Hotwater physa (Physella wrighti) COSEWIC assessment and upate status report: chapter 2

Executive Summary

Hotwater Physa
Physella Wrighti

Species information

The Hotwater Physa, Physella wrighti, is a freshwater snail of the family Physidae. This family is characterized by sinistral (left-handed) coiling. The maximum shell length recorded for P. wrighti is 9.1 mm but most specimens are smaller.

Within the scientific community, there is uncertainty as to whether P. wrighti is biologically distinct from the common, widespread P. gyrina. Recent studies of genetic relationships of these snails have not resolved the uncertainties in this group.

Distribution

Physella wrighti occurs only within the Liard River hotsprings complex located in Liard River Hotsprings Provincial Park (LRHPP) in northern British Columbia. The Extent of Occurrence of P. wrighti is approximately 16,310 (0.02 km²), within which the Area of Occupancy is 1 km². Since the snail occupies only a narrow strip at the edges of two pools and an outlet stream, the real area occupied is approximately 4.6 m² (4.6 × 10-6 km²).

Habitat

Physella wrighti occurs in habitat that maintains water temperature of 23–40°C year round. It occupies substrates near a water/air interface in areas of little or no water flow where the snails can position themselves and their eggs at temperatures optimal for life history requirements. This habitat occurs in LRHPP along parts of the margins of Alpha Stream and around the perimeters of Alpha and Beta pools.

Biology

Physella wrighti grazes on algal and microbial growth. As a physid snail, P. wrighti is an oviparous (egg-laying) hermaphrodite. In temperate climates, physids generally lay eggs in the spring. The eggs develop directly into juveniles that mature during the summer, lay eggs the following spring, and die. However, physids living at warmer temperature might accelerate these life history traits and exhibit no seasonality of reproduction. No studies have been conducted on P. wrighti so no data are available on the growth rate, longevity, age at sexual maturity, egg development rate, or seasonality of reproduction for this species in its natural habitat.

Population sizes and trends

The population of P. wrighti at LRHPP occurs in three definable areas: Alpha Stream, lower Alpha Pool and Beta Pool, all of which are probably connected through the movements of wildlife and humans, and by natural events. Three abundance estimates of P. wrighti in Alpha Stream found the number of snails to be 2,100 in September 1997, 5,200 in August 2000, and 1,400 in August 2006. Differences in these population estimates might partially be due to differences in the length of the stream surveyed. Additional surveys with standardized protocols are required to assess the population trend within Alpha Stream but the current evidence does not indicate a decline in the population of P. wrighti. Two abundance estimates in Alpha Pool found the number of snails to be 2,100 in January 2000 and 23 in August 2006. This difference might be a seasonal population trend similar to that noted for a different species of hotsprings snails in Banff National Park where the population is larger in the winter. Alternatively, the differences in these population estimates could be related to the absence of Chara plants in Alpha Stream in 2006. One abundance estimate in Beta Pool found the number of snails to be 910 in August 2006.

Limiting factors and threats

The most obvious natural limiting factors for Physella wrighti are its putative requirement for warm water and its requirement to access the water/air interface for respiration. This speciesis extremely vulnerable to disturbance because it is endemic to the Liard River Hotsprings complex. The source of the heated water in these springs lies outside of LRHPP, and exploratory drilling for oil and gas could potentially be a significant threat to this species if drilling into the fracture results in a redirection of flow away from the springs.

These hotsprings have been developed for human use for many years and have had up to 40,000 visitors per year. Natural or anthropogenic diversion of Alpha Stream could expose P. wrighti to lethal ambient air temperatures, and the addition of foreign substances to Alpha or Beta Pools (e.g., shampoo, bath oil) might limit the snail’s access to air and/or coat them in substances that could interfere with life processes.

The introduction of turtles, found and removed on at least two occasions, and the potential for introducing other exotic animals into the Liard Hotsprings, is also a serious threat. These could have devastating ecological effects on P. wrighti if an aggressive predator or competitor was introduced.

Special significance of the species

Hot water species are of significant scientific interest because they might have arisen from a marginal population that possesses a gene pool more readily able to adapt or acclimate to changing conditions than can congeneric species. Physella wrighti is an indicator that in LRHPP the relatively warm northern ecosystem continues to provide appropriate habitat for unique fauna in spite of development and continued human use. Physella wrighti is one of several locally endemic plants and animals that are associated with the consistently warm lotic and lentic habitats afforded by this hotspring system.

Existing protection or other status designations

In May 2000, P. wrighti was listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada, and based on this designation, it was placed on Schedule 1 of the Species at Risk Act (SARA) in 2003. SARA designates Fisheries and Oceans Canada as the responsible jurisdiction for P. wrighti. Under the Fisheries Act (Canada) protection is afforded by preventing harmful alteration, disruption or destruction of fish habitat and prohibits release of deleterious substances into fish-bearing waters. As a Class A B.C. Provincial Park, LRHPP has its management governed by the Park Act (1996), which protects the park’s natural resources. In accordance with SARA regulations, a recovery strategy for P. wrighti has been developed.

COSEWIC History

The Committee on the Status of Endangered Wildlife in Canada (COSEWIC) was created in 1977 as a result of a recommendation at the Federal-Provincial Wildlife Conference held in 1976. It arose from the need for a single, official, scientifically sound, national listing of wildlife species at risk. In 1978, COSEWIC designated its first species and produced its first list of Canadian species at risk. Species designated at meetings of the full committee are added to the list. On June 5, 2003, the Species at Risk Act (SARA) was proclaimed. SARA establishes COSEWIC as an advisory body ensuring that species will continue to be assessed under a rigorous and independent scientific process.

COSEWIC Mandate

The Committee on the Status of Endangered Wildlife in Canada (COSEWIC) assesses the national status of wild species, subspecies, varieties, or other designatable units that are considered to be at risk in Canada. Designations are made on native species for the following taxonomic groups: mammals, birds, reptiles, amphibians, fishes, arthropods, molluscs, vascular plants, mosses, and lichens.

COSEWIC Membership

COSEWIC comprises members from each provincial and territorial government wildlife agency, four federal entities (Canadian Wildlife Service, Parks Canada Agency, Department of Fisheries and Oceans, and the Federal Biodiversity Information Partnership, chaired by the Canadian Museum of Nature), three non-government science members and the co-chairs of the species specialist subcommittees and the Aboriginal Traditional Knowledge subcommittee. The Committee meets to consider status reports on candidate species.

Definitions (2008)

Wildlife Species
A species, subspecies, variety, or geographically or genetically distinct population of animal, plant or other organism, other than a bacterium or virus, that is wild by nature and is either native to Canada or has extended its range into Canada without human intervention and has been present in Canada for at least 50 years.

Extinct (X)
A wildlife species that no longer exists.

Extirpated (XT)
A wildlife species no longer existing in the wild in Canada, but occurring elsewhere.

Endangered (E)
A wildlife species facing imminent extirpation or extinction.

Threatened (T)
A wildlife species likely to become endangered if limiting factors are not reversed.

Special Concern (SC) Footnotea
A wildlife species that may become a threatened or an endangered species because of a combination of biological characteristics and identified threats.

Not at Risk (NAR) Footnoteb
A wildlife species that has been evaluated and found to be not at risk of extinction given the current circumstances.

Data Deficient (DD) Footnotec
A category that applies when the available information is insufficient (a) to resolve a species' eligibility for assessment or (b) to permit an assessment of the species' risk of extinction.

 

Canadian Wildlife Service

The Canadian Wildlife Service, Environment Canada, provides full administrative and financial support to the COSEWIC Secretariat.

 

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