Great Basin spadefoot (Spea intermontana) COSEWIC assessment and status report: chapter 11

Technical Summary

Spea intermontana

Great Basin Spadefoot – Crapaud du Grand Bassin

Range of Occurrence in Canada:
British Columbia

Extent and Area Information

Extent of occurrence (EO) (km²):
The range consists of several separate regions in the Okanagan valley Similkameen valley, Kettle-Granby River valley, Thompson-Nicola valley and South Cariboo, respectively. Populations in the Nicola Valley and in the South Cariboo might be further separated from the rest of the northern population. Calculated from distribution records from 1985 to 2006.
30,770 km²
Specify trend in EO:
Stable
Are there extreme fluctuations in EO?
No
Area of occupancy (AO) (km²):
Method A) Calculated as the area of all observations from 1985 to 2006 buffered by a 1 km radius circle centred on each observation; overlapping circles were merged together to avoid counting the same area more than once. Method B) Calculated as the area of the 2 km × 2 km grid squares intersecting all observations from 1985 to 2006.
619 km²(method A), 864 km² (method B)
Specify trend in AO:
Unknown
Are there extreme fluctuations in AO?
Probably not
Number of known or inferred current locations
Calculated from distribution records from 1985 to 2006; localities closer than 500 m were considered the same site, and each distribution record was treated equally.
About 235 sites, possibly more in the Cariboo region
Specify trend in #:
The increase in number of known sites within past 10 years due to increased search effort does not reflect an expansion of AO; it is unknown whether all sites recorded since 1985 are still occupied:
Unknown
Are there extreme fluctuations in number of locations?
The number of occupied breeding sites fluctuates greatly from year to year, depending on environmental conditions, mainly availability of water:
Yes
Specify trend in area, extent or quality of habitat :
All are declining

Population Information

Generation time (average age of parents in the population):
No data available – approximated from sexual maturity, which occurs at 2-3 years, and longevity (10 or more years):
Ca. 3-5 years
Number of mature individuals:
based on observations of a few, very large choruses although numbers fluctuate from year to year and most choruses are small.:
Maximum 10,000 but due to fluctuations may periodically be much less.
Total population trend:
Unknown
% decline over the last/next 10 years or 3 generations.
Unknown
Are there extreme fluctuations in number of mature individuals? Based on breeding records and comparison with related species.
Yes
Is the total population severely fragmented?
Yes
Specify trend in number of populations:
unknown
Are there extreme fluctuations in number of populations?
Not at large scales

List populations with number of mature individuals in each:

Thompson-Nicola valleys/South Cariboo:
thousands of adults;
Okanagan, Similkameen, Kettle-Granby River valleys:
possibly >5,000 adults; no accurate estimates available

Threats (actual or imminent threats to populations or habitats)

Rescue Effect (immigration from an outside source)

Status of outside population(s)?

USA:
Not at risk: N5 (“demonstrably widespread, abundant, and secure”)
Arizona
S2 (“imperiled”).
Colorado and Wyoming
S3 (“vulnerable to extirpation or extinction”).
Idaho and Nevada
S4 (“apparently secure”).
California, Oregon, Utah and Washington
S5 (“demonstrably widespread, abundant, and secure”).
Is immigration known or possible?
Possible
Would immigrants be adapted to survive in Canada?
Probably
Is there sufficient habitat for immigrants in Canada?
Possibly
Is rescue from outside populations likely?
No

Quantitative Analysis

Current Status

Status and Reasons for Designation

Status: Threatened

Alpha-numeric code: B2ab(ii,iii)c(iv)

Reasons for Designation: This small, rotund, toad-like amphibian has under each hind foot a prominent tubercle, or “spade”, which it uses for burrowing. The species has a restricted distribution in Canada in the semi-arid and arid areas of southern interior British Columbia. Parts of this region are experiencing rapid loss and alteration of critical habitats for the spadefoot, including loss of breeding sites, because of urban and suburban expansion, increased agriculture and viticulture, and the introduction of alien fish species and disease. The protected areas it inhabits are losing surrounding natural buffer habitats due to encroaching agricultural and housing developments. In consequence, available habitat in some parts of the range is becoming fragmented, resulting in increased local extinction probabilities for the sites that remain. Although spadefoots may use artificial habitats for breeding, there is evidence that such habitats may be ecological traps from which there may be little or no recruitment.

Applicability of Criteria

Criterion A: (Declining Total Population): Insufficient data to quantify decline.

Criterion B: (Small Distribution, and Decline or Fluctuation): Qualifies for Threatened as the Area of Occupancy is <1,000 km² and declines are evident in Area of Occupancy and in the area, extent and quality of habitat. The species is critically dependent upon a limited number of small breeding sites that are increasingly isolated from each other due to habitat fragmentation. Furthermore, there is a high probability of large fluctuations in the number of adult individuals.

Criterion C: (Small Total Population Size and Decline): May meet the criteria for Threatened C2a as the total adult population size may fluctuate below 10,000 individuals and overall decline in abundance may be inferred from the loss and degradation of habitats. Accurate estimations of decline in abundance are likely precluded due to fluctuating population sizes.

Criterion D: (Very Small Population or Restricted Distribution): Not applicable.

Criterion E: (Quantitative Analysis): Not applicable.

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2018-01-02