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Showing posts with label treatment. Show all posts

Sunday, 25 March 2018

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Health for all: Overview of Herbicide Poisoning

Health for all: Overview of Herbicide Poisoning: prevention is better than cure
Herbicides are used routinely to control noxious plants. Most of these chemicals, particularly the more recently developed synthetic organic herbicides, are quite selective for specific plants and have low toxicity for mammals; other less selective compounds (eg, sodium arsenite, arsenic trioxide, sodium chlorate, ammonium sulfamate, borax, and many others) were formerly used on a large scale and are more toxic to animals.
Vegetation treated with herbicides at proper rates normally will not be hazardous to animals, including humans. Particularly after the herbicides have dried on the vegetation, only small amounts can be dislodged. When herbicide applications have been excessive, damage to lawns, crops, or other foliage is often evident.
The residue potential for most of these agents is low. However, runoff from agricultural applications and entrance into drinking water cannot be ruled out. The possibility of residues should be explored if significant exposure of food-producing animals occurs. The time recommended before treated vegetation is grazed or used as animal feed is available for a number of products.
Most health problems in animals result from exposure to excessive quantities of herbicides because of improper or careless use or disposal of containers. When used properly, problems of herbicide poisoning in veterinary practice are rare. With few exceptions, it is only when animals gain direct access to the product that acute poisoning occurs. Acute signs usually will not lead to a diagnosis, although acute GI signs are frequent. All common differential diagnoses should be excluded in animals showing signs of a sudden onset of disease or sudden death. The case history is critical. Sickness following feeding, spraying of pastures or crops adjacent to pastures, a change in housing, or direct exposure may lead to a tentative diagnosis of herbicide poisoning. Generally, the nature of exposure is hard to identify because of storage of herbicides in mis- or unlabeled containers. Unidentified spillage of liquid from containers or powder from torn or damaged bags near a feed source, or visual confusion with a dietary ingredient or supplement, may cause the exposure. Once a putative chemical source has been identified, an animal poison control center should be contacted for information on treatments, laboratory tests, and likely outcome.
Chronic disease caused by herbicides is even more difficult to diagnose. It may include a history of herbicide use in proximity to the animals or animal feed or water source, or a gradual change in the animals’ performance or behavior over a period of weeks, months, or even years. Occasionally, it involves manufacture or storage of herbicides nearby. Samples of possible sources (ie, contaminated feed and water) for residue analysis, as well as tissues from exposed animals taken at necropsy, are essential. Months or even years may be required to successfully identify a problem of chronic exposure.
In order to recognize whether a subject is exposed to herbicides, or even accidental poisoning, now standardized analytical procedure for diagnostic investigation of biological materials have become established and these are subsumed under the term“biomonitoring”. Accurately biomonitoring is an important tool that can be used to evaluate human or animal exposure to such herbicides by measuring the levels of these chemicals, their metabolites or altered biological structures or functions in biological media such as urine, blood or blood components, exhaled air, hair or nails, and tissues  The use of urine has advantage because of ease of availability.  As such urine has been used for biomonitoring of several herbicides such as 2,4-D, 2,4,5-T, MCPA (2-methyl-4-chlorophenoxyacetic acid), atrazine, diuron, alachlor, metolachlor, paraquat, diquat, imazapyr, imazapic,  imazethapyr, imazamox,  imazaquin and  imazamethabenz-methyl with the objective to assess exposure and health risk to exposed subjects.

If poisoning is suspected, the first step in management is to halt further exposure. Animals should be separated from any possible source before attempting to stabilize and support them. If there are life-threatening signs, efforts to stabilize animals by general mitigation methods should be started. Specific antidotal treatments, when available, may help to confirm the diagnosis. As time permits, a more detailed history and investigation should be completed. The owner should be made aware of the need for full disclosure of facts in order to successfully determine the source of poisoning, eg, unapproved use or failure to properly store a chemical.
Toxicity and Management of Poisoning
There are >200 active ingredients used as herbicides; however, some of them are believed to be obsolete or no longer in use. Of these, several have been evaluated for their toxic potential and are discussed below. More specific information is available on the label and from the manufacturer, cooperative extension service, or poison control center. Selected information on herbicides, such as the acute oral toxic dose (LD50) in rat, the amount an animal can be exposed to without being affected (no adverse effect level), the likelihood of problems caused by dermal contact in rabbit (dermal LD50, eye and skin irritation), deleterious effects on avian species and toxicity to fish in water is included for some commonly used herbicides (TABLE 1). Comparative toxic doses (TD) and lethal doses (LD), of selected herbicides in domesticated species such as monkeys, cattle, sheep, pigs, cats, dogs, chickens is also summarized (TABLE 2). The information is only a guideline because the toxicity of herbicides may be altered by the presence of other ingredients (eg, impurities, surfactants, stabilizers, emulsifiers) present in the compound. With a few exceptions, most of the newly developed chemicals have a low order of toxicity to mammals. However, some herbicides such as atrazine, buturon, butiphos, chloridazon, chlorpropham, cynazine, 2,4-D and 2,4,5-T alone or in combination, dichlorprop dinoseb, dinoterb, linuron, mecoprop, monolinuron, MCPA (2-methyl-4-chlorophenoxyacetic acid), prometryn, propachlor, nitrofen, silvex, TCDD (a common contaminant during manufacturing process of some herbicides such as 2,4- D and 2,4,5-T), tridiphane and tridiphane are known to have adverse effects on development of

Overview of Herbicide Poisoning

By P. K. Gupta, PhD, Post Doc (USA), Hon DSc PGDCA, MSc VM & AH BVSc, FNA VSc, FASc, AW, FST, FAEB, FACVT (USA), Gold Medalist, Editor-in-Chief, Toxicology International
The Merck Veterinary Manual (2016). Chapter “Herbicide Poisoning” by PK GUPTA 11th edition, Merck & Co. Inc Whitehouse Station, NJ, USA  pp 2969-99
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Friday, 16 March 2018

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Overview of Pentachlorophenol Poisoning (Penta poisoning)



Pentachlorophenol (PCP), commonly known as penta, has been used as a fungicide, molluscicide, insecticide, and wood preservative. Its use is now permitted only for industrial purposes; agricultural and domestic uses are prohibited, because it is classified as a highly hazardous pesticide.
The oral LD50 of penta in rats is 150–210 mg/kg body wt. Common signs of poisoning include nervousness, rapid pulse and respiratory rate, weakness, fever, muscle tremors, convulsions, loss in righting reflexes, and asphyxial spasms followed by death. Corneal injury may result from splashes or vapor overexposure. Chronic poisoning results in emaciation, fatty liver, nephrosis, and weight loss.
The persistence of penta in soil and water and apparent widespread use has resulted in significant exposure to animals. Young swine have died after dermal exposure to freshly penta-treated wood used in farrowing crates or farrowing houses. In vivo studies in swine demonstrated that exposure to penta-contaminated soil can result in significant dermal absorption of the pesticide. Penta can be absorbed through intact skin and lungs and is an intense irritant to the skin and mucous membranes. Penta absorption in skin was greater in water or water-based mixtures than in 100% ethanol. Because animals typically have access to water at all times, this hydrophilic characteristic of penta suggests enhanced dermal absorption.
When absorbed, penta increases metabolism by uncoupling cellular phosphorylation. Animals fed in troughs made of lumber treated with PCP may salivate and have irritated oral mucosa. Both penta and its major metabolite, tetrachlorohydroquinone (TCHQ), can induce epidermal hyperplasia in mice.
Poultry have been exposed to sawdust and shavings from penta-treated wood. Associated adverse effects include reduced growth rates, kidney hypertrophy, and decreased humoral immune response. Penta exposure can also result in an off-taste to eggs and meat as a result of degradation of chlorophenols to chloroanisols. Vaporization or leaching of penta in pens, enclosures, homes, and barns has caused illness and death.
Cattle and pigs exposed to wood treated with commercial grade penta had increased mortality, possibly decreased fertility in boars, and reduced productivity (milk, meat, etc). The lethal dose in cattle and sheep is ~120–140 mg/kg body wt.
Commercial lots of technical-grade penta contain small but biologically significant amounts of highly toxic impurities such as chlorinated dioxins and dibenzofurans, tetrachlorophenols, and hydroxychlorodiphenyl ethers; these compounds can exert their own effects such as early fetotoxicity. Commercial-grade penta causes hepatic porphyria, increased microsomal monooxygenase activity, and increased liver weight. Pure penta was not teratogenic in rats.
Penta can cause residues in animal tissues. Also, a significant amount of hexachlorobenzene is metabolized in animal tissues to penta. Pentachlorophenol is considered to be a carcinogen and a tumor promoter, although studies have shown that the pure material does not increase the incidence of tumors in rats and mice. The technical-grade material has also been shown to be immunotoxic in laboratory studies. Penta must be handled very carefully and kept away from animal contact.
Whole blood analysis for penta may aid in the diagnosis of poisoning; diagnosis is usually made on the basis of the signs and the proximity of treated lumber in the animal’s environment.
There is no known antidote. Termination of exposure, bathing dermally exposed animals, oral administration of activated charcoal, and supportive therapy may be indicated. Bathing should be done gently with cold water and detergent so as not to cause vasodilation and increased absorption. Antipyretics, eg, aspirin and acetaminophen, should not be used. Treatment involves cooling the animal and administering fluids, electrolytes, and anticonvulsants. Read more --------

Overview of Pentachlorophenol Poisoning - Merck Veterinary Manual

www.merckvetmanual.com › Toxicology › Pentachlorophenol Poisoning
By P. K. GuptaPhD, Post Doc (USA), PGDCA, MSc VM & AH BVSc, FNA VSc, ... FAEB, FACVT (USA), Gold Medalist, Editor-in-Chief, Toxicology International.
The Merck Veterinary Manual (2016). Chapter “Pentachlorophenol Poisoning” by PK GUPTA 11th edition, Merck & Co. Inc Whitehouse Station, NJ, USA pp 3052-53
·         Pentachlorophenol Poisoning



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