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Vet Guide

Rodent Threat
Rodent Control
Anticoagulant Rodenticides - A Success Story
Anticoagulant Safety
Acute Oral Toxicities to Dogs
Acute Oral Toxicities to Cats
Case Study I
Case Study II
Case Study III
Recommendations for Treatment
Bibliography

Rodent Threat

Rodents are among the most important competitors with humans for food and other resources. It has been estimated that worldwide there is one rat for every human being. Both rats and mice constitute a major threat to mankind because of the disease organisms they harbor and damage they cause. The Food and Agricultural Organization of the United Nations reported that in 1982, worldwide, rats destroyed more than 42 million tons of food worth $30 billion. Other reports indicate that one-fifth to one-third of all the world's food crops are consumed or contaminated by rats each year. Moreover, in the past century alone, more than 10 million people have died from rodent-borne diseases. Thus, rodent pest management is essential to achieving and maintaining an acceptable standard of living.

In the United States, the adoption of rodent control measures by homeowners and public health and professional pest control personnel has prevented the extreme losses seen in some developing countries. Nonetheless, each year an estimated 50,000 Americans, mostly children, are bitten by rats. Property losses include millions of dollars worth of food consumed or contaminated on farms and in warehouses. In addition, numerous building fires are attributed to rodents chewing lead gas pipes or stripping insulation from electrical wires. Furthermore, the diseases carried by rodents in this country are numerous and include murine typhus, rickettsial pox, lymphocytic choriomeningitis, tularemia, leptospirosis, trichinosis, salmonellosis and dysentery. And each year, the several human deaths in the Western states resulting from sylvatic rodent-borne plague serve to remind us of the potential for disaster if we relax rodent control measures [47].

In addition to spreading human diseases or causing damage to buildings and their contents, rodents can severely affect the health of farm and domestic animals. Rat attacks on animals such as newborn pigs and poultry cause death and mutilation, and numerous animals suffer illness or death from rodent-borne diseases.

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Rodent Control

Against this background of rodent problems, commendable efforts have been seen in the development of more effective and more practical rodent control methods. While trapping rodents has been practiced for about 5,000 years, modern traps are easier to set and some feature a multiple catch capability. Other non-chemical methods of rodent control include public health education, physical exclusion of rodents, and sanitation measures, all of which are aimed at denying rodents food and shelter, measures that should form a primary part of any rodent control program. Unfortunately, non-chemical methods are time-consuming, may not always be practical or affordable, and used alone may not achieve acceptable short-term results. For these reasons, the use of rodenticides plays a vital role in most integrated rodent management programs.

Rodenticide use is not a new approach. Aristotle reported the use of strychnine for rodent control in 350 B.C. For the next 23 centuries, until 1950, the various rodenticides which were used could all be described as acute or single exposure toxicants. They included botanical extracts (e.g. red squill and strychnine), inorganic chemicals (e.g. arsenic, phosphorus and thallium sulfate) and, in the 20th century, various synthetic organic chemicals (e.g. ANTU, DDT and sodium fluoroacetate). In addition to the aforementioned chemicals which were used to make rodenticide baits, various fumigants, including hydrogen cyanide and carbon bisulfide, were used for many decades prior to 1945 [47].

Acute rodenticide baits and fumigants have the advantage of potentially producing a fast kill of rodents, sometimes within a few minutes. However, in the case of baits, the rodents often relate eating the bait to the onset of poisoning symptoms. This results in some rodents ceasing bait consumption before they have taken a lethal dose and, thereafter, becoming bait shy and virtually impossible to control with the same bait. Another important disadvantage of the acute rodenticides is that they are nearly all highly toxic to non-target species, including people, a drawback made worse by the absence of specific antidotes. However, some acute rodenticides, e.g. zinc phosphide and red squill, do have a good safety record due to their taste, odor and color character-istics, which attract rodents while repelling most domestic animals. The addition of emetics to some acute baits offers added protection since rats and mice cannot regurgitate [35]. However, the addition of emetics or substances which repel non-target species may reduce palatability of the bait to rodents.

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Anticoagulant Rodenticides - A Success Story

In the 1940s, with the development of warfarin and later pindone, a new class of rodenticides became available which substantially improved chemical control of rodents and was less hazardous than some older acute rodenticides. These new compounds are anticoagulants and their mode of action involves reducing the ability of blood to clot so that exposed animals bleed internally and die.

Anticoagulants are cumulative poisons and act relatively slowly compared to most acute rodenticides; rodents typically die several days after initial ingestion if anticoagulant consumption has been steady. The usually slow onset of undramatic toxic effects allows anticoagulant baits to be formulated with very low concentrations of active ingredient, which avoids their being repellent. Typically, rodents feed repeatedly on the rodenticide bait without becoming bait shy. In the case of warfarin and other so-called first-generation anticoagulant baits, multiple feeding over several days is usually necessary before a lethal dose accumulates in the rodent.

If the problem is identified or diagnosed early, the slow action of the first-generation anticoagulants allows more time for treatment of poisoned non-target species than with most non-anticoagulant materials. Most important, vitamin K1 is an effective antidote for anticoagulant poisoning. For these reasons, and because of their effectiveness, anticoagulants have become the most widely used type of rodenticide. An estimated 95% of all chemical control of commensal rodents in the United States is now conducted with anticoagulants, and application of most acute rodenticides is restricted to professional use.

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Anticoagulant Safety

In general, anticoagulant rodenticides have had a good reputation for safety. This reputation is based on their widescale use by amateurs and professionals with relatively few serious incidents of poisoning of non-target species, despite numerous exposure incidents. Human poisoning records indicate that anticoagulant poisonings are substantially less than poisonings from medicines, alcohol and other household chemicals. Regarding animals, in the first three years (September 1978 to August 1981) of HOTLINE calls to the Animal Poison Control Center at the University of Illinois Urbana, 4.4% of total calls related to anticoagulants. In 1982, anticoagulants accounted for 8% of HOTLINE calls and ranked fourth in concern, behind insecticides, toxic vegetation and certain household products [16, 17]. In 1983, the number of calls for all poisonings had increased, as did the percentage of anticoagulant-related calls, which were more than 10% [15]. For the year July 1982 to June 1983, about 0.8% of all calls to LAMARPIC (Los Angeles Medical Association Regional Poison Information Center) related to anticoagulant exposures of all species [57]. This represented about 8% of all their pesticide calls; 41% of all anticoagulant calls involved dogs, a fact also found in other countries [45].

Considering that more than 25 million pounds of anticoagulant bait are estimated to be used each year in the United States, the safety record is impressive but hardly surprising. After all, such baits contain low concentrations of toxicant and their mode of toxic action and the availability of an antidote make death of non-target domestic animals unlikely, particularly when veterinary intervention is available. A survey of 483 dogs treated by veterinarians for warfarin poisoning in England showed that the majority (81%) recovered, although the number that succumbed was significant and the costs incurred for veterinary care were considerable [9]. Similar results were noted in a recent survey of United States veterinary institutions: 35 dogs (22%) died of the 158 poisoned with warfarin (or associated anticoagulants generically termed as such), where the outcome was known [26]. Fortunately, permanent effects from sublethal intoxication with anticoagulants are rare.

The past good safety record of anticoagulants is no reason for complacency. Recent events indicate that more care in their use by both professional and non-professional applicators is essential because a wider variety of anticoagulant rodenticides is now available, some of which are widely used and differ markedly from warfarin in toxicity and effects on rodents and non-target species [33, 48].

The anticoagulants first marketed in the 1950s could be described as multiple-dose or multiple-feeding anticoagulants. Warfarin, pindone and isovaleryl indandione (PMP) are examples of such first-generation anticoagulants. These products, as formulated into baits, are only moderately toxic to rodents and most non-target species, and normally achieve their lethal effects only when repeated feedings over several days produce an accumulation of the compound within the body. A single feeding by a rodent or non-target animal is usually sublethal. The challenge is to place these baits where they will be frequently consumed by rodents and not by non-target species.

Two baits introduced later in the 1950s and 1960s utilized more potent anticoagulants: diphacinone (trade names include Ditrac®, Promar®, Ramik®) and chlorophacinone (trade names include Rozol®). These products also tend to be more toxic to certain non-target species, although chlorophacinone is about as toxic as warfarin to dogs and cats and is apparently less toxic to humans and swine than warfarin.

In the past 15 years, we have seen the introduction of second-generation anticoagulants, which are based on three toxicants which are many times more acutely toxic to rodents than warfarin [10, 28, 40]. These are brodifacoum (trade names include Ratak®, Talon®, Havoc®, Klerat®); bromadiolone (trade names include BootHill®, Maki®, Super-Caid®, Just One Bite® brand, Bromone®, Contrac®); and difethialone (trade names include Hombre®, Generation®, and D·Cease®). Even low concentration (0.005%) baits based on brodifacoum and bromadiolone toxicants and even lower concentration (0.0025%) baits with difethialone are capable of producing rodent kill after a single feeding; hence they are commonly referred to as single-feeding anticoagulants (although in practice rodents feed repeatedly and can accumulate much more than a lethal dose).

Unfortunately, these three toxicants and diphacinone, mentioned above, are much more acutely toxic to non-target species like dogs and cats than the older anticoagulants such as warfarin. Of these, brodifacoum has appeared to be the most toxic to dogs and swine [5, 26, 38]. Indeed, in 1984, HOTLINE calls to the Animal Poison Control Center showed that the number of rodenticide-related calls had risen to first place, with 17% of total calls, ahead of calls related to insecticides and toxic vegetation. More than 92% of these rodenticide-related calls were due to anticoagulants and, of those calls where toxicosis or suspected toxicosis was assessed, 57% were due to brodifacoum [52]. These estimates may be biased because only a few rodenticide product labels include the HOTLINE number. Tables 1 and 2 compare the acute oral LD50 (where known) of first- and second-generation anticoagulants for dogs and cats.

In practical terms, these differences in acute oral LD50 potentially mean that, in the case of the most toxic products, a single bait station or consumer packet contains enough product (a few to several ounces) to kill an otherwise healthy 22-pound dog which consumes the entire contents at one time. In contrast, the same dog may need to eat the contents of 15 or more bait stations or consumer packets containing more than 35 ounces of 0.05% warfarin bait before consuming a lethal dose. However, the differences between anticoagulants go far beyond differences in acute oral LD50 values. Some of the newer anticoagulants have longer or much longer biological half-lives than warfarin and may remain in the body at a toxic level for many months [41]. The prolonged turnover may reflect differences in metabolic rates, tissue and blood release of compounds, binding to blood or other cells and plasma proteins, and genetic susceptibility or resistance. By contrast, compounds other than warfarin have a longer residue half-life in tissues [55]. The residue half-life is clearly of importance both from the viewpoint of treating poisoned animals and in the potential for secondary poisoning when companion animals or wildlife consume poisoned rodents [49]. A long biological half-life also increases the possibility of primary intoxication in non-target species such as dogs, which may repeatedly consume sublethal doses with an additive lethal outcome.

Considering these differences among anti-coagulants, it is indeed unfortunate, whether from ignorance or apathy, that both amateur and professional users of rodenticides often use (and misuse) all anticoagulants as though they were as safe as warfarin. The result is an increasing number of severe or fatal poisoning incidents involving non-warfarin toxicants. The problem is exacerbated when, in the absence of information to the contrary, veterinarians treat the animals for generically-assigned warfarin poisoning when, in the case of more toxic anticoagulants, the animal may require much more extensive antidotal therapy and supportive treatment [13, 20, 43, 44]. For instance, in many cases involving brodifacoum poisoning of dogs, the animals died after being sent home following veterinarian examination and treatment for anticoagulant poisoning. The majority of these animals could have been saved by extending antidotal therapy.

The following case histories are representative of the range of dog poisoning incidents involving anticoagulants now being encountered and thus may be of use to veterinarians when designing treatment programs. While the focus in this brochure is on anticoagulant poisoning, it is important that veterinarians understand that acquired or inherited hemostatic defects (e.g. disseminated intravascular coagulation, liver disease, quantitative and qualitative platelet defects, von Willebrand's disease, and the hemophilias) may produce symptoms that can be confused or concomitant with anticoagulant poisoning. The various coagulation tests and their limitations should also be borne in mind when making differential diagnoses [23, 30]. Dog poisoning case histories have been chosen because these represent a substantial majority of the companion animal poisoning incidents which are reported [16, 26, 39, 45, 46, 48, 57]. However, poisoning of cats, birds, horses and other animals are also reported and their treatment would similarly vary according to the type of anticoagulant to which they had been exposed.

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Acute Oral Toxicities to Dogs

I II III IV V
Generic Name
(Trade Name*)
LD50 of Active Ingredient
(mg/kg)†(a)
Usual %
Active Ingredient in Bait
Quantity of Bait to Give LD50 in10 kg (22 lb) Dog Source of Data for Column II

(see Bibliography)
brodifacoum
(Havoc, Talon, d-CON)
0.25-1.0
0.25-2.5
1.09-3.6
0.005 50 g (1.8 oz) to
720 g (25.4 oz)
4, 5, 38
31
27
bromadiolone
(BootHill, Maki, Contrac)
11-15 (b)
15-20
15-20
0.005 2,200 g (77.6 oz ) to
4,000 g (141.2 oz)
29
2, 56
43
chlorophacinone
(Rozol)
50-100
50-100
50-100
0.005 10 kg (352.7 oz) to
20 kg (705.4 oz)
56
39
56
coumafuryl
(Fumarin)
equal to warfarin 0.025 -- 7
diphacinone
(Diphacin, Ditrac, Promar, Ramik)
0.88
3.0-7.5
5.15
0.005 176 g (6.2 oz) to
3,000 g (105.8 oz)
37
34, 51, 56
7, 14, 42
isovalerylindandione
(PMP, Valone)
unknown (c) 0.055 -- 22
pindone
(Pival)
4
75-100
0.025 160 g (5.6 oz) to
4,000 g (141.1 oz)
25
11
warfarin
(Coumafene)
20-50 (d)
200
200-300
0.025
or
0.05 (e)
400 g (14.1 oz) to
6,000 g (211.6 oz)
8, 12, 38, 53
51
14, 32
difethialone
(Hombre, Generation, D·Cease)
4 0.0025 1600 g (57.1 oz) 59

*Common examples of trade names. This does not imply endorsement of these products by either the authors or their respective affiliations.

Table 1 Footnotes

†Key to Column II and III

a.Underscored LD50 range used in calculating Column IV.

b.This is derived from a study which was not designed to obtain an LD50 .

c.Secondary poisoning studies suggest that isovaleryl indandione baits are more hazardous to dogs than warfarin baits (Evans and Lorin, 1967). It is now mostly used in the form of a 2% tracking powder.

d.This LD50 range was originally established by the U.S. Fish and Wildlife Service, 1949.

e.This bait concentration used for calculating Column IV.

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Acute Oral Toxicities To Cats

I II III IV V
Generic Name
(Trade Name*)
LD50 of Active Ingredient
(mg/kg)†(a)
Usual %
Active Ingredient in Bait
Quantity of Bait
to Give LD50 in
2 kg (4.4 lb) Cat
Source of Data for Column II

(see Bibliography)
Brodifacoum
(Havoc, Talon, d-CON)
25 (approx.) 0.005 1,000 g (35.3 oz) 3, 5, 38
Bromadiolone
(BootHill, Maki, Contrac)
25 (approx.) (b) 0.005 1,000 g (35.3 oz) 1
Chlorophacinone
(Rozol)
unknown 0.005 --- --
Coumafuryl
(Fumarin)
unknown 0.025 -- --
Diphacinone
(Diphacin, Ditrac, Promar, Ramik)
5-15
15
0.005 200 g (7.0 oz) to
600 g (21.2 oz)
7, 14, 42
3
IsovalerylIndandione
(PMP, Valone)
unknown 0.055 -- --
Pindone
(Pival)
unknown (c) 0.025 -- --
Warfarin
(Coumafene)
5-50 (d)
6-40
200-300
0.025
or
0.05 (e)
100 g (3.5 oz) to
6,000 g (211.6 oz)
8, 18 38
14
Difethialone
(Hombre, Generation, D·Cease)
>16 0.0025 1,280 g (45.7 oz) 60

*Common examples of trade names. This does not imply endorsement of these products by either the authors or their respective affiliations.

Table 2 Footnotes

†Key to Column II and III

a.Underscored LD50 range used in calculating Column IV.

b.This figure is actually the maximum tolerated oral dosage (MTD).

c.Secondary poisoning studies suggest that pindone has low toxicity to cats (Beauregard et al., 1955).

d.Cats are generally regarded as being as susceptible as dogs to warfarin. The range of LD50 may be partly explained by increased susceptibility to poisoning during estrus (Spencer, 1950).

e.This bait concentration used for calculating Column IV.

The following case studies taken from the files of the Laboratory of Hematology of NYSDH exemplify three common scenarios with respect to anticoagulant rodenticide poisonings and have been summarized in Table 3. Diagnostic and therapeutic regimes reflect a composite of inputs including foreign sources [19, 20, 36, 44, 50].

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Case Study I

History:

A three-year-old, spayed female terrier was admitted to a veterinarian's office because of recent clinical signs of occasional bleeding from the gums accompanied by the presence of black, tarry stools. On questioning the owner, there had been no previous history of a bleeding tendency and no known exposure to anticoagulant rodenticides or other toxicants.

Course of Action:

The referring veterinarian in considering the history rules out the likelihood of a congenital coagulation defect because the animal was spayed uneventfully and had no previous history of excessive bleeding. Suspecting rodenticide toxicosis, the veterinarian has two courses of action to recommend:

1. The preferred option involves collection of blood samples to perform routine hemograms and coagulation profiles, plus immediate treatment with vitamin K1 and blood transfusion(s), if the latter are needed to control bleeding. Once laboratory data are available, vitamin K1 treatment can cease if results rule out anticoagulant rodenticide exposure. As the time from ingestion of rodenticide to sampling is unknown in many confirmed cases, treatment should continue for 4-6 weeks to control the long-term effects of the more toxic first- or second-generation anticoagulants. The alternative is to serially monitor coagulation weekly or biweekly until values return to normal limits, although costs may be substantial here.

2. The alternative option, when costs are a factor for the client, is to initiate and maintain treatment without confirmatory laboratory data. This is less desirable because the suspected diagnosis cannot be confirmed, thus failing to provide adequate documentation should it be needed, and treatment must be maintained for 4-6 weeks in the absence of serial monitoring for the reasons stated above.

Note that induction of vomiting is not recommended in such cases because the animal is already bleeding, and retching may aggravate the situation. Also, if rodenticide exposure is the cause, the toxicant has already been absorbed as clinical signs are evident and vomiting is unwarranted.

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Case Study II

History:

A six-month-old intact Doberman pinscher female was admitted to a veterinarian's office with a swollen stifle. X-rays revealed only a soft tissue swelling. However, epistaxis began the next day and continued until the hematocrit had dropped to 13%. The owner indicated that on searching the area where the dog usually exercised, small amounts of material like warfarin were found. A local rancher admitted to placing the toxicant in the surrounding area to control rodents in the past few days, and the dog's owner failed to keep the dog confined to his own property.

Course of Action:

Upon admission but prior to the onset of clinical signs obviously referable to bleeding, the veterinarian should:

1. Induce vomiting, as toxicant exposure is known and one needs to eliminate any remaining, unabsorbed stomach contents.

2. Examine and identify sample of poison, if available.

3. Collect blood samples for diagnostic tests (as described in Case Study I above).

4. Initiate treatment (as described in Case Study I above).

As toxicant exposures may need to be proven to establish responsibility for the incident, it is especially important that properly collected blood samples (anticoagulated with citrate or 'blue-top' Vacutainer® tubes, and not with EDTA or 'purple-top' Vacutainers) be obtained. Coagulation profiles and preferably specific clotting factor assays should be performed as soon as possible on the plasma prepared from the patient's whole blood. Ideally, the blood should be immediately spun to remove plasma, and this should be put on ice if testing is delayed. These tests are usually run only at commercial clinical reference laboratories or by veterinary teaching institutions or specialized laboratories such as the NYSDH Laboratory of Hematology in Albany, New York.

In the specific case described here, the animal's clinical signs were more severe than would be expected by exposure to a standard warfarin product. The clue comes from the fact that the patient is a Doberman pinscher, a breed known to have a high prevalence (50%) of von Willebrand's disease (VWD), an inherited bleeding disorder, as well as hypothyroidism, which also produces a bleeding tendency [19]. Thus the animal should be blood tested for both VWD and thyroid function. As it turns out, many of the recently studied rodenticide poisoning cases involving Dobermans kept as guard dogs and allowed to roam free also had VWD, which aggravated their clinical course upon rodenticide ingestion [26]. Prompt treatment with vitamin K1, whole blood transfusions and thyroid supplementation if needed, is especially important in such cases.

The above situations emphasize certain breed susceptibilities to complications arising from poisonings or low-dosage exposures which might otherwise be of little consequence. Another example is with whippets and greyhounds, two breeds known to have an overall lower tolerance to toxicants. The physiological and health status of the animal (e.g. estrous, pregnant, pseudo-pregnant, hypothyroid, debilitated, geriatric, etc.) at the time of exposure can also contribute significantly to the severity of signs and outcome of the case.

The size of the exposed animal is important as well, because smaller animals can go into shock and become moribund more rapidly from blood loss. Massive bleeding into the gastrointestinal tract can produce ileus with delayed emptying of the bowel. In such cases, there may be no overt signs of hemoptysis or melana, but just progressive weakness or collapse. It is critical to monitor the hematocrit here, for if it continues to drop precipitously, internal bleeding should be suspected. Prompt treatment with whole blood transfusions and vitamin K1 should reverse the situation. Usually within the next 12-24 hours, black, tarry stools will begin to be passed as the ileus relaxes.

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Case Study III

History:

An eight-year-old, intact golden retriever male was found by the owner lying in the backyard with blood running from the nose; black, tarry feces were noticed nearby. The owner immediately rushed the animal to the nearest veterinary clinic where rodenticide toxicosis was the presumptive diagnosis. The dog was treated with a fresh whole blood transfusion (300 cc) and vitamin K1.

On questioning the owner, he related that a pest control operator (PCO) had placed a second-generation rodenticide product in the neighborhood for rodent control, but had assured the local residents that the product was 'entirely safe around pets'. Nevertheless, the animal made a dramatic and uneventful recovery and was sent home three days later with oral vitamin K1 supplementation prescribed for five days' duration. Two weeks after the initial hemorrhagic crisis, the dog became lethargic and refused to eat; the following day he collapsed and was readmitted to the veterinary clinic. At this time blood samples were collected for routine hemagrams and coagulation tests, and the toenail bleeding time exceeded 15 minutes (normal range up to 6 minutes), at which point the nail was cauterized and bleeding ceased. The animal was treated again with vitamin K1 pending laboratory results, which confirmed the persistence of anticoagulant poisoning.

Course of Action:

In cases such as this one it is important to:

1. Obtain a sample of the product or discuss the matter with the PCO involved, and thereby identify the suspected causative toxicant.

2. Collect blood samples for coagulation tests to confirm the diagnosis, as it was suspected that a more toxic rodenticide, having a prolonged in vivo metabolic half-life, was involved.

This case serves to emphasize the importance of treating poisoned animals for several weeks to control the long-lasting effects of newer, more toxic products and the need for education of professional pest control operators, homeowners and veterinarians about the enhanced toxicity and dangers of such products to non-target species. All too often, poisonings are generically referred to as warfarin to include any type of anticoagulant rodenticide. Such mistakes can be costly to the animal and the client.

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Recommendations For Treatment

The principles of treatment and management of anticoagulant rodenticide poisoning are summarized in Table 4. Basically, once blood samples have been collected for the requisite diagnostic tests, the affected animal should receive a parenteral injection of vitamin K1. This form of the vitamin is preferred because vitamin K3 has little or no effect for the acute stages of poisoning [50]. Also, vitamin K1 should not be given intravenously, as the manufacturer's insert clearly recognizes the hazard of anaphylaxis from intravenous use of this product. On numerous occasions, the authors have been informed of situations where anaphylaxis was associated with intravenous vitamin K1, a circumstance which may not be defensible in subsequent litigation. Treatment with vitamin K1 should continue for up to 4-6 weeks unless laboratory monitoring of coagulation shows that values have returned to normal limits sooner. In cases where the toxicant is known to be warfarin rather than generically referred to as such, vitamin K1 supplementation is usually needed for up to 5-7 days. However, when identity of the toxicant is unknown, it is prudent to assume that one of the more toxic, longer-lasting products is involved.

The dosage of vitamin K1 given should generally not exceed 1 mg/lb/day, or at least should be given cautiously if higher doses are deemed necessary [20]. Doses exceeding 2 mg/lb/day may be dangerous and have been shown recently to induce Heinz body hemolytic anemia [24]. In our extensive experience with the monitoring and treatment of rodenticide poisoning cases, we have not had to exceed 1 mg/lb/day of vitamin K1 for successful control of bleeding [20]. This regimen is about half the dosage recommended recently by Mount and Feldman [50, 51]. Regardless of the anticoagulant involved, it is important to initiate therapy promptly. When the product has not been identified, as frequently occurs, it is necessary to follow the regimen of prolonged treatment outlined in Table 4 to avoid relapse and to reduce the overall cost to the client.

For severely poisoned cases, bleeding may have caused serious anemia and therefore also necessitates one or more transfusions with fresh compatible whole blood. In addition to transfusions, where animals have bled in the pulmonary, pleural or pericardial cavities, surgical intervention may be necessary to remove blood to give space for lung or cardiac function. Once the poisoned animals are under treatment and are recovering, it is important to keep them quiet, confined and on a softened diet, for another 2-7 days (depending on the toxicant involved) to minimize hemorrhage in locations such as the central nervous system. Foods rich in vitamin K are green, leafy vegetables (especially broccoli, green beans and lettuce). As vitamin K replenishes circulating clotting factors in a time course consonant with their respective synthetic half-lives, it takes several days for severely depleted animals to resynthesize these factors and no longer be at risk for bleeding complications.

Finally, in cases of acute emergencies related to poisonings, call Chemtec at 1-800-424-9300.

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Bibliography

1.ANONYMOUS. (Undated). Maki bromadiolone. Rodenticide technical bulletin. Chempar Chemical Co. Inc., New York, NY. 9pp.

2.ANONYMOUS. (Undated). Rozol and Maki, Chempar Rodent Control Products. Chempar Chemical Co. Inc., New York, NY. 11pp.

3.ANONYMOUS. (Undated). Klerat, ICI Public Health Products. ICI Surrey, England. 39pp.

4.ANONYMOUS. (Undated). Talon technical information: for experimental use only.ICI Americas Inc., Goldsboro, NC. 4pp.

5.ANONYMOUS. 1978. Talon rodenticide technical information: for experimental use only. ICI Americas Inc., Wilmington, DE. 4pp.

6.ANONYMOUS. (Undated). Technical report on chlorophacinone (approved name). Lipha Laboratories, Lyon, France. 72pp.

7.ANONYMOUS. 1977. Rodent eradication and poisoning programs. U.S. Dept. H.E.W., P.H.S., CDC, Atlanta, GA. 83pp.

8.ANONYMOUS. 1949. U.S.D.I. Fish and Wildlife Service, Denver, CO. Special report, 58.

9.ASHWORTH, B. 1973. The frequency of animal poisoning by warfarin. The Veterinary Record, 93:50.

10.BARLOW, A.M., A.L. GAY and B.K. PARK. 1982. Difenacoum (Neosorexa) poisoning. British Medical Journal, 285:541.

11.BEAUREGARD, J.R., T.W. TUSING and R.F. HANZEL. 1955. Toxicity and antidotal studies on 2-pivalyl-1,3-indandione (Pival), an anticoagulant rodenticide. Agricultural and Food Chemistry, 3(2):124-127.

12.BENTLEY, E.W. and Y. LARTHE. 1959. The comparative rodenticidal efficiency of five anticoagulants. Journal of Hygiene, 57(2):135-149.

13.BRAITHWAITE, G.B. 1982. Vitamin K and brodifacoum. Journal of American Veterinary Medical Association, 181:531-532.

14.BROOKS, J.E. 1970. Properties, uses and hazards of common rodenticides. NYS Dept. Health, Albany, NY, 10pp.

15.BUCK, W.B. 1983a. Personal communication (Dec. 16, 1983). Director, Animal Poisoning Control Center, Univ. IL, Urbana, IL.

16.BUCK, W.B. 1983b. A report of poisonings in the dog and cat in 1982. Presented at 75th Annual Conference for Veterinarians, NYS College of Veterinary Medicine, Ithaca, NY, 18-20 Jan., 1983.

17.BUCK, W.B. 1983c. Causes of poisoning in dogs and cats. Pest Management, 2(7):11-13.

18.BUCK, W.B., G. D. OSWEILER and G.A. VAN GELDER. 1976. Clinical and diagnostic veterinary toxicology, 2nd Edition. Kendall/Hunt Publishing Co., Dubuque, IA. pp. 253-256.

19.DODDS, W.J. 1984. Von Willebrand's disease in dogs. Modern Veterinary Practice, 95:681-686.

20.DODDS, W.J. and S.C. FRANTZ. 1984. Dog and cat poisonings. Pest Control Technology, 12(3):14.

21.EBELING, W. 1978. Urban entomology. University of California Press, Berkeley. 695pp.

22.EVANS, J. and A.L. WARD. 1967. Secondary poisoning associated with anticoagulant-killed nutria. American Veterinary Medicine Association. 151(7):856-861.

23.FELDMAN, B.F. 1981. Coagulopathies in small animals. Journal of American Veterinary Medical Association, 179:559-563.

24.FERNANDEZ, F.R., A.P. DAVIES, D.J. TEACHOUT, A. KRAKE, M.M. CHRISTOPHER and V. PERMAN. 1984. Vitamin K-induced Heinz body formation in dogs. Journal of American Animal Hospital Association, 20:711-720.

25.FITZEK, A. 1978. Pharmacokinetics of 2-pivaloylindan-1,3-dione in dogs. Acta Pharmacol. et Toxicol. 42:81-87.

26.FRANTZ, S.C., W.J. DODDS and S. KIM. 1984. A study of accidents, illnesses and deaths resulting from the use of commensal rodenticides. EPA Public Hearings on Rodenticide Bait Stations, Sacramento, CA, March 5, 1984.

27.GODFREY, M.E.R., T.C. REID and H.J.F. McALLUM. 1981. The oral toxicity of brodifacoum to rabbits. N.Z. Journal of Experimental Agriculture, 9:23-25.

28.GODFREY, M.E.R., T.C. REID and H.J.F. McALLUM. 1981. The acute oral toxicity of the anticoagulant brodifacoum to dogs. N.Z. Journal of Experimental Agriculture, 9:147-149.

29.GRAND, M. 1976. Experimental data on a new anticoagulant raticide: bromadiolone. Phytiatrie-Phytopharmacie, 25:69-88.

30.GREEN, R.A., P. ROUDEBUSH, and C.L. BARTON. 1979. Laboratory evaluation of coagulopathies due to vitamin K antagonism in the dog: three case reports. Journal of the American Animal Hospital Association 15:691-697.

31.HADLER, M.R. 1979. Brodifacoum _ a potent new rodenticide. Proceedings Fifth British Pest Control Conference, Stratford-upon-Avon, England. September 26-29, 1979. pp.1-8.

32.HAGAN, E.C. and J.L. RADOMSKI. 1953. The toxicity of 3-(acetonylbenzyl)-4-hydroxycoumarin (warfarin) to laboratory animals. Journal of American Pharmaceutical Association. 52(6):379-382.

33.HAYES, W. 1982. Pesticides studied in man. Williams and Wilkins, Baltimore, 672pp.

34.HAZELTON LABORATORIES Inc. 1957. Report on diphacinone (2-diphenylacetyl-1,3-indandione). Hazelton Laboratories Inc., Falls Church, VA, April 19, 1957.

35.HOUPT, K., J.C. ZGODA and C.C. STAHLBAUM. 1984. Use of taste repellents and emetics to prevent accidental poisoning of dogs. American Journal of Veterinary Research, 45:1501-1503.

36.KECK, P. 1984. Diagnostic analytique et traitement des intoxications des carnivores. Department of Pharmacology and Toxicology, National Veterinary School, Lyon, France. 19(2):129-131.

37.KOSMIN, M. and J.N. BARLOW. 1976. Rodent control using a novel formulation of diphacinone, Ramik®. Proceedings First Afro-Asian Vertebrate Pest Congress. Nov. 8-11, 1976. Cairo, Egypt. 7pp.

38.KAUKEINEN, D.E. 1979. Experimental rodenticide (Talon) passes lab tests; moving to field trials in pest control industry. Pest Control 46(1):19-21.

39.LABE, J. and G. LORGUE. 1977. Intoxication des carnivores domestiques par les raticides anticoagulants. pp128-140. Notes de Toxicologie Veterinaire, No. 3. Centre d'Informations Toxicologiques Veterinaire, Ecole Nationale Veterinaire, Marcy L'Etoile, France.

40.LECK, J.B. and B.K. PARK. 1981. A comparative study of the effects of warfarin and brodifacoum on the relationship between vitamin K1 metabolism and clotting factor activity in warfarin-susceptible and warfarin-resistant rats. Biochemical Pharmacology, 30:123-128.

41.LIPTON, R.A. and E.M. KLASS. 1984. Human ingestion of a 'Superwarfarin' rodenticide resulting in a prolonged anticoagulant effect. Journal of American Medical Association, 252:3004-3005.

42.LISELLA, F.S., K.R. LONG and H.G. SCOTT. 1971. Toxicology of rodenticides and their relationship to human health. Part II, Journal of Environmental Health, 33(4):361-365.

43.LORGUE, G. 1980. Bromadiolone toxicity in the dog: an antidotal therapy in the intoxicated dog. Laboratory of Toxicology, Ecole National Veterinaire de Lyon and Lyonnaise Industrielle Pharmaceutique, Lyon, France.

44.LORGUE, G. 1984. Domestic animal poisonings by rodenticides. Pratique Medicale et Chirurgicale de l'Animale de Compagnie. Ecole National Veterinaire de Lyon, Charbonnieres-les-Bains, France. 19(2):133-135.

45.LORGUE, G. and A. NAHAS. 1984. Les intoxications des carnivores domestiques: generalites. Pratique Medicale et Chirurgicale de l'Animal de Compagnie. Ecole National Veterinaire de Lyon, Charbonnieres-les-Bains, France. 19(2):125-127.

46.MADDY, K.T. and J. WINTER. 1980. Poisoning of animals in the Los Angeles area with pesticides during 1977. Veterinary and Human Toxicology, 22:409-412.

47.MALLIS, A. 1982. The handbook of pest control. Franzak and Foster, Cleveland OH. 1101pp.

48.MARSH, R.E. 1985 (in press). The susceptibility of dogs to anticoagulant rodenticides.

49.MENDENHALL, V.M. and L.F. PANK. 1980. Secondary poisoning of owls by anticoagulant rodenticides. Wildlife Society Bulletin, 8:311-315.

50.MOUNT, M.E. and B.F. FELDMAN. 1982. Vitamin K and its therapeutic importance. Journal of American Veterinary Medical Association, 180:1354-1356.

51.MOUNT, M.E. and B.F. FELDMAN. 1983. Mechanism of diphacinone rodenticide toxicosis in the dog and its therapeutic implications. American Journal of Veterinary Research, 44:2009-2017.

52.NATIONAL ANIMAL POISON CONTROL CENTER. 1985. Annual progress report, 1984. College of Veterinary Medicine, Urbana, Illinois.

53.PAPWORTH, D.S. 1958. A review of the dangers of warfarin poisoning to animals other than rodents. Royal Society of Health Journal, 78:52-60.

54.PLESTINA, R. 1984. Prevention, diagnosis and treatment of insecticide poisoning. WHO/VBC/84.889.

55.POCHE, R.M. Personal communication (Nov. 30, 1984). Director of Technical Services, Lipha Chemicals Inc.

56.RAMPAUD, M. 1981. Toxicologie des raticides. Conference Prononcee en Novembre 1981 au Collogue de Moulins (Allier) 53-59.

57.SMITH, C.R. 1984. Survey of rodenticide bait-related exposures reported by the Los Angeles Medical Association Regional Poison Information Center _ July 1, 1982, to June 30, 1983. EPA Public Hearings on Rodenticide Bait Stations, Sacramento, CA, March 5, 1984.

58.SPENCER, H. J. 1950. U.S.D.I. Report of Activities, Wildlife Research Laboratory, Denver, CO. 1st Quarter, 12.

59.HARLING, R., P. BUFORD, and S. FREYER. 1986. LM2219 (difethialone) oral toxicity study in beagle dogs (13 weeks). Huntindon Research Center, UK. Unpublished study.

60.LORGUE, G. 1986. Acute oral toxicity study of LM2219 (difethialone) in cats. Ectoxicology Laboratory (INRA-ENVL), National Veterinary School, Lyon, France. Unpublished study.

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