Description of Residence for the Eastern Yellow-Bellied Racer (Coluber Constrictor Flaviventris) in Canada
Section 33 of the Species at Risk Act (SARA) prohibits damaging or destroying the residence of a listed threatened, endangered, or extirpated species. SARA defines residence as: "a dwelling-place, such as a den, nest or other similar area or place, that is occupied or habitually occupied by one or more individuals during all or part of their life cycles, including breeding, rearing, staging, wintering, feeding or hibernating" [s.2(1)].
The prohibition comes into effect in different ways depending on the jurisdiction responsible for the species. Because the Eastern Yellow-bellied Racer is not protected under pre-existing federal jurisdiction such as the Migratory Birds Convention Act or the Fisheries Act, the residence prohibition is only automatically in effect on federal lands on which the species occurs. SARA also contains a provision to prohibit the damage or destruction of species' residences on non-federal lands (provincial, territorial, and private lands) by way of an Order by the Governor in Council (GIC), if the Minister of Environment recommends it necessary to do so [s.34(2), 35(2)]. Unless such an Order is made, responsibility for protecting this species' residences remains with provinces and territories in which the species occurs.
The following is a description of residence for the Eastern Yellow-bellied Racer (Coluber constrictor flaviventris), created for the purposes of increasing public awareness and aiding enforcement of the above prohibition.
Eastern Yellow-bellied Racers are known to have two types of residence- over-wintering sites (called hibernacula) and egg-laying sites (called nests).
* COSEWIC: Committee on the Status of Endangered Wildlife in Canada
Distribution and Population
The distribution of the Eastern Yellow-bellied Racer is widespread across North and Central America, from Maine to southern British Columbia, south to the Florida Keys and northern Guatemala1. Eastern Yellow-bellied Racers are common in the northern states including Montana, North Dakota, and Iowa south to Texas and Louisiana.
The Eastern Yellow-bellied Racer reaches the northern edge of its range in Canada and the Canadian population represents a very small proportion of the global abundance of this species (Figure 1). In Canada, Eastern Yellow-bellied Racer populations are confined to areas of extreme southcentral Saskatchewan in proximity to Grasslands National Park and the Agriculture and Agri-Food Canada Val Marie Community Pasture 1-3. In addition, there have been one probable and four confirmed Eastern Yellow-bellied Racer sightings in extreme southeastern Alberta near Onefour, and two confirmed sightings near the Big Muddy River Valley in Saskatchewan 4-8. No empirical population estimates exist for Eastern Yellow-bellied Racers in Canada.
Physical Appearance and Context
Suitable hibernacula for Eastern Yellow-bellied Racers occur within stable slump zones, mammal burrows, rock crevices or ledges, deep holes in soft hillside soil, and abandoned cisterns 9-12, within mixed-grass prairie and sagebrush thicket areas1 (Figures 2, 3 and 4). Previous research indicates a preference for south facing slopes1; however, recent observations suggest that there may be more variation in directionality, although north facing slopes seem to be avoided. Although hibernacula have not been characterized for Eastern Yellow-bellied Racers, they have been characterized for Western Yellow-bellied Racers (Coluber constrictor mormon) in British Columbia13. Considering the similarities between the two subspecies, information on the attributes of suitable hibernacula for Western Yellow-bellied Racers is likely applicable to Eastern Yellow-bellied Racers as well. These attributes include: fracturing (maintains constant temperature and prevents freezing), humidity (prevents snake desiccation during hibernation), thermal momentum (the hibernaculum's capacity to absorb and retain heat), and cover (defined as rocks, boulders, grass, forbs or brush that aids in thermoregulation during emergence) 13. 'Cover' areas immediately adjacent to the entrance of the hibernacula are considered part of the residence.
Hibernacula provide refuge from extreme cold during winter. The function of hibernacula during spring emergence from, and fall return to, hibernacula is regulation of body temperature.
Figure 1. This map identifies the currently known range of the Eastern Yellow-bellied Racer in Alberta and Saskatchewan, Canada, based on data obtained from the Alberta and Saskatchewan Conservation Data Centres in 2009. The map also identifies potential range for the species in northern Montana, United States, based on data obtained from the Montana Natural Heritage Program in 2009.
In Canada, Eastern Yellow-bellied Racers are primarily confined to areas of extreme south central Saskatchewan in proximity to Grasslands National Park and the Agriculture and Agri-Food Canada Val Marie Community Pasture along the Frenchmen River Valley. Sightings of individuals outside of extreme south central Saskatchewan are limited, but there have been one probable and four confirmed Eastern Yellow-bellied Racer sightings in extreme southeastern Alberta near Onefour and Lost River and two confirmed sightings near the Big Muddy River Valley in Saskatchewan. The Canadian and US range information suggests that that there is some connectivity among Canadian and US populations, but this has not been confirmed.
Figure 2. This map presents the locations of known current (evidence of use by individual Eastern Yellow-belled Racers during spring 2008 and 2009 emergence), historic (no evidence of current use by the species, but evidence of historic use in 1987 or 1993) and unused (no evidence of current or historic use by the species, but potentially appropriate) hibernacula in Canada.
All records occur in Saskatchewan. There are seven current hibernacula: two in the Agriculture and Agri-Food Canada Val Marie Community Pasture and five in Grasslands National Park. There are nine historic hibernacula: five in Grasslands National Park, three on privately-managed land and one on provincial lands. There are six unused hibernacula: three in Grasslands National Park, two on privately-managed land and one on provincial lands.
In accordance with section 124 of the Species at Risk Act (2002), and upon the advice of the Committee on the Status of Endangered Wildlife in Canada (J. Hutchings, pers. comm. 2010), the precise locations of hibernacula are not provided to protect them from potential human disturbance.
Figure 3. This photo shows three hibernacula entrances used by Eastern Yellow-bellied Racers in Grasslands National Park (arrows point to entrances).
Figure 4. This photos shows a close-up of hibernacula entrance used by Eastern Yellow-bellied Racers in Grasslands National Park. Rattlesnake (Crotalus viridis) visible to left of entrance.
Damage and Destruction of Residence
Examples of activities that are likely to result in the damage or destruction of hibernacula include, but are not limited to, the following:
|Activity likely to damage or destroy hibernacula||Potential effect of the activity on hibernacula|
If damage or destruction to a hibernaculum occurs when it is occupied by an individual of the species, the SARA prohibition again the killing, harming and harassment of individuals [s.32(1)] may be applicable in place of, or in addition to, the prohibition against the damage or destruction of a species' residence [s.33].
Period and Frequency of Occupancy
Hibernacula are permanently occupied by multiple individuals from September/October to May/June. Eastern Yellow-bellied Racers live for at least 7-8 years10, and the species exhibits hibernacula site fidelity, often using the same hibernaculum over multiple, consecutive years 15. Most of these hibernacula are also occupied by other species of snakes 16.
Any place used as a hibernaculum by Eastern Yellow-bellied Racers is considered a residence year-round. Considering the life span of the species and evidence of re-use of hibernacula over multiple, consecutive years, locations identified as Eastern Yellow-bellied Racer hibernacula are considered residences until they are known not to have been used by Eastern Yellow-bellied Racers for eight consecutive seasons (September - June).
Suitable evidence for use of a hibernaculum includes observation of one or more individuals in cover areas just after emerging from or prior to entering the hibernacula in the spring or fall, respectively.
Physical Appearance and Context
Nests have not been detected for Eastern Yellow-bellied Racers in Canada, but it is believed that eggs are laid in loose soil, mammal burrows or under large rocks 1, 10. In southcentral Saskatchewan, young of the year have been observed 200 - 500 metres from hibernacula2, therefore it is expected that nests are likely present near those areas.
Nests are the locations where eggs are laid, and then develop and hatch. Data on Western Yellow-bellied Racers suggest that the species does not incubate their eggs themselves, but instead use nests that are suitable for the passive incubation of the eggs 17, which may explain why, in US study sites, females prefer warm, south-facing, slopes as nest sites 18.
Damage and Destruction of Residence
Examples of activities that are likely to result in the damage or destruction of nests, but are not limited to, the following:
|Activity likely to damage or destroy nests||Potential effect of the activity on nests|
If damage or destruction to a nest occurs when it is occupied by an individual of the species (e.g., nesting female, egg, hatchling), the SARA prohibition again the killing, harming and harassment of individuals [s.32(1)] may be applicable in place of, or in addition to, the prohibition against the damage or destruction of a species' residence [s.33].
Period and Frequency of Occupancy
Although no Eastern Yellow-bellied Racer nests have been found in Canada, in other parts of their range 10, nests are occupied soon after emergence from the hibernacula in the spring (May/June). Data from Western Yellow-bellied Racers 18, 19, suggest that incubation lasts up to 2 months after eggs are laid. It is not known how long young of the year may use nests after hatching. Until additional information becomes available, nests are considered occupied from May/June until September/October.
Female Eastern Yellow-bellied Racers likely mature at two to three years and live to seven or eight years of age10, meaning that females are capable of reproduction for approximately four years. Some mature Eastern Yellow-bellied Racers, however, may not reproduce yearly10, therefore nests may not be occupied annually. However, as with other egg-laying species of snakes, it is possible that nests are used by multiple individuals. Eastern Yellow-bellied Racers may also display nest site fidelity, laying eggs in the same nests for several years, as evidenced in Western Yellow-bellied Racers20.
Any place used as a nest by Eastern Yellow-bellied Racers is considered a residence year-round. Considering the likely mature period for females and the use of nests over multiple years, locations identified as Eastern Yellow-bellied Racer nests are considered residences until they are known not to have been used by Eastern Yellow-bellied Racers for four consecutive seasons (May - October). The description of this residence type should be reviewed amended as more information becomes available.
Suitable evidence for use of a nest includes observation of one or more individuals at a suspected nest site during the active season and/or reptilian eggs or egg shells that are suspected with reasonable certainty to be Eastern Yellow-bellied Racers.
For more information on the Eastern Yellow-bellied Racer, go to: http://www.sararegistry.gc.ca/species/speciesDetails_e.cfm?sid=280
For more information on SARA, go to: http://www.sararegistry.gc.ca/
Please cite this document as:
Government of Canada. Species at Risk Act Public Registry. Residence Descriptions. Description of residence for the Eastern Yellow-bellied Racer (Coluber constrictor flaviventris) in Canada. [date]. [web link]. (Access date).
1 COSEWIC. 2004. COSEWIC assessment and update status report on the Eastern and Western Yellow-bellied Racers, Columber constrictor flaviventris and Coluber constrictor mormon in Canada. Committee on the Status of Endangered Willdife in Canada, Ottawa. vii + 35pp.
2 Martino, J. M.Sc. Candidate, University of Regina. Regina, SK. personal communication, 2009.
3 Poulin, R. and A. Didiuk. 2008. Survey for Eastern Yellow-bellied Racers on AAFC-PFRA Pastures: A 2007 project for Agriculture and Agri-food Canada - PFRA and supported by the Interdepartmental Recovery Fund. 40pp.
4 Skiftun, C. 2001. Amphibian Surveys in WMU 102, 2001. Fish and Wildlife Management Information System, Alberta Sustainable Resource Development, Retrieved July 29, 2009.
5 Wallis, C. 2006. Burrowing Owl Nesting Success in the Onefour District, 2006. Fish and Wildlife Information Management System, Alberta Sustainable Resource Development, Retrieved July 29, 2009.
6 Wershler, R. 2001. Lethbridge Occurrence Reports, 2000-2002. Fish and Wildlife Management Information System, Alberta Sustainable Resource Development, Retrieved July 29, 2009.
7 Wershler, R. 2001. Medicine Hat Occurrence Reports, 2001. Fish and Wildlife Management Information System, Alberta Sustainable Resource Development, Retrieved July 29, 2009.
8 Wershler, R. 2001. Mountain Plover Habitat and Population Surveys in Alberta, 2001. Fish and Wildlife Management Information System, Alberta Sustainable Resource Development, Retrieved July 29, 2009.
9 Campbell, C.A. and D.W. Perrin. 1991. COSEWIC status report on the Blue Racer Coluber constrictor foxiiin Canada. [With additions on the eastern and western Yellow-bellied Racers by J.M. Macartney and additions on the Blue Racer by B.C. Porchuk; revised and edited by F. Cook and the Subcommittee on Amphibians and Reptiles of COSEWIC for the 1991 meeting; and by R.J. Brooks in 1997]. Committee on the Status of Wildlife in Canada, Ottawa. 36.
10 Fitch, H.S.1963. Natural history of the racer Coluber constrictor. University of Kansas Museum of Natural History Publications. 15(8): p. 351-468.
11 Minton, S.A., Jr. 1972. Amphibians and reptiles of Indiana. Indianapolis: Indiana Academy of Science.
12 Owens, V.1949. An overwintering colony of Coluber constrictor (Say) [sic] and Elaphe o. obsoleta (Say). Herptologica. 5: p. 90.
13 Hobbs, J. and M. Sarell. 2002. An Assessment of Racer and Gopher Snake Habitat in the Williams Lake and 100-Mile Forest Districts. BC Ministry of Environment, Williams Lake, BC.
14 Government of Canada. 2004. Species at Risk Act Policy. DRAFT Technical Guidelines for Describing Residence. Environment Canada, Gatineau, QC. 31 pp.
15 Brown, W.S. and W.S. Parker.1976. Movement ecology of Coluber constrictor near communcal hibernacula. Copeia. 2: p. 225-242.
16 Kissner, K.J., D.M. Secoy, and M.R. Forbes. 1996. Assessing population size and den use of Prairie Rattlesnakes (Crotalus viridis viridis) in southern Saskatchewan. Annual Report Volume 1. Grasslands National Park, 34.
17 Shewchuk, C.H. 1996. The natural history of reproduction and movement patterns in the gopher snake (Pituophis melanoleucus) in Southern British Columbia. Master of Science, University of Victoria.
18 Sarell, M.J. 2003. Racer Species Account. Identified Wildlife Management Strategy, Standards for Managing Identified Wildlife, Version 2003.
19 Nussbaum, R.A., E.D. Brodie, Jr., and R.M. Storm. 1983. Amphibians and reptiles of the Pacific Northwest. Moscow: The Northwest Press of Idaho, A Division of the Idaho Research Foundation. 332.
20 Sarell, M. 2004. Racer. Coluber Constrictor mormon. Identified Wildlife Management Strategy, Accounts and Measures of Managing Identified Wildlife. BC Ministry of Environment, 7pp.
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