Field Evaluation of Coumatetralyl for the Control of Wild Boar, Sus scrofa cristatus

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PJZ_49_3_1143-1146

Field Evaluation of Coumatetralyl for the Control of Wild Boar, Sus scrofa cristatus

Abdul Aziz Khan1,*, Shahid Munir2 and Irfan Ahmed2

1Pakistan Agricultural Research Council, Islamabad, Pakistan

2Vertebrate Pest Management Programme, National Agricultural Research Centre, Park Road, Islamabad, Pakistan

ABSTRACT

We evaluated the field efficacy of coumatetralyl maize grain bait (0.0375%) against wild boar population in Fatima Jinnah Park, Islamabad. A total of 1838 kg bait was applied at 32 bait points, out of which 1627 kg was consumed by wild boars during 17 nights. The consumption of bait increased asymptotically and attained peak on the 7th night. The bait in-take, external and internal pathological symptoms were similar as has been described for warfarin and brodifacoum. The bleeding period ranged from 8.06 to 12.94 nights with 13% variation in time. Based upon the total consumption of coumatetralyl bait, 400-450 wild boars were estimated as killed during the operation. The results of the study showed that coumatetralyl is a promising and potential alternate to sodium flouroacetate compound (1080) for managing wild boar populations in diverse environments.

Article Information

Received 27 August 2015

Revised 15 December 2016

Accepted 20 December 2016

Available online 26 May 2017

Authors’ Contributions

AAK designed the study and finalized the manuscript. All authors equally contributed in field work.

Key words

Anticoagulant, Pathological symptoms, Wild pigs, Environmental pest.

DOI: http://dx.doi.org/10.17582/journal.pjz/2017.49.3.sc10

* Corresponding author: [email protected]

0030-9923/2017/0003-1143 $ 9.00/0

Wild boar (Sus scrofa cristatus) is widely distributed in majority of the agro-ecological zones of Pakistan and is a major vertebrate pest of crops i.e., maize, potatoes, sugarcane, groundnut, sunflower, canola, wheat, rice, and forest plantations, plant nurseries etc. (Taber, 1965; Inayatulla, 1973; Pavlov, 1980; Shafi and Khokhar, 1986; Brooks et al., 1989; Khan, 1991; Brooks and Ahmad, 1993; Roberts, 1997). Due to its digging and wallowing habits, water courses particularly in irrigated forest plantations are badly damaged and heavy expenditure is incurred in rebuilding them. In addition to this, they damage eggs and young ones of birds and wild animals. In USA, Australia and many European countries, feral pigs are considered as big game animals, and have important economic, social and cultural values (Tisdell, 1982). They are the most important vertebrate modifiers of ecosystems, causing losses of native plants, birds and invertebrates habitats, thus, enhancing conditions for alien plants and bird diseases, increasing erosion and altering nutrient cycles, by way of its digging and up-rooting habits. They are known to cause foot-and-mouth disease (FMD) to livestock in Australia by sharing common grazing grounds (Dunne, 1970). In addition to this, the wild boar is subject to many infectious diseases such as swine fever, trichinosis and vesicular stomatitis, and exchange infections with domestic pigs, domestic livestock and wild animals.

The distribution of wild boar in Pakistan is a part of its ancestral range (Heptner et al., 1966). They are most associated with Indus basin riverain tracts having thickest of Saccharum munja and S. spontaneous grasses (Beg and Khan, 1982). Also, they have adapted perfectly to man-made irrigated forest plantations of the Punjab and Sindh provinces. The spread of Arizona mesquite (Prosopis juliflora) in the irrigated plantations provided an excellent habitat, favouring tremendous increase in wild boar population. Roberts (1997) reported that wild boars are found at elevation up to 1000 m in the Margalla National Park and around Kahuta Tret in the Murree foot hills, and throughout the Punjab and Sindh, down to Indus delta (Smiet et al., 1979). In Khyber Pakhtunkhwa (KPK), they are found in many areas, west of Indus river and have been reported in the southern part of Chitral valley (Fulton, 1963). In Balochistan wild boar populations are confined to scrub vegetation in the vicinity of stream beds and the broader valleys of Kohlu and Nasirabad divisions. In recent years, its distribution has expanded to Muzaffarabad and Kohala areas of AJ&K (Siddique Awan, pers. comm.) Due to extension of irrigation system in Thal, wild boar is commonly sighted in the forest plantations and crop lands. Before 1950’s, wild boars were absent from the desert lands of Thal. Wild boars have been commonly sighted in Galliats of Murree Hills (Ejaz Ahmad, pers. comm.). It is expected that the wild boar population will increase within few years in Galliats and abundant prey will be available to leopards, resulting in the decrease of predation on livestock and attack on humans.

Various methods and techniques have been evaluated or being practiced in many countries for the control of wild boar (Anonymous, 1957; Inayatullah, 1973; Tisdell, 1982; Hone and Atkinson, 1983; Shafi and Khokhar, 1986; O’Brien, 1988; Brooks et al., 1988). Among these the chemical control is the most effective and economical mean that offers large-scale population reduction of wild boar. In Pakistan, various workers used highly toxic insecticides i.e., endrin, aldrin, aldicarb, follidol, metasystox, gusathion etc. for the control of wild boar in crop lands and forest plantations (Karim and Zakria, 1963; Inayatullah, 1973; Khan et al., 1980). Shafi and Khokhar (1986) used grain baits of sodium fluoroacetate (1080) in sugarcane fields and obtained 80-100% reduction in wild boar population. The strong taste and smell of the insecticidal compounds prevent their acceptance by the wild boar on the scale necessary to control large areas. Also, the baits commonly used in such cases are highly favoured by livestock and non-target wildlife species. Although widely used in Australia and New Zealand, the application of 1080 bait is extremely hazardous to livestock, wildlife and humans. Experienced and certified vertebrate pest control operators are recommended for its operational use. Bait-shyness, aversion and tolerance are some other associated problems which prevent the complete eradication of wild boars with the use of 1080 baits. Also, perfect antidote is not available in case of poisoning.

In search of potential alternate toxicants, warfarin, an anticoagulant, has been evaluated against wild pigs in Australia and U.S.A. with promising results (Hone and Stone, 1989; Choquenont et al., 1990). The literature suggests that pigs are very susceptible to anticoagulants. (Dobson, 1973; Saunders, 1988; O’ Brien et al., 1988; McIlroy et al., 1989) Therefore, this study was conducted to determine the effectiveness of an anticoagulant coumatetralyl (manufactured by Bayer, Germany) against wild boar which could supplement or replace the use of 1080 for wild boar control in the longer term. In properties, it is similar to warfarin. Coumatetralyl is a registered rodenticide for the control of rats and mice in agriculture and urban environments in Pakistan.

Materials and methods

The study was conducted in Fatima Jinnah Park, F-9 (formerly known as Capital Park), located in the Zone-1 as per Master Plan of the Islamabad territory. It is equivalent to one full sector area (307.3 ha), and was designed by the Japanese architectures in 1970. The park is surrounded on three sides by the residential sectors: F-8 to the east side, E-9 to the north and F-10 to the western boundary. Towards south lies the civic-business-commerce centre of the city known as Jinnah Avenue. It is nearly two kilometers away from the foot hills of Margalla National Park in the north. The topography of the park resembles the overall terrain of the capital city where the land is uneven (rolling) and there is a slope from north to south. The elevation of the park lies between 488-549 m from the sea level. The most predominant feature of the study site is the presence of two nullahs which join each other towards the south of the park. The banks of these nullahs are badly eroded. In the past, the land of this area was used for agriculture till the time it was acquired for urban development.

The land of the park was developed by clearing off thorn scrub vegetation. At the time of this study the vegetation cover of the park comprised of Dalbergia sissoo Roxb, Broussonetia papyrifera (L.) L. Hertit, Acacia modesta (L.) Wall, Pinus roxburghii Sargent, Morus alba L. etc. (trees), and Cynodon dactylon L., Cyperus rotundus L., Sorghum halepense (L.) Pers, Desmostachya bipinnata (L.) Stapf etc. (grasses). Banks of nullahs, having thickest of B. papyrifera and S. halepense provided hide-outs to wild boars, the migrants from the Margallah Hills. The observed wildlife consisted of common foxes and few partridges. The trees provided roosting sites to crows.

Coumatetralyl (Racumin) bait was prepared by mixing molasses with whole maize grain, and racumin master mix (0.75%) in the ratio of 1:18:1 by weight, to give a final concentration of 0.0375% coumatetralyl. Blue dye was incorporated by the manufacturer in the master mix to provide warning that the bait is not human food. Also, birds avoid eating such coloured stuff. Fresh bait was prepared daily and used the same in the late afternoon.

Before the baiting was initiated, the park was thoroughly surveyed for places where wild boar activity was evident i.e., wallows, rooting of grass tubers, tusk or mud marks on tree trunks, numerous foot prints, trails etc. All the active places were flagged with red coloured ribbon. Altogether 32 places were selected as bait points. The baiting was conducted in the late afternoon (1530-1830 h) and the bait consumption was checked in the morning. Starting with an initial placement of 2.5 to 3.5 kg per point and for the following nights the quantity of the bait placed was adjusted according to the previous night’s bait consumption. The baiting at all points continued for 17 nights. Daily records were kept of the bait placed and consumed over night at each bait point.

Results and discussion

During the 17 nights baiting, the observations recorded about the bait intake, external and internal pathological symptoms, indicated that coumatetralyl (0.0375%) maize grain bait was highly effective in reducing wild boar population in different areas of the park. Boars ingesting coumatetralyl showed similar pathological symptoms as described for warfarin and brodifacoum (O’Brien and Lukins, 1990). External evidence of anticoagulant toxicity consisted of bloody rectal or nasal discharge or frank blood in faecal matter. Autopsied animals showed extensive haemorrhages in stomach, small and large intestines. Weight bearing joints also showed bleeding symptoms. Bleeding and nasal discharge was observed at 28 bait points. First bleeding sign was recorded on the 7th day of baiting while it continued to be observed on different days up to 14th day, mean being, 10.5±2.44 nights. Thus, the bleeding period ranged from 8.06 to 12.94 nights with 13% variation in time. During the study it was, also, observed that wild boars having lethal doses of coumatetralyl showed markedly reduced movements and feeding prior to death. Although anticoagulants can pose both a primary and a secondary poisoning hazard to non-target species under certain circumstances, the authors did not record any such case in the present study because coumatetralyl has a much shorter serum half-life and is likely to show persistence (O’Brien and Lukins, 1990).

Thirty two bait points were established in various areas of the park where wild boar activity was evident. After first night’s baiting, bait intake was recorded from 29 bait points and later on all of them became active. Baiting was conducted for 17 nights. A total of 1838 kg bait was applied and out of this 1627 kg bait was consumed by the wild boars. During the 17 nights the maximum bait applied at one bait point was 99 kg while the minimum quantity was 21 kg, average being 56 kg. Similarly, the maximum bait consumed at one bait point was 88.2 kg while the minimum quantity was 19.2 kg, average being 51.8 kg. The consumption of bait increased asymptotically and attained peak on the 7th night and thereafter declined steadily (Fig. 1). The bait applied and consumed by the 17th night declined to 10.26 and 9.14% of the peak, respectively. The quantity of bait applied and consumed varied by 20.99 and 19.20%, respectively which means that the bait applied per night was sufficient for wild boars visiting each bait point. The bait consumption ranged from 1.6-6.52 kg per night with an average of 4.1 kg. The bait consumption data suggest that maize grain bait of coumatetralyl was highly accepted by the wild boars. Although, no comparison was made with any other kind of bait in this study, however, the results of other studies showed that the consumption of grain bait by wild boars was significantly higher than pellet baits (O’Brien et al., 1988). The observation documented revealed that bait type has broader implications for vertebrate pest control. Bait type can be an important determinant of a compound’s toxicity and may be a source of variation in response and also when the natural food is abundant in the operational area. The observations on the pattern of bait consumption showed that the natural food was not easily available to wild boars in the park area.

During this study 1627 kg coumatetralyl (0.0375%) bait was consumed by the wild boars which must have contained 610 g of active ingredient of the compound when it was formulated in the factory. Dobson (1973) conducted pen studies which indicated that coumatetralyl at dosages ranging from 0.1 to 1.0 mg/kg created haemorrhages in majority of pigs and died on the 8th day from consuming 0.25 to 1.0 mg/kg of coumatetralyl for 7 days. He concluded that a total intake of less than 2 mg/kg should be lethal provided this is ingested over a period of seven days. In this study the coumatetralyl master mix (0.75%) was imported in 1975 and may have lost its efficacy by 10-15%, and 1627 kg bait consumed may have contained 549-513g active ingredient. In this study, the first mortality was recorded on the 12 day and followed upto 17th night, which otherwise would have been observed on the 7 or 8 day (Dobson, 1973; O’Brien and Lukins, 1990). This late mortality indicated the loss of toxicity of the compound. The baiting was terminated on the 17th night. Thereafter, post-treatment bait in-take census was conducted for three nights. On the average, 30 bait points were not visited by the wild boars, indicating 93.75% reduction in wild boar activity in the park. Sixty two dead bodies of wild boar were found in different areas of the park. Based on the total consumption of bait, 400-450 wild boars were estimated as killed during this operation. Saunders (1988) and McIlory et al. (1989) evaluated warfarin as an agent for pig control and obtained 98.9 and 93.7% reduction in pig abundance. Similar results were obtained by Choquenont et al. (1990) with the usage of warfarin bait. The results of the present study and that of earlier preliminary trials (Brooks et al., 1988) suggest that coumatetralyl is a promising and potential alternate to 1080 for managing wild boar infestations in crops, forest plantations, rangelands, parks and protected areas.

Conclusions

The coumatetralyl, an anticoagulant, was highly effective in controlling wild boar population in the park, and that the maize grain as base bait material was palatable and consumed in a relishing way by the wild boars. Also, coumatetralyl proved to be a potential alternate toxicant and replacement to the use of 1080 for wild boar control as problems of bait-shyness, aversion, tolerance, hazards to live-stock, wildlife and humans are not associated with the use of baits formulated from this compound. In view of the findings of this study, for effective management of wild boar populations in crop lands, forest plantations, and protected areas, the use of anticoagulant baits such as coumatetralyl (0.0375%), warfarin (0.025%) and brodifacoum (0.005%) be preferred over the use of sodium flouroacetate (1080) baits for control of wild boar.

Acknowledgements

This publication is dedicated to late Mr. Shakeel Ahmad, our dear colleague and fellow scientist. The financial and labour inputs were provided by the Capital Development Authority (CDA), Islamabad.

Statement of conflict of interest

Authors have no conflict of interest in this study.

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