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The methods of toxicological detection of the rodenticides Dirax and Vacor (urea derivates) in biological material were worked out and tested. The new chromatographic methods using a thin silica gel layer can be of help in laboratory toxicological diagnostics.
Four patients developed severe burning feet after ingestion of the rodenticide RH-787 (Vaccor-B) attempting suicide. Parenteral administration of vitamin-B-complex relieved the symptom in all patients. Based on the results of these four patients and other data in the literature, vitamin-B-deficiency is discussed as a possible cause of burning feet.
The analytical method which is described enables to detect principal anticoagulants presently used in France as rodenticides. Its particularity lies in using a mixture of iso octane and dichloromethane 95/5 (V/V) in the extractive part whose output varies according to the compounds from 80 to 25 per cent in supplemented liver. Besides thin layer chromatography which is used to achieve identification and semi quantitative evaluation, spectrometric measurement can be carried through to confirm identity and precise quantity with more accuracy. Sensitivity varying according to compounds, it is possible to detect products whose minimum concentration in biological materials is between 1 and 5 ppm.
A patient who had severe orthostatic hypotension secondary to ingesting Vacor, a rodenticide containing N-3 pyridilmethyl-N'-nitrophenyl urea (PNU), fully recovered from this initially disabling condition 11 months after poisoning. Initial treatments with elastic stockings, fludrocortisone acetate, and dihydroergotamine mesylate resulted in no obvious improvement of his orthostasis. Findings from a hemodynamic study performed with the patient was severely orthostatic suggested functional impairment of vascular adrenergic nerve terminals as a major lesion. A similar study after recovery from orthostasis showed that the baroreceptor reflex mechanism returned to normal. This report shows that initially severe and disabling orthostatic hypotension may not be a hopelessly permanent sequela of PNU intoxication and that a gradual, spontaneous full recovery from orthostasis is possible.
The baits used consisted of 2% zinc phosphide and 0.005% bromadiolone. The baitings were carried out at the flowering stage of cucumber crop. Double baiting treatments comprising zinc phosphide and bromadiolone in different combinations resulted in better reduction of rodent population and crop damage. Deployment of different rodenticidal treatments saved yield loss from 7.00 to 11.82q/ha. Thus, accomplishing cost benefit ratio of 1:88 to 1:107. Bromadiolone followed by bromadiolone, the most profitable combination is suggested for control of rodent population in cucumber crop fields.
The occurrence, the diagnosis, and the treatment of anticoagulant rodenticide poisoning in dogs in the Netherlands was evaluated by a survey among Dutch veterinarians carried out by the National Poisons Control Center (NPCC). The survey included information on 54 dogs, 32 being treated by veterinarians who consulted the NPCC and 22 that were admitted to the Utrecht University Clinic for Companion Animals (UUCCA). The poisons that were suspected were brodifacoum (n = 19), bromadiolone (n = 14), difenacoum (n = 8), difethialone (n = 6) and chlorophacinone (n = 1). In 6 dogs the identity of the poison was unknown. Of 31 dogs with hemorrhages, 2 died shortly after presentation to practitioners and 2 died shortly after admission to the UUCCA. Signs of bleeding occurred especially in poisoning by brodifacoum (n = 16). In all but one of the dogs without hemorrhages, the intake of poison had taken place within 24 hours before presentation. The method of treatment varied, with the induction of vomiting and the use of vitamin K mentioned most. The choice of therapy was determined by the length of time after intake of the poison, the clinical signs and whether or not an anticoagulant toxicosis was suspected at the time of the initial examination. These findings provide the basis for discussion of several aspects of diagnosis and treatment.
"Kela" is a commercial rodenticide bait commonly used in Israel, made of wheat grains, which, according to its label, contains chlorophacinone. This product was involved in the death case of a man in which the victim's female companion was accused of assisting in this suicide and was subsequently convicted. Analysis of the wheat grains revealed zinc phosphide, whose use is restricted to authorized exterminators only, instead of chlorophacinone. Zinc phosphide was identified using microscopic examination, scanning electron microscopy/energy dispersive X-ray spectroscopy (SEM/EDX) and X-ray powder diffraction (XRD).
With implementation of the Food Quality Protection Act (FQPA), questions have been raised concerning the adequacy of current guideline testing under the Federal Insecticide, Fungicide and Rodenticide Act (FIFRA) to assure compliance with FQPA. Specifically, there have been questions about whether FIFRA testing is adequate to assure protection of the most sensitive individuals in the population that might be exposed to FIFRA-regulated chemicals. In most cases, concern has been expressed about protection of infants and children. One way to examine the adequacy of current testing is to retrospectively examine data generated from tests similar to, or the same as, standard FIFRA tests on chemicals with known effects on developing organisms, effects that occur at doses below the effect level for adults. Lead is an example of a compound that has been widely studied and where infants and children have been shown to be more susceptible than adults to certain types of lead-induced toxicity. A review of the available animal toxicity studies on lead compounds, studies that were similar in design to testing required under FIFRA, was performed and the adequacy of the studies for setting human exposure levels that would be protective of child and infant health was assessed. The assessment demonstrated that current guideline testing under FIFRA would have resulted in setting of an exposure level in humans that is below the current regulatory action level for lead, without the use of an additional FQPA safety factor.
Recently, a major topic of discussion has been the impact of synthetic chemicals that possess the capacity to alter hormonal activity, the so-called "endocrine modulators," with potentially the capacity to alter the reproductive capability of humans. Particularly, various synthetic pesticides and industrial chemicals that persist in the environment and/or bioaccumulate have been implicated. Further, it has been alleged that the standard tests for pesticide registration as required by the U.S. Environmental Protection Agency (EPA) and other regulatory agencies may be inadequate to detect endocrine modulating effects. To address these shortcomings, it has been proposed that very specific tests for estrogen receptor binding, or in vitro cell response to chemicals, be used to identify potential endocrine modulators. However, such approaches have certain flaws that limit their application as screens. First, very specific tests, like receptor binding, evaluate only a single chemical event per test. Such tests do not measure toxicity or biological response. Isolated systems are very important for studying mechanisms of action or structure activity relationships, but can only provide a preliminary screen for a single mechanism of toxicity. Isolated systems can not be used to regulate a chemical without additional information. Second, they fail to test many other parts of the neuroendocrine control of the reproductive system. Testing for adverse effects in highly specific in vitro systems failed to replace whole-animal models in carcinogenesis and will also fail in reproductive toxicology because this system is too complicated for such as in vitro approach to be accurately predictive. Advanced tests, such as the EPA multigeneration study, are more effective, and reliable means for evaluation than any specific and narrowly focused screening tests. Experience has shown that a better approach to testing chemicals is to evaluate their effects on the whole animal. When one part of the system is adversely affected, various processes may be indirectly affected and can be detected in the animal model. For example, a modulation of testosterone synthesis could lead to (1) altered accessory sex organ morphology, size, and function; (2) decreased sperm counts; and (3) even decreased fertility. These and many other effects would be noted in toxicity studies that are already required for the registration of crop protection chemicals. The developmental and reproductive toxicity guidelines were recently reviewed in a hearing that included the representatives from the EPA, the public, and the Scientific Advisory Panel. The EPA kept the basic study design the same, but added a few new endpoints to further assess chemical-induced effects on reproductive development and function. The review presented herein concentrates on the required Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) testing for pesticides, and demonstrates how the massive arrays of sensitive endocrine endpoints that are delineated in FIFRA Subdivision F have been successfully used to detect both weak and potent hormonally modulating chemicals. For example, (1) diethyl-stilbestrol (DES), which is a potent synthetic therapeutic estrogen, (2) DDT, which is weakly estrogenic but persistent and bioaccumulating, and (3) dioxins, which have antiestrogenic properties, were all found as being hormonally active in tests similar or identical to FIFRA tests. All food-use pesticides have been evaluated using a comprehensive multigeneration reproduction test. Hence, the FIFRA testing procedures have been demonstrated to identify endocrine modulators of sufficient potency to represent a concern to human health.
BACKGROUND: Successful organ donation has been reported after death from poisonings with cyanide, carbon monoxide, methanol, benzodiazepines, and tricyclic antidepressants. In this report, we describe a case of multiple organ donation from a previously healthy individual who died from poisoning with the long-acting anticoagulant rodenticide, brodifacoum. METHODS: Case report and review of the literature. RESULTS: All organs procured from the poisoned donor functioned adequately, and there were no hemorrhagic complications in any of the recipients. CONCLUSION: This case demonstrates that brodifacoum poisoning is not an absolute contraindication to organ donation from brain-dead patients who have sustained a fatal ingestion.
Reports concerning the ineffectiveness of warfarin rodenticide, used at farms and stores in a rural area about 8 kilometers in diameter near Raleigh, North Carolina, prompted subsequent laboratory testing. All of the 25 Norway rats trapped from the area survived 6 days of no-choice feeding of bait containing 0.025 percent (by weight) warfarin.
The first activity of the Federal Insecticide. Fungicide, and Rodenticide Act (FIFRA) Environmental Model Validation Task Force, established to increase confidence in the use of environmental models used in regulatory assessments, was to review the literature information on validation of the pesticide root zone model (PRZM) and the groundwater loading effects of agricultural management systems (GLEAMS). This literature information indicates that these models generally predict the same or greater leaching than observed in actual field measurements, suggesting that these models are suitable for use in regulatory assessments. However, additional validation research conducted using the newest versions of the models would help improve confidence in runoff and leaching predictions because significant revisions have been made in models over the years, few of the literature studies focused on runoff losses, the number of studies having quantitative validation results is minimal, and modelers were aware of the field results in most of the literature studies. Areas for special consideration in conducting model validation research include improving the process for selecting input parameters, developing recommendations for performing calibration simulations, devising appropriate procedures for keeping results of field studies from modelers performing simulations to validate model predictions while providing access for calibration simulations, and developing quantitative statistical procedures for comparing model predictions with experimental results.
A clinical syndrome, characterized by acute diabetic ketoacidosis associated with a toxic neuropathy, developed in five men who intentionally ingested a recently introduced rodenticide (Vacor) containing N-3-pyridylmethyl-N'-p-nitrophenyl urea (RH-787). A 7-yr-old boy, who accidentally ingested this poison, died within 14 h. Marked insulinopenia, without a reduction in glucagon levels, suggested a specific beta-cytotoxic effect, which was supported after autopsy in three cases by histopathologic evidence of extensive beta cell destruction. Lethal effects in rats prevented investigation of RH-787's diabetogenicity in vivo; however, studies in isolated rat islets confirmed a direct inhibitory effect, which was prevented by concomitant incubation with nicotinamide, suggesting a mechanism of action similar to that of streptozotocin. We detected islet cell-surface antibodies in two of four patients studied. These findings indicate that this nongenetic, acquired form of insulinopenic diabetes, which has persisted in the surviving patients for up to 3 yr, presents a unique opportunity to test in man the concept that hyperglycemia and the accompanying metabolic consequences of insulinopenia can induced diabetic microangiopathy in the absence of genetic predisposition.
A user interface to the U.S. Environmental Protection Agency pesticide root zone model (PRZM) was constructed to allow Monte Carlo sampling of input parameter distributions. The interface was constructed employing the Visual Basic for Applications development environment, along with the functionality of the Crystal Ball Professional forecasting and risk analysis package. The tool has been utilized by the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) Environmental Model Validation Task Force to perform detailed statistical analyses of model input parameter uncertainty and the propagation of this uncertainty on the model outputs as well as comparisons of modeled and field-measured data.
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