Increasing Prevalence of Canine Heartworm in Coyotes from California

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Increasing Prevalence of Canine Heartworm in Coyotes from California Author: Benjamin N. Sacks Source: Journal of Wildlife Diseases, 34(2) : 386389 Published By: Wildlife Disease Association URL: https://doi.org/10.7589/0090355834.2.386 BioOne Complete (complete.bioone.org) is a fulltext database of 200 subscribed and openaccess titles in the biological, ecological, and environmental sciences published by nonprofit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Complete website, and all posted and associated content indicates your acceptance of BioOne s Terms of Use, available at www.bioone.org/termsofuse. Usage of BioOne Complete content is strictly limited to personal, educational, and noncommercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research.

JIimirmIaI IIf %% ihulifr :3.02). 1995. pp. 356:359 \iki1ife 1)iseast Asizx.aliomm 1995 Increasing Prevalence of Canine Heartworm in Coyotes from California Benjamin N. Sacks, Department of Environmental Science, Policy, and Management, 151 Hilgard Hall, University of California, Berkeley, California 94720, USA. ABsTRA(:T: Thirtyseven subadult and adult coyotes (Canis latrans), collected August 1992 through December 1996 from a coastal foothill area in northern California (USA), were cxamined for adult heartworm (Dirofilaria irnmitis). During 1992 through 1993, at the end of a 6 yr drought, none of four coyotes exammed were infected with heartworms. However, during 1994 through 1996, after the drought had ended, prevalences were 91% in 23 adult coyotes and 40% in 10 subadult coyotes. Heartworm intensity did not differ by sex of coyote, and averaged (±SE) 19.4 ± 3.8 among adults; one subadult had >238 heartworms. The preyalence and intensity of heartworrn infection in coyotes reported here for 1994 through 1996 are the highest reported anywhere in the United States. Key words: Canis latrans, coyote, Dirofilana immitis, heartworm, survey. The range of canine heartworm (Dirofilaria immitis) in dogs in the United States has been expanding outward from its core in the mesic southeast for several decades (Otto, 1972). Canine heartworm is a filarial nematode with a 6 mo life cycle that requires both mosquito and canid hosts (Courtney, 1989). Earlier studies in the plains states suggested that heartworm infection was rare in coyotes relative to dogs, making the coyote an unlikely reservoir (Gier, 1968; Franson et at., 1976; Graham, 1975). However, later studies in the southeastern United States (Crowd et at., 1978; Custer and Pence, 1981) and California (Weinmann and Garcia, 1980; Acevedo and Theis, 1982) found prevalences of heartworm in coyotes to be at least as high as in dogs, indicating that coyotes constituted an important reservoir for heartworm in those areas. Heartworm infection was not commonly found in dogs (or presumably coyotes) in northern California until the 1970 s, when the prevalence reportedly increased substantially (Weinmann and Garcia, 1980). Since then, the rate of infection has varied; heartworm prevalence in dogs declined steadily throughout a drought beginning in the late 1980 s (Theis et at., 1996). Infection rate also has varied geographically; the SierraNevada foothills showed a significantly higher prevalence of heartworm in both coyotes (Acevedo and Theis, 1982) and dogs (Theis et at., 1996) than other regions of the state such as the coastal foothills. The western treehole mosquito (Aedes sierrensis), which is thought to be the primary vector for heartworm in northern California, is abundant in both the SierraNevada and coastal foothills (Weinmann and Garcia, 1974). It is possible that heartworm had not become fully established in the coastal foothills when the aforementioned studies were conducted. As part of a larger investigation of coyote behavioral ecology and predation of sheep (Sacks, 1996), I surveyed for adult heartworms in coyotes collected from a coastal foothill site over a 4.5 yr period (199296) beginning at the end of a 6 yr drought. This study was conducted at the University of California s Hopland Research and Extension Center (HREC) (39#{176}00 N, 123#{176}05 W). The HREC encompasses 2,168 ha of northcoastal mountains and is situated approximately 65 km inland in the Russian River drainage, with elevations ranging from 150 m to 900 m. Oak (Quercus spp.) woodland, annual grassland, mixed evergreendeciduous forest, and chaparral vegetation types dominate the landscape; Murphy and Heady (1983) provide a detailed description of plant communities at HREC. The climate is characterized by hot, dry summers and mild, wet winters. Average annual precipitation is about 100 cm and falls mosfly as rain, 386

SHORT COMMUNICATIONS 387 between November and February (Murphy and Heady, 1983). Average temperature is 21 C in summer and 7 C in winter, with summer temperatures frequently reaching over 38 C (Murphy and Heady, 1983). Coyotes removed from H REC and vicinity (10 km) by specialists (United States Department of Agriculture/Animal Plant Health Inspection Service/Animal Damage Control, Fort Collins, Colorado, USA) or shepherds August 1992 through December 1996 (ii 34) were examined, in addition to three coyotes that died of natural causes including one each due to predation by a mountain lion (Felis concolor) and another coyote, and one of an unknown cause. No carcasses were collected 13 March 1993 to 13 August 1994. Ages of coyotes were determined by counting the cementum annuli of sectioned lower canines (Matson Laboratory, Milltown, Montana, USA). Coyotes at HREC are usually whelped between mid March and midapril (Sacks, 1996); to estimate ages, all coyotes were assumed to be whelped on 1 April. Six to 12moold coyotes were considered subadults and coyotes 12moold were considered adults. The occurrence of adult heartxvorm in coyotes was determined primarily by inspection of the internal surfaces of the right ventricle and pulmonary artery; remaiming chambers of the heart and associated blood vessels were also examined. Fisher exact tests (Zar, 1984) were used to detect differences in heartworm prevalence in adult coyotes between 199293 (August through March) and 199495 (August through July), and between 199495 and 199596 (August through December). Significance was set at P 0.05 for analyses. Heartworms were counted in infected coyote hearts. Heartworms were fixed in a solution of 20 parts 70% ethyl alcohol and one part glycerin at 62 C, and stored in the same solution (Orihel, 1961). Because coyotes were sometimes found several days after death, some heartworms were TABLE 1. Prevalence amid intemisitv of imifection by admult Dirofiluria iininitis imi 37 cootes fromui liopland Research and Extension Center and viciuiity ( 10 kmii), California, Amugmust 1992 throimgh 1)ecember 1996. Peroxi Age 199293 smubadimlt 199495 199596 aclimlt sul)adlmlt a(hmmlt siubadumlt adrult Prevalemice T (mu1 ) 0 (1) 0 (3) :38 (8) 90 (10) 50 (2) 92 (13).1 SIul)L(I(mlts are < 1 \TOld ami(i a(iluits are I rold. 1, Nomniber of LO\)t( S exammmimutri. Imutt musit (5 SE mmsummmher/ jmub ctiomu) 21.4 ± 6.l >238 s 18 ± 49t I. Five hearts s ere imua(lvertemutlv (liscar(ie(i after determmmimuimug presemi(e/(ti)st mlct. Ixforv mu(.mmiat(xles (()mul(l Ix (Ommmite(l; these imiciuded all three imufecte(i hearts fromum tin 199495 stmlatdsult samumple amid umue imofecterl Iueart frommi each of tlue 199495 amal 199.596 a(imultsamolple s.time remmmaimuimug21.)1mmfected Imeamts were rmserl to (Ivte rrmumue imotemmsit of imufectiomu. II Omulv Imeartwormims mmg(xxi comu(iitiomo (mm 238) svr (omumit( (l mu tluisi)i 1ctml1rIueart; laosed omi tlur volummit md tumuidemitifiai)ie fragmmmemuts. time total mumummml)ersvas I)rIiIIIY closer tmm 3(K). partly decomposed. In such cases, it was not always possible to determine exactly the numbers present and intensity was estimated as follows: the ratio of the volume of unidentifiable nematode tissue to countable (intact or piecedtogether) individuals from the same heart was multiplied by, and the product added to, the number of countable nematodes; most of the heartworms were countable (1 ± SD = 84 ± 13% of the total number estimated). Intensity was compared between years and between coyote sexes using MannWhitney Utests (Zar, 1984). Voucher specimens were deposited in the U.S. National Parasite Collection (Animal Parasitology Institute, Beltsville, Maryland, USA; accession number 87091). Hearts of 37 adult and subadult coyotes were examined (Table 1). Prevalence of heartxvorm infection in 199495 (90%) was significantly higher (P < 0.01) than in 199293 (0%) in adult coyotes, although the sample size in 199293 was small (n = 3). There was no difference (P > 0.5) between the adult infection rate in 199495

388 JOURNAL OF WILDLIFE DISEASES, VOL. 34, NO. 2, APRIL 1998 and 199596 (92%). Sample sizes of subadult coyotes were too small in 199293 and 199596 for betweenyear comparisons of heartworm prevalence; in 199495, prevalence in subadults was 38%. Heartworm intensity did not differ between 199495 and 199596 (P > 0.50) in adult coyotes, nor was there a difference in the number of heartworms found in male versus female coyotes of all ages, in both years combined (P > 0.10). The higher prevalence of heartworm in adult coyotes from HREC since 1994 may have been related to a drought that ended in 1993 (1 ± SE annual rainfall 198792 = 65.6 ± 2.3 cm, 198386 91.9 ± 28.7 cm, and 199396 74.5 ± 26.7 cm) and its influence on vector populations. The sample size from 199293 (n 3 adults) was sufficiently small to warrant caution; nevertheless, heartworm prevalence in northern California domestic dogs was relatively low during the same drought (Theis et at., 1996), supporting the trend found in this study. Western treehole mosquito (vector) density varies with rainfall (Hawley, 1985); therefore, it is likely to be a primary limiting factor in prevalence of heartworm. In contrast, density of coyotes (host) probably does not vary substantially as a function of rainfall in northcoastal California (Sacks, 1996) and density of dogs almost certainly does not. Heartworm abundance in coyotes tends to increase with age (Custer and Pence, 1981; Holzman et al., 1992; this study). However, the coyote with the most heathvorms in this study (n > 238) was a subadult, indicating either that heartworm infection can occur very frequently in some circumstances or that some mosquitoes harbor and inject large numbers of larvae. Earlier reports of canine heartxvorm in coyotes from California showed the Sierra Nevada foothills as having the highest prevalence among five regions of northern California, which included the coastal foothills, where the present study was conducted (Weinmann and Garcia, 1980; Acevedo and Theis, 1982). A more recent (19831988) survey of domestic dogs (Theis et at., 1996) supported this pattern: prevalence was nearly eight times greater in the SierraNevada foothills (9%) than in the coastal foothills (1%). However, preyatence of heartworm in adult coyotes in the SierraNevada foothills was only 45% in the late 1970 s (Weinmann and Garcia, 1980), as compared to 92% in the coastal foothills during the present study. Even in the southeastern United States, where heartworm prevalence has historically been highest in domestic dogs (Otto, 1972), prevalence in coyotes at approximately 70% (Crowd! et at., 1978; Custer and Pence, 1981 ) was lower than currently at HREC. Heartworm intensity in coyotes also was higher at HREC (total ± SE = 30.4 ± 11.8, not including one individual with unusually high intensity 19.4 ± 3.8) than previously reported in northern California (1 = 9 and 16 for female and male coyotes, respectively) by Weinmann and Garcia (1980) or in Texas and Louisiana (1 13.6) by Custer and Pence (1981). The intensity of >238 heartworms found in one coyote at HREC was far greater than in any other coyote in this study or any other reported; maximum numbers of worms were 12, 23, 58, 82, and 84 in the studies of Graham (1975), Franson et at. (1976), Crowell et at. (1977), Weinmann and Garcia (1980), and Custer and Pence (1981), respectively. Although heartworm intensity reported in this survey was not exact, estimates appeared to be good approximations. It is likely that nearly all mate heartworms were identified because their posterior ends are easily recognized even after considerable decomposition; these counted males comprised 42% (B. N. Sacks, unpubl. data) of the total number of heartworms estimated, which is similar to the proportion of mates reported at 47% by Weinmann and Garcia (1980) and at 45% by Custer and Pence (1981). I thank K. Blejwas for supplying hearts from coyotes killed in 1996, G. Johnson for providing most specimens, and D. Sacks

SHORT COMMUNICATIONS 389 for lending surgical expertise. C. Vaughn provided lab space and chemicals. Comments from J. Neale and two anonymous reviewers greatly improved this manuscript. J. Poor, J. Meissler, T. Weller, J. Dayton, K. Ryan, C. Meinke, A. Chavez, M. Jaeger, and D. McCullough assisted in various ways. The United States Department of Agriculture/AnimalPlant Health Inspection Service/National Wildlife Research Center provided most of the necessary funding. Additional funding was provided by the Graduate Student Fund of the Department of Environmental Science, Policy, and Management at the University of California at Berkeley. Personnel of the University of California Hopland Research and Extension Center generously provided use of their facilities. LITERATURE CITED AcEvEDO, R. A., AND J. H. THEIS. 1982. Prevalemice of heart mr orm (Dirofilaria imn;niti.s Leidy) in coyotes from five northern California corunties. American Jorurnal of Tropical Medicine and Hygiene 31: 968972. COURTNEY, C. H. 1989. Transmission and hifecycle of the heartworm. In Proceedings of the California heartworm symposium, M. Kittleson (ed). California Veterinarian. Special Edition. California Veterinary Medical Association, Sacramento, California, pp. 8. CROWELL, W A., T. R. KLEI, D. I. HALL, N. K. SMITH, AND J. D. NEWSOME. 1978. Occurremice of Dirofilaria immitis and associated pathology iui coyotes and foxes froun Louisiana. In Proceedings of the heartworm symposium, 1977, C. F. Otto (ed). Veterinary Medicine Publishing Cornpany, Bonner Springs, Kansas, pp. 1013. CUSTER, J. \V, AND D. B. PENcE. 1981. 1)irofilariasis in wild canids from the gulfcoastal prairies of Texas and Louisiana, USA. Veterinary Parasitology 8: 7182. FRANSON, J. C., R. D. JORGENSON, AND E. K. BoG GESS. 1976. Dirofilariasis in Iowa coyotes. Journal of Wildlife Diseases 12: 165166. (;IER, H. T. 1968. Coyotes in Kamisas. Kauisas State College Agrictultiural Experiment Statiomi, Biulletin 393, Mamihattami, Kansas, 1 18 pp. GRAHAM, J. M. 1975. Filariasis in coyotes from Kansas amid Colorado. The Jotunial of Parasitologv 61: 5 135 16. HALEY, \V A. 1985. Populatiomu dvnamiuics of Aedes.sierrensi.s. in Ecology of mnosqtuitoes: Procee(1 ings of a workshop. L. P. Lomumiibos, J. H. Rev, amirl J. 11. Frauik (eds.). Florida Niedical Emitounologv Laboratory. Vero Beach, Florida. pp. 167184. H0LzNIAN, S., M. J. C0NR0Y, NI) \V R. 1)AvIDsoN. 1992. Diseases, parasites, amid siurvi al of coyotes in somuthcentral Ceorgia. Jomurnal of\vildhife Diseases 28: 572580. MURPhY, A. H., ANI) H. F. HEsoy. 1983. Vasciular plauits of the Ilopland Field Station. Niendocimio Cotumity, California. \\ asnuamin Journal of Biology 41: 5396. ORILIEL, T. C. 1961. Morphology ofthe lanai stages of I)irofi/aria iinmnitis in the dog. The Jomuruial of Parisitologv 47: 251262. OTTO, C. F. 1972. Epizootiologv of canine heartworm disease. In Canine heartworni disease: tile current kulowledge, proceedings of the secouid Umliversity of Florida svuuiposiumii omi camlimle hiearts orm disease, R. E. Bradley and C. Pacheco (eds.). University of Florida, Caiuiesville, Florida, pp. 116. SACKS, B. N. 1996. Ecology and behavuor of coyotes on a California shleep rauich imi relatiomi to depredation and comltrol. MS. Thesis, Umiiversity of California, Berkeley, Cahiforuiia, 223 pp. TIIEIS, J. H., C. CALISTA, H. COLE, B. CuUz, I). MURRAY, ANI) B. Scorr. 1996. Ileartworm imu nonendemic areas, part 2. Camiine Practice 21: 6 11. WEINMANN, (. J., AND E. GARCIA. 1974. Cauiiuie heartwormn in California. with observations on Aedes sierrensis as a potential vector. California Vector Views 21: 4550. AND. 1980. Coyotes and cauiine hieartsvormii iui California. Jomurnal of \Vildlife l)iseases 16: 217221. ZAR, J. H. 1984. Biostatistical amialvsis. 2nd Edition. Preultice Hall, Inc., Englewood Cliffs. New Jersey. 718 pp. Received fi)r publication 14 Iarc/z 1997.