloned and expressed in Escherichia coli, seems to be very promising.

Animals↗

Poisoning in children: Indian scenario.

The retrospective data on childhood poisoning from eight regional hospitals in India has been reviewed. The demographic features and types of poisonings encountered have been compared. The analysis of the data indicated that pediatric poisonings constituted 0.23-3.3% of the total poisoning. The mortality ranged from 0.64-11.6% with highest being from Shimla. Accidental poisoning was common involving 50-90% of children below 5 years of age and males outnumbered the females. Suicidal poisoning was seen after 13 years of age and was due to drugs and household chemicals. One of the hospitals in Delhi recorded a very high incidence (66.6%) of drug poisoning in children. The drugs consumed belonged to phenothiazines, antiepileptics and antipyretics. Iron poisoning was seen in younger children. Kerosene was one of the causes of accidental poisoning at all hospitals except Shimla and rural Maharashtra were probably wood charcoal is widely used. Pesticide poisoning was more prevalent in Punjab and West Bengal whereas plant poisoning was very common in Shimla. Significant number of snake envenomation has been recorded from rural Maharashtra. Other less common accidental poisonings in children included alcohol, corrosives, heavy metals, rodenticides, detergents and disinfectants. Thus various regions in the country showed some variation in types and frequency of childhood poisoning which could be attributed to different geographical and socio-economic background.

Adolescent↗

The use of dogs as second species in regulatory testing of pesticides. I. Interspecies comparison.

The relevance of studies in dogs on regulatory testing of pesticides was examined retrospectively using data of 216 pesticides (acaricides, fungicides, growth regulators and hormones, herbicides, insecticides, molluscicides, nematicides, rodenticides, synergists for insecticides) submitted for regulatory purposes during the past 40 years to the Federal Institute of Health Protection of Consumers and Veterinary Medicine (BgVV), the competent national authority in Germany. At first the relevance of the no-observed-effect levels (NOEL) for safety assessment was evaluated for each chemical in 4-week (subacute), 13-week (subchronic) and 52/104-week (chronic) toxicity studies carried out on dogs, rats and mice. After subchronic and chronic application of fungicides the sensitivity of rats and dogs to the toxic chemicals was quite similar. However, the dog was generally a more sensitive species to toxic effects of insecticides than rat and mouse. On the other hand the NOEL was lower in the rat than the dog in chronic studies on herbicides. When the lowest-observed-effect level (LOEL) was evaluated in animal species, the dog was the most sensitive in approximately 15% of the studies. Mice were found to be the most sensitive species only in approximately 1% of the studies on 216 pesticides. Comparison of organ specific toxicity at the LOEL in subacute studies on fungicides and herbicides revealed a poor correlation of target-specific organ toxicity across species. However, in the subchronic and chronic studies (13 and 52/104 weeks) no significant differences in species-specific organ toxicity were observed in the three species rat, mouse and dog. The only exception were haematoxic effects in chronic studies on herbicides, which were more frequent in dogs (40%) than in rats and mice (20%). The results support the established concept that studies on dogs and rats are important for the safety assessment of pesticides, while studies on mice do not provide further information, except for detection of an oncogenic potential which is a further controversial issue. Further analysis of subacute, subchronic and chronic studies in dogs should reveal if all of the studies are essential for safety assessment of pesticides.

Animals↗

Diabetic microangiopathy, genetics, environment, and treatment.

As the major cause of disability and death in insulin-dependent diabetes, microangiopathy is obviously of major concern to diabetologists. Unlike macroangiopathy, which can readily be prevented by means that are currently on hand, the origin and treatment of microangiopathy remain far more problematical. The complexity of this lesion is indicated by the findings in this laboratory that hyperglycemia induced by the rodenticide, vacor, can cause microangiopathy independent of genetic diabetes, yet significant microangiopathic lesions can be detected in genetic diabetic patients before the appearance of hyperglycemia. Further, there is now intriguing evidence based both on basement membrane measurements from our laboratory and on clinical studies showing that significant microangiopathy only rarely occurs prior to the onset of puberty. The evidence that control or even normalization of blood glucose levels does not influence the course of established microangiopathy is becoming increasingly convincing. Five prospective, randomized studies over the past five years have shown that strict regulation of glucose has no consistent benefit on, and in some studies may, at least transiently, accelerate, the retinopathy of diabetes. Moreover, the first controlled study of successful pancreatic transplantation to achieve normalization of blood glucose levels has again demonstrated that established retinopathy is neither prevented nor even delayed by normal glucose levels. This review, therefore, emphasizes that, though hyperglycemia is required for clinically significant microangiopathy to occur, clearly other factors, genetic, environmental, or both, must play major roles in determining the course of microangiopathy. It is toward these nonglycemic factors in the development of diabetic microangiopathy that future research should increasingly be directed.

Blood Glucose↗

Sulfaquinoxaline inhibition of vitamin K epoxide and quinone reductase.

Sulfaquinoxaline (N1-(2-quinoxalinyl)sulfanilamide) has been shown to be a potent (Ki = 1 microM) freely reversible inhibitor of the dithiothreitol-dependent reduction of both vitamin K epoxide and vitamin K quinone by rat liver microsomes in vitro. This observation provides an explanation for the hemorrhagic syndrome occasionally seen in poultry on medicated feed and the efficacy of sulfaquinoxaline in anticoagulant based rodenticides. Sulfaquinoxaline inhibition resembled inhibition by coumarin anticoagulants (e.g., warfarin) and hydroxynaphthoquinones (e.g., lapachol). Inhibition was observed in assays using microsomes from control strain rats, but the enzyme was resistant to sulfaquinoxaline in microsomes from warfarin-resistant rats. Steady-state kinetics inhibition patterns were nearly competitive versus dithiothreitol and nearly uncompetitive versus vitamin K epoxide as is observed for warfarin and lapachol. These results suggest that this inhibitor binds to the oxidized form of vitamin K epoxide reductase in the same way as suggested for the coumarins and hydroxyquinones. Of 10 other sulfa drugs tested, none were inhibitors, and of fragments and related compounds tested, only 2-aminoquinoxaline benzenesulfonamide was active. These results provide a probably orientation in the binding site in relation to that for warfarin and lapachol.

Animals↗