Learn about North America’s “Song Dog”



As the most persecuted native carnivore the Coyote represents all misunderstood & exploited predators. Find out more…


At least 19 subspecies of coyote roam North & Central America, occupying a broad range of habitats. Find out more…


Two hundred years of costly persecution has not eliminated the resilient coyote from our landscape. Find out more…


Adaptable to a wide range of environments, coyotes help to keep an ecosystem in balance. Find out more…


The coyote, our unique Song Dog who has existed in North America since the Pleistocene, is the most persecuted native carnivore in North America. The coyote is the flagship species for all misunderstood and exploited carnivores. Poisoned, trapped, aerial gunned and killed for bounties and in contests, an estimated half a million coyotes are slaughtered every year in the U.S. — one per minute.

Maligning stereotypes and fallacies follow the coyote wherever she goes. Unlike many predators who face extinction, coyotes continue to survive and thrive in the face of persecution. Their survival is attributed to their intelligence, adaptability, and resilience, traits many Native Americans revered in the coyote as the creator, trickster and ancestor.

A vital part of both our rural and urban landscapes, the coyote’s ability to adjust to changing conditions and diverse environments sets her apart and makes the coyote so difficult to pigeonhole, perhaps further contributing to people’s fear and misunderstanding.

In her intelligence and adaptability, the coyote teaches us about our own capacity to evolve and coexist in the face of rapid ecological and social change. By helping to shift attitudes toward coyotes and other native carnivores, we replace fear and ignorance with understanding and appreciation.

As the only organization whose mission is to foster coexistence between people and carnivores and compassionate conservation through education, science and advocacy, Project Coyote builds a critical bridge between wildlife conservation and animal welfare/protection, bringing the best science and ethics to our advocacy on behalf of coyotes and other native carnivores.

Feature photo: Coyote Howl by © Wally Nussbaumer. Round photo: Coyote by lacomj via Creative Commons










Compiled from information obtained from Wild Earth Guardians using USDA’s Wildlife Services data.

The above methods account for 95% of coyotes killed with the remaining 5% using other methods including hounds, calling, spotlighting and den eradication.

Above photos: Coyotes on fence by Wildlife photographer Steve Creek took this photo of dead coyotes tied to a fence last year in Oklahoma. They were “on display near a major 4-lane highway,” Creek says on his web site. Coyotes on an Alberta Barn (photographer unknown).

The United States Department of Agriculture’s Wildlife Services accounts for over 76,000 of the estimated 500,000 coyotes that are killed each year. As shown below, most are killed for sport or fun. Many states allow unlimited killing of coyotes including the following practices:

  • Bounties (starting at as little as $1 for each animal killed)
  • Poisoning (using Compound 1080 and Sodium Cyanide M-44s)
  • Aerial gunning (shooting animals from low-flying aircraft on private and public lands)
  • Leghold trapping (which are nonselective and often injury non-target species)
  • Snaring (a lethal wire intended to catch and strangle a coyote to death)
  • Calling & shooting (distress calls of wounded young or prey are used to lure coyotes in to point blank range where they are then shot)
  • Hound hunting (pursued by hounds and torn apart)
  • Killing contests, derbies or tournaments (where awards are given for those who kill the most and largest animals)
  • Denning (the killing of coyote pups in their dens)



The coyote represents a more primitive form of Canis than the gray wolf, as shown by its relatively small size and its comparatively narrow skull and jaws, which lack the grasping power necessary to hold the large prey wolves specialize in. It is not as specialized a carnivore as the wolf is, as shown by the larger chewing surfaces on the molars, reflecting the species’ relative dependence on vegetable matter. In these respects, the coyote resembles the fox-like progenitors of the genus more so than the wolf. (Nowak, 1978) The evolution of the coyote can be traced back to an extinct type of small omnivorous fox-like canid endemic to North America 10.3—3.6 million years ago. (Kurten, 1980)

Modern coyotes arose during the Middle Pleistocene, and showed much more variation than they do today. (Nowak, 1978) They were larger and more robust, likely in response to larger competitors and prey. (Meachen, J. A.; Samuels, J. X., 2012)

Their reduction in size occurred after an extinction event, when their large prey died. (Meachen, J. A.; Samuels, J. X., 2012) Furthermore, Pleistocene coyotes were unable to exploit the big game hunting niche left vacant after the extinction of the dire wolf, as it was rapidly filled by gray wolves, which likely actively killed off the large coyotes. (Meachen, J. A. et al, 2014)

Main photo of coyotes in different environments from left;
Canis latrans at Sunset, Marin Headlands by Matt Knoth via Creative Commons; Coyote by Dave Ballard Photo via Creative Commons and Coyote in the snow by David Schenfeld via Creative Commons. Above: Mearns coyote (Canis latrans mearnsi) is a subspecies of coyote native to extreme southwestern Colorado, Utah, Nevada, Arizona, and California. It is a small subspecies, with medium-sized ears, a small skull, and small teeth. The fur is richly and brightly colored. The fulvous tints are exceedingly bright, covering the hind and forelegs.
Photo: Coyote Dad by g’pa bill via Creative Commons and caption from Wikimedia Commons.


At least 19 subspecies of coyote roam North and Central America, from California to Newfoundland and Alaska to Panama, occupying a broad range of habitats. Coyotes play an important ecological role helping to maintain healthy ecosystems and species diversity. As the top carnivore in some ecosystems, coyotes provide a number of benefits including regulating the number of mesocarnivores (such as skunks, raccoons, and foxes) which in turn, helps to boost biodiversity.

The Mountain coyote (Canis latrans lestes), also known as the Great Basin coyote, is a subspecies of coyote native to British Columbia and southeastern Alberta south to Utah and Nevada. It is similar to C. l. latrans, but has lighter-colored upper parts. Photo and caption from Wikimedia Commons by Mariomassone

A map of the distribution of the 19 known subspecies of canis latrans plus Canis latrans “var”, the Eastern Coyote, a hybrid between the coyote and wolf. 

  1. Canis latrans cagottis
  2. Canis latrans clepticus
  3. Canis latrans dickeyi
  4. Canis latrans frustor
  5. Canis latrans goldmani
  6. Canis latrans hondurensis
  7. Canis latrans impavidus
  8. Canis latrans incolatus
  9. Canis latrans jamesi
  10. Canis latrans latrans
  11. Canis latrans lestes
  12. Canis latrans mearnsi
  13. Canis latrans microdon
  14. Canis latrans ochropus
  15. Canis latrans peninsulae
  16. Canis latrans texensis
  17. Canis latrans thamnos
  18. Canis latrans umpquensis
  19. Canis latrans vigilis
  20. Canis latrans “var”

Modified from: Hel-hama used under Creative Commons Attribution, Sharelike.


Coyotes may live as solitary individuals, in pairs, or in small family groups, both in rural and urban areas. Coyotes are generally monogamous, with pair bonds frequently lasting for many years, and some for life. Both male and female coyotes actively maintain territories that may vary in size from 2 to 30 square miles.

Reproduction is generally once per year and limited to the group’s leaders, while other females remain behaviorally sterile. Breeding season peaks in mid February, followed by 4-8 pups born in a den in April or May. Pup mortality is high, with an average of 50-70% dying within their first year. Some juveniles disperse in late fall to seek new territory, and some individuals remain with their parents and form the basis of the pack.

The graphic below produced by the Humane Society illustrates how predator management programs focused on killing coyotes disrupt the pack structure.

Images: Coyotes and coyotes hunting in tandem by Matt Knoth via Creative Commons.


Western coyotes typically weigh 18 to 30 pounds and look similar to a small Shepherd or collie-type dog but have longer, denser fur and pointed, erect ears. Coyotes have a long, bushy, black-tipped tail that is usually carried pointed down. Their eastern counterparts may be larger, averaging 35-55 pounds, which is believed to be a result of interbreeding with wolves 50-70 years ago. Coyotes are usually grayish brown with reddish tinges behind the ears and around the face, but coloration can vary from silver-gray to black.

Coyote by © Wally Nussbaumer


In rural habitats, coyotes hunt by day and night. In urban areas, coyotes appear to be more nocturnal but can often be seen during daylight hours, especially at dawn and dusk. They communicate by vocalizing, scent marking and through a variety of body displays.

It is common to hear them howling and yipping at night, or even during the day in response to sirens and other loud noises. Indeed, the coyote’s scientific name is Canis latrans which means “barking dog.” With approximately a dozen different vocalizations, it is common to mistake a few coyotes communicating with each other for a large group. Coyotes are fast and agile; they can run at speeds of 25-40 mph (65 km/h) and jump 6 feet. Coyotes are also highly intelligent and social animals; they learn quickly and are devoted parents.

Coyote Symphony recorded by Rocky Raybell in Colville Indian Reservation, Washington State, USA via Wiki Commons


Coyotes eat a wide variety of food, and like most animals, prefer food that is easiest to obtain. They are true omnivores, and will eat a wide variety of foods, including rodents, rabbits, insects, lizards, snakes, vegetables, and fruits. They will also take advantage of unsecured garbage and pet food left outdoors. As scavengers, they provide an ecological service by helping to keep our communities clean of carrion. In suburbia, coyotes have been known to take smaller pets if left unprotected. Animal guardians are advised to keep cats indoors, and dogs under control during the day and indoors at night.

Above photo: Coyote along the Firehole River with feathers in mouth by Neal Herbert for Yellowstone National Park.


When coyotes live close to human populations, conflicts — often driven by fears of predation on domestic animals — may arise, and most conflicts continue to result in de-facto killing of coyotes (Fox and Papouchis, 2005; Fox, 2006). However, despite decades of poisoning, trapping, and shooting, coyotes persist in North America today and conflicts with people continue. The fact is that two hundred years of costly persecution have not eliminated the resilient coyote, but raise significant animal welfare issues (Alexander, 2015).

Why is killing ineffective and ecologically disruptive? The coyote’s remarkable success appears to be closely related to human attempts to control the animal’s population. As with other carnivore species, coyote populations are naturally regulated by available food and habitat. Lethal control, however, can disrupt the group hierarchy, allowing more coyotes to reproduce, encouraging larger litter sizes because of decreased competition for food and habitat, and increasing pup survival rates (Crabtree and Sheldon 1999). It is also likely that lethal control favors the survival of the most resilient and genetically robust coyotes (Crabtree and Sheldon 1999). More critically, with the disruption of pack structure, training across generations of coyotes that promotes consumption of wild prey can be compromised and increase killing of livestock and pets (Crabtree and Sheldon, 1999; Mitchel et al, 2004).

Despite the ineffectiveness and destructiveness of lethal approaches, at least half a million coyotes are killed every year in the U.S — one per minute — by federal, state and local governments as well as private individuals (Fox and Papouchis 2005). Most of this killing is carried out in the name of “livestock protection” at the behest of agribusiness and private ranchers. U.S taxpayers subsidize this predator carnage at the cost of 100 million dollars annually. (Read more about the USDA’s Wildlife Services program here or download our factsheet here.)

Indiscriminate lethal control in the name of management persists, despite scientific evidence that this approach has significant negative ecological and welfare implications and is ultimately economically ineffective (Fox 2006).

Coyotes are also killed for their fur, for “sport,” for fun, for hate, and in “body-count” contests where prizes are awarded for killing the most coyotes. Most states set no limit on the number of coyotes who may be killed, nor do they regulate the killing methods. While killing coyotes en mass or relocating individual coyotes can reduce their population in the very short term, it is not recommended for clear and important reasons described above. Project Coyote implements a number of programs that demonstrate how to peacefully coexist with coyotes and other wildlife in both urban and rural communities. You can download additional information about coexisting with coyotes here, including tips for keeping pets and livestock safe.

Above photo: Coyote pups at a den site by © Kees Hollemans & © Iris van Noort in Yellowstone National Park.


Adaptable to diverse environments, coyotes provide the following ecological benefits:

Coyotes limit mesocarnivore populations and increase bird diversity and abundance (Crooks and Soule 1999). Mesocarnivores such as skunks, raccoons, and foxes as well as feral cats can have a destructive impact on bird populations by raiding nests, etc. While coyotes can coexist with these species, studies indicate that coyotes limit mesocarnivore populations largely through competitive exclusion, thereby having a positive impact on ground-nesting birds and songbird diversity and abundance.

Coyotes keep rodent and rabbit populations in check.
Rodents and lagomorphs (rabbits and hares) are important food items for coyotes, often making up more than half of the dry weight of prey items found in scats (Fedriani et al., 2001; Morey et al., 2007). This however varies regionally, seasonally, and by level of urbanization – all of which affect the availability of rodents and lagomorphs as prey items. Laundré and Hernandez (2003) estimated 162 – 192 lagomorphs or 3110 – 3681 rodents per year are needed to fulfill metabolic needs (more if breeding/lactation was accounted for) for coyotes in the Great Basin Desert – and that therefore lagomorphs were a better energy return on hunting investment.

Thus, coyotes provide benefits to both urban and rural communities by keeping rodent and lagomorph populations in check. City dwellers enjoy cleaner environments (and avoid having to use rat poisons that can impact non-target animals). Ranchers benefit from coyotes controlling micro-herbivores (such as rabbits and gophers) that otherwise compete with their grazing animals for food. Farmers also suffer less crop loss or damage when coyotes naturally control rodent populations.

Coyotes help control disease transmission. Coyotes provide an invaluable public health service by helping to control rodents, thus reducing the spread of rodent-born zoonotic diseases such as plague and hantavirus (Watts et al, 2014).

Coyotes clean up the environment. As scavengers, coyotes provide an ecological service by helping to keep our communities clean of carrion (dead things).

Main photo: Coyote catches a rodent by © Linda L Delano. Above photo: Coyote visits a backyard by © Peggy Faranda.

Learn more about coyotes by visiting our multimedia and resources section.


Urban and rural residential landscapes offer an abundance of food, water, and shelter for coyotes. Take the following steps to prevent coyotes from being attracted to your home.

• Wildlife-proof garbage in sturdy containers with tight fitting lids.
• Don’t leave pet food outside.
• Take out trash the morning pick up is scheduled.
• Keep compost in secure containers.
• Keep fallen fruit off the ground. Coyotes eat fruit.
• Keep birdseed off the ground; seeds attract rodents which then attract coyotes. Remove feeders if coyotes are seen in your yard.
• Keep barbecue grills clean.
• Eliminate accessible water sources.
• Clear away brush and dense weeds near buildings.
• Close off crawl spaces under decks and around buildings where coyotes may den.
• If you frequently see a coyote in your yard, make loud noises with pots, pans, or air horns, and haze the coyote with a water hose.
• Share this list with your neighbors; coexistence is a neighborhood effort.

Discover how to coexist with coyotes here.

Above photo: Llama works to protect its flock by © Camilla H Fox.


Alexander, S.M. 2015. “Carnivore conflict, management, and conservation GIS in Canada.” In B. Mitchell, ed., Resources and Environmental Management in Canada. Ontario: Oxford University Press, 293-317.

Alexander, S.M. and M.S. Quinn. 2011.” Coyote (Canis latrans) interactions with humans and pets reported in the Canadian print media (1995–2010).” Human Dimensions of Wildlife 16:345-359.

Atkinson, K.T., and D.M. Shackleton. 1991. Coyote, Canis latrans, ecology in a rural-urban environment. Canadian Field-Naturalist 105:49-54.

Berger, K. (2006) Carnivore-livestock conflicts: Effects of subsidized predator control and economic correlates on the sheep industry. Conservation Biology, 20(3), 751 – 761.

Allen, JJ, M. Bekoff, and RL Crabtree. 1999. An observational study of coyote (Canis latrans) scent-marking and territoriality in Yellowstone National Park. Ethology 105:289-302.

Bekoff, Marc. 1978. Coyotes: Biology, Behavior, and Management. Academic Press, Inc., New York, New York.

Bekoff, Marc. 1995. Coyotes: Victims of their own Success. Canid News 3:1-6.

Bekoff, M., and Wells, M.C. 1986. Social ecology and behavior of coyotes. Adv. Study Behav. 16: 251–338.

Crabtree, RL, and JW Sheldon. 1999. The Ecological Role of Coyotes on Yellowstone’s Northern Range. Yellowstone Science 7(2):15-23.

Crooks KR, Soulé ME. 1999. Mesopredator release and avifaunal extinctions in a fragmented system. Nature 400: 563–566.

Fedriani, J. M., Fuller, T. K., Sauvajot, R. M. 2001. “Does Anthropogenic Food Enhance Densities of Omnivorous Mammals? An Example with Coyotes in Southern California”. Ecography. 24(3): 325-331.

Fox, C. H. 2006. Coyotes and humans: can we coexist? Pp. 287-293 in: R.M. Timm and J. H. O’Brien (eds.), Proceedings, 22nd Vertebrate Pest Conference. Publ. Univ. Calif.-Davis.

Fox, C.H. and C.M. Papouchis. 2005. Coyotes in Our Midst: Coexisting with an Adaptable and Resilient Carnivore. Animal Protection Institute, Sacramento, California.

Gese, E. M., Rongstad, O. J., Mytton, W. R. 1988. “Home Range and Habitat Use of Coyotes in Southeastern Colorado”. Journal of Wildlife Management. 52(4): 640-646.

Gehrt, S.D. and Riley, S.P.D. 2010. Coyotes (Canis latrans). In: Urban Carnivores (Gehrt, S.D., Riley, S.P.D., Cypher, B.L., eds.). John Hopkins University Press. pp. 78-95.

Gibeau, M.L. 1998. Use of urban habitats by coyotes in the vicinity of Banff Alberta.
Urban Ecosystems 2:129-139.

Kurtén, Björn.1980. Pleistocene Mammals of North America. pp. 167–9. Columbia University Press. ISBN 0231037333.

Laundré, J.W., Hernandez, L. 2003. “Total energy budget and prey requirements of free-ranging coyotes in the Great Basin desert of the western United States”. Journal of Arid Environments. 55(4): 675 – 689

Lukasik, V.M. and S.M. Alexander. 2012. “Spatial and temporal variation of coyote (Canis latrans) diet in Calgary, Alberta.” Cities and the Environment (CATE). Special Topic Issue: Urban Predators 4(11): Article 8. Retrieved from http://digitalcommons.lmu.edu/cate/vol4/iss1/8/

Meachen, J. A.; Samuels, J. X. (2012). “Evolution in coyotes (Canis latrans) in response to the megafaunal extinctions”. Proceedings of the National Academy of Sciences 109 (11): 4191. doi:10.1073/pnas.1113788109. PMID 22371581.

Mitchell, B. R., Jaeger, M. M., Barrett, R. H., 2004. “Coyote Depredation Management: Current Methods and Research Needs”. Wildlife Society Bulletin. 32(4): 1209-1218.

Monzon, J., Kays, R., Dykhuizen, D. E. 2014. “Assessment of Coyote-Wolf-Dog Admixture Using Ancestry-Informative Diagnostic SNPs”. Molecular Ecology. 23: 182-197.

Morey, P. S., Gese, E. M., Gehrt, S. 2007. “Spatial and Temporal Variation in the Diet of Coyotes in the Chicago Metropolitan Area”. The American Midland Naturalist. 158(1): 147-161.

Nowak, R. M. (1978) “Evolution and taxonomy of coyotes and related Canis”, pp. 3–16 in M. Bekoff (ed.) Coyotes: Biology, Behavior, and Management. Academic Press, New York.

Patterson, B. R., Messier, F. 2001. “Social Organization and Space use of Coyotes in Eastern Canada Relative to Prey Distribution and Abundance”. Journal of Mammalogy. 82(2): 463-477.

Pryah, D. 1984. “Social Distribution and Population Estimates of Coyotes in North-Central Montana”. The Journal of Wildlife Management. 48(3): 679-690

Riley, S.P.D., R.M. Sauvajot, T.K. Fuller, E.C. York, D.E. Kamradt, C. Bromley, and R.K. Wayne. 2003. Effects of urbanization and habitat fragmentation on bobcats and coyotes in southern California. Conservation Biology 17:566-576.

Tigas, L.A., D.H. Van Vuren, and R.M. Sauvajot. 2002. Behavioral responses of bobcats and coyotes to habitat fragmentation and corridors in an urban environment. Biological Conservation 108:299-306.

Wang, X., R.H. Tedford, and M. Anton. 2010. Dogs: Their Fossil Relatives and Evolutionary History. Columbia University Press. 219pp.

Watts, A., V.M. Lukasik, S.M. Alexander, and M.J. Fortin. 2015. “Urbanization, grassland, and diet influence coyote (Canis latrans) parasitism structure.” EcoHealth DOI: 10.1007/s10393-015-1040-5

Way, J.G. 2003. Description and possible reasons for an abnormally large group size of adult eastern coyotes observed during summer. Northeastern Naturalist 10(3): 335-342.

Way, J.G. 2007. Social and Play Behavior in a Wild Eastern Coyote (Canis latrans var.) pack. Canadian Field-Naturalist 121(4): 397-401.

Way, J.G. 2013. Taxonomic Implications of Morphological and Genetic Differences in Northeastern Coyotes (Coywolves) (Canis latrans × C. lycaon), Western Coyotes (C. latrans), and Eastern Wolves (C. lycaon or C. lupus lycaon). Canadian Field-Naturalist 127(1): 1–16.

Way, J.G. and Lynn, W.S. 2016. Northeastern coyote/coywolf taxonomy and admixture: A meta-analysis. Canid Biology & Conservation 19(1): 1-8. Retrieved from http://www.canids.org/CBC/19/northeastern_coyote_taxonomy.pdf.

Written by Project Coyote


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