Recovery Strategy for the Gray’s Desert-parsley (Lomatium grayi) in Canada
Table of Contents
- Recommendation and Approval Statement
- Executive Summary
- Recovery Feasibility Summary
- 1. COSEWIC Species Assessment Information
- 2. Species Status Information
- 3. Species Information
- 4. Threats
- 5. Population and Distribution Objectives
- 6. Broad Strategies and General Approaches to Meet Objectives
- 7. Critical Habitat
- 8. Measuring Progress
- 9. Statement on Action Plans
- 10. References
- Appendix A: Effects on the Environment and Other Species
© Carrina Maslovat
For copies of the recovery strategy, or for additional information on species at risk, including COSEWIC Status Reports, residence descriptions, action plans, and other related recovery documents, please visit the SAR Public Registry.
Cover illustration: Gray’s Desert-parsley photograph by Carrina Maslovat.
Également disponible en français sous le titre
« Programme de rétablissement du lomatium de Gray (Lomatium grayi) au Canada »
© Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment, 2014. All rights reserved.
Catalogue no. En3-4/174-2013E-PDF
Content (excluding the illustrations) may be used without permission, with appropriate credit to the source.
Recommendation and Approval Statement
The Parks Canada Agency led the development of this federal recovery strategy, working together with the other competent minister(s) for this species under the Species at Risk Act. The Chief Executive Officer, upon recommendation of the relevant Park Superintendent(s) and Field Unit Superintendent(s), hereby approves this document indicating that Species at Risk Act requirements related to recovery strategy development have been fulfilled in accordance with the Act.
Field Unit Superintendent, Coastal BC, Parks Canada Agency
Chief Executive Officer, Parks Canada Agency
The federal, provincial, and territorial government signatories under the Accord for the Protection of Species at Risk (1996) agreed to establish complementary legislation and programs that provide for effective protection of species at risk throughout Canada. Under the Species at Risk Act (S.C. 2002, c.29) (SARA), the federal competent ministers are responsible for the preparation of recovery strategies for listed Extirpated, Endangered, and Threatened species and are required to report on progress five years after the publication of the final document on the SAR Public Registry.
The Minister of the Environment and the Minister responsible for the Parks Canada Agency is the competent minister for the recovery of the Gray’s Desert-parsley and has prepared this strategy, as per section 37 of SARA. To the extent possible, it has been prepared in cooperation with the provincial government of British Columbia.
Success in the recovery of this species depends on the commitment and cooperation of many different constituencies that will be involved in implementing the directions set out in this strategy and will not be achieved by the Parks Canada Agency, or any other jurisdiction alone. All Canadians are invited to join in supporting and implementing this strategy for the benefit of the Gray’s Desert-parsley and Canadian society as a whole.
This recovery strategy will be followed by one or more action plans that will provide information on recovery measures to be taken by the Parks Canada Agency and other jurisdictions and/or organizations involved in the conservation of the species. Implementation of this strategy is subject to appropriations, priorities, and budgetary constraints of the participating jurisdictions and organizations.
The recovery of Gray’s Desert-parsley will be coordinated with the recovery of other species inhabiting Garry Oak woodlands (Parks Canada Agency 2006).
Thank you to Carrina Maslovat for collecting and compiling the species and habitat information used in preparing this recovery strategy. The Garry Oak Ecosystems Recovery Team is the recovery team for the Gray’s Desert-parsley and was involved in the development of this recovery strategy. Further revision was the result of comments and edits provided by a number of organizations: the Province of British Columbia, Parks Canada Agency, and Environment Canada. Thank you to all the landowners who support recovery of this species on their land and provided access for surveys.
The Canadian population of Gray’s Desert-parsley (Lomatium grayi) was assessed as Threatened in 2008 by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) and in 2011 the Canadian population was listed as Threatened under Canada’s Species at Risk Act.
Gray’s Desert-parsley is a perennial plant that grows on southwest facing cliffs or steep slopes in areas that are difficult to access by people and herbivores. The Canadian population of Gray’s Desert-parsley comprises <1% its global range. In Canada, Gray’s Desert-parsley is limited to three populations on two separate Gulf Islands: two on Salt Spring Island and one on Galiano Island.
Several factors limit the survival of Gray’s Desert-parsley populations in Canada, including its specificity to rare habitats, limited dispersal abilities, weak competitive ability, predisposition to demographic failure, small area of physical occupancy, and small, highly fragmented populations that constrain genetic diversity. The primary threat to Gray’s Desert-parsley is herbivory by mammals that directly consume and trample the plants, flowers and seeds. Further, Gray’s Desert-parsley populations are at risk from competition from invasive alien plants, recreational activities (specifically rock climbing), dumping of garbage and garden waste, and horticultural collection.
In the short term, recovery objectives for Gray’s Desert-parsley will focus on the maintenance of the three extant populations. Broad strategies to be taken to address the threats to the survival and recovery of the Gray’s Desert-parsley are presented in section 6 Broad Strategies and General Approaches to Meet Objectives.
This recovery strategy identifies critical habitat for the Gray’s Desert-parsley in Canada, to the extent possible at this time, based on the best available information. Activities likely to result in the destruction of critical habitat have been identified.
Further recovery action for Gray’s Desert-parsley will be incorporated into one or more action plans by 2018.
Recovery Feasibility Summary
The recovery of Gray’s Desert-parsley in Canada is considered feasible based on the criteria outlined by the Government of Canada (2009):
- Individuals of the wildlife species that are capable of reproduction are available now or in the foreseeable future to sustain the population or improve its abundance.
Yes. Mature individuals of Gray’s Desert-parsley have plentiful seed-set. The seed germinates readily and seedlings have been observed in the wild.
- Sufficient suitable habitat is available to support the species or could be made available through habitat management or restoration.
Yes. There is sufficient habitat to support all three existing populations at their current levels and active stewardship and restoration may increase the amount of available habitat to support larger populations as outlined in the broad strategies and general approaches to meet the population and distribution objectives.
- The primary threats to the species or its habitat (including threats outside Canada) can be avoided or mitigated.
Yes. With the cooperation of all responsible jurisdictions and the participation of the private landowner, the primary threats facing Gray’s Desert-parsley can be addressed and at least partially mitigated through recovery actions. There are no unavoidable threats to this species or its habitat that preclude recovery.
- Recovery techniques exist to achieve the population and distribution objectives or can be expected to be developed within a reasonable timeframe.
Yes. Recovery success will be closely tied to addressing threats through habitat stewardship and public outreach and education, in combination with long-term population monitoring and inventory.
1. COSEWIC Species Assessment Information
2. Species Status Information
The Canadian population of Gray’s Desert-parsley (Lomatium grayi) was assessed as Threatened in 2008 by the Committee on Status of Endangered Wildlife in Canada (COSEWIC), and in February 2011 the population was listed as Threatened under Canada’s Species at Risk Act (SARA). Less than 1% of Gray’s Desert-parsley range and population occurs within Canada. Conservation ranks for Gray’s Desert-parsley in other jurisdictions where it occurs are provided in Table 1.
|British Columbia||S1||Critically imperilled|
|United States||NNR||Not ranked|
|New Mexico||S1?||Critically imperilled?|
3. Species Information
3.1. Species Description
Gray’s Desert-parsley is a large, strong-smelling perennial in the carrot family (Apiaceae). It grows from a deep taproot and usually has a branched stem-base (caudex). The leaves are finely divided and bluish-green in colour. Plants are usually 20–40 cm tall and can be up to 40–50 cm wide. The leafless flowering stems are taller than the foliage and produce large yellow-flowered umbels. The fruits are flattened, elliptical and have wings that are 2/3 the width of the fruit body.
The COSEWIC status report and the Illustrated Flora of B.C. provide more detailed descriptions of the species (COSEWIC 2008; Douglas et al. 1998).
3.2. Population and Distribution
Globally, Gray’s Desert-parsley is found in northwestern North America between the Cascade/Sierra Nevada Mountains and the Rocky Mountains (Figure 1). It has been recorded in Washington, Idaho, Oregon, Wyoming, Nevada, Utah, Colorado, California, and New Mexico (COSEWIC 2008; NatureServe 2011).
In Canada, Gray’s Desert-parsley is at the northern edge of its global range (Figure 2). The Canadian population is separated by 250 km from the closest extant population in the U.S and there have not been any taxonomic or genetic studies on the Canadian plants.
There are three known Gray’s Desert-parsley populations in Canada, one on Galiano Island and two on Salt Spring Island. Recent surveys concluded that the single Salt Spring Island population listed in the status report (COSEWIC 2008) should be considered two populations (Maxwell Point and Mount Maxwell), because the two locations are separated by more than 1 kilometre (Maslovat 2010).
From 2002/2004 to 2010 the abundance of all three populations has increased (except for one subpopulation) and the proportion of flowering plants has remained constant (Janszen and Roemer 2002; COSEWIC 2008; Maslovat 2010; Table 2). Surveys of the three subpopulations at Maxwell Point in 2010 found the number of flowering plants is similar to previous surveys, but the number of non-flowering plants is much higher. In comparison, both the number of flowering and non-flowering plants at Mount Maxwell was higher in 2010 than previously counted in 2002. The Mount Maxwell non-flowering plants included large plants that appeared mature but most were small seedlings found in soil at the base of the cliffs. Some of the 10 subpopulations identified in 2002 were determined to be contiguous in 2010 since plants were found between the previously isolated points. Contiguous subpopulations were, therefore, amalgamated into six subpopulations. Because plants were found between the previously identified subpopulations at Mount Maxwell, it is possible that these represent patches that were present but were missed during previous surveys. Alternatively, a release from the previous grazing pressure from feral livestock may be allowing plants to expand in the area. Lastly, the Galiano population count in 2010 had no margin of error since surveys were conducted from both the top and bottom of the cliff (Maslovat 2010).
Long-term trends are not available for this species. Although there is no physical evidence that the range of Gray’s Desert-parsley has changed since historic times (COSEWIC 2008), Gray’s Desert-parsley habitat is closely associated with Garry Oak ecosystems which have seen a decline of more than 95% in the Victoria area (Lea 2006). Further, the remaining ecosystems fragments are affected by broad changes in ecological dynamics (e.g., fire suppression, and increased grazing and browsing). It is unknown whether threats have reduced population sizes below historic levels.
Figure 1. Global distribution of Gray’s Desert-parsley, shaded regions indicate the species’ range (from COSEWIC 2008).
Figure 2. Distribution of Gray’s Desert-parsley in Canada (adapted from COSEWIC 2008). Large closed circles indicate extant populations and the numbers refer to locations listed in Table 2.
|Number on map||General location||Population size, description and year counted||Land Tenure|
|2002: 1650 plants +/-100 plants (1/2 to 2/3 flowering)|
2010: 1738 plants (926 flowering and 812 non-flowering)
|2004: 40 plants (1/2 to 2/3 flowering)|
-estimated 50 plants due to habitat inaccessibility
2010: 69 plants (19 flowering and 50 non-flowering)
-estimated total of 85 plants due to habitat inaccessibility
|2002: 150 plants (1/2 to 2/3 flowering)|
-estimated 190 plants due to habitat inaccessibility
2010: 359 plants (187 flowering and 172 non-flowering)
-estimated total of 450 plants due to habitat inaccessibility
3.3. Needs of the Gray’s Desert-parsley
Throughout its range Gray’s Desert-parsley is found in a range of dry, rocky habitats including sagebrush slopes, rocky talus slopes, knolls, cliffs, open grassland, and dry stream beds. In Canada, Gray’s Desert-parsley is found in Garry Oak and associated ecosystems in the dry Coastal Douglas-fir Biogeoclimatic Zone on the Gulf Islands adjacent to southeastern Vancouver Island. This species grows in shallow, well-drained, rocky soils primarily on southwest facing cliff faces or in extremely steep terrain. The plants establish on rock ledges, under rock overhangs, in crevices, or on accumulations of loose talus that are surrounded by rock (Figure 3). Some sites have spring seepage along adjacent rock walls, usually wet in the fall, winter, and spring and dry in the summer months. In Canada, Gray’s Desert-parsley is found from sea level to 600 m elevation, whereas in the United States it occurs from lowlands to near alpine elevations. The species is tolerant of partial shade produced by scattered, stunted trees and shrubs. There are no consistent plant communities associated with Gray’s Desert-parsley and species combinations depend on which other species are able to establish in the adjacent habitat (COSEWIC 2008; Maslovat 2010).
A number of factors may limit the survival and recovery of Gray’s Desert-parsley in Canada:
- Dependence on highly specific habitats associated with Garry Oak and associated ecosystems, most of which have been lost or damaged by habitat conversion (i.e., the loss of suitable habitat, often as a result of urban development), forest encroachment, and/or a shift to ecosystem dominance by invasive alien plants.
- A lack of special structures to aid in the long-distance dispersal of seeds limits the potential for local rescue effects or establishment in unoccupied habitat areas.
- Apparently weak competitive ability, especially with respect to invasive alien plants.
- Predisposition to demographic failure because its annual life cycle may result in high juvenile mortality if the late spring/early summer drought arrives early.
- Very small area of physical occupancy, which leaves it susceptible to chance events including those which operate at a small scale.
- Extremely small population sizes, which may constrain the species’ genetic diversity, and increase its vulnerability to extirpation due to demographic stochasticity.
Figure 3. Gray’s Desert-parsley habitat at Mount Maxwell, Salt Spring Island. Photo by Carrina Maslovat.
4.1. Threat Assessment
|Threat||Level of Concern1||Extent||Occurrence||Frequency||Severity2||Causal Certainty3|
|Disturbance or harm|
|Alien, invasive or introduced species|
|Encroachment by invasive alien plants||Low||Widespread||Current||Continuous||Low||Medium|
|Dumping garden waste or garbage||Low||Localized||Unknown||Unknown||Low||Medium|
|Biological Resource Use|
2 Severity: reflects the population-level effect (High: very large population-level effect, Medium, Low, and Unknown).
3 Causal certainty: reflects the degree of evidence that is known for the threat (High: available evidence strongly links the threat to stresses on population viability; Medium: there is a correlation between the threat and population viability e.g., expert opinion; Low: the threat is assumed or plausible).
4.2. Description of Threats
4.2.1. Disturbance or harm
Grazing is the biggest threat to Gray’s Desert-parsley. Gray’s Desert-parsley plants grow almost exclusively on steep, inaccessible terrain that cannot be reached by grazing mammals. Despite growing on deeper soil, the few plants that are accessible to herbivores are small because grazing limits either their long-term survival or prevents them from reaching full size (COSEWIC 2008). Flowering plants growing in deeper soil were found in only one location where the deeper soil habitat could not be accessed by deer (Maslovat 2010).
Both historic grazing by feral livestock and contemporary grazing by native herbivores at increased abundances are considered threats to Gray’s Desert-parsley. Feral livestock have been present on both Galiano and Salt Spring Islands. Feral goats (Capra hircus) were on Galiano Island from 1920 until at least 1960 (Geist 1960). Neither feral goats nor domestic sheep (Ovis aries) are currently on Galiano Island (Crowe pers. comm. 2010). Feral goats were on Salt Spring from the 1920s until 1957 but goats have not been observed on Mount Maxwell in recent years (Geist, 1960; Linton pers. comm. 2010). It is unlikely sheep are still present on Mount Maxwell: two sheep were seen two years ago but have not seen since (Linton pers. comm. 2010). Native Black-tailed Deer (Odocoileus hemionus columbianus) are abundant on both Galiano and Salt Spring Islands and increased habitation by people has limited predator populations and increased the abundance of native herbivores. In addition to direct consumption, herbivores may cause damage by trampling or dislodging plants.
Small herbivores may also be a threat. Cultivated Gray’s Desert-parsley specimens are eaten by mice, rats, and cottontail rabbits on both Galiano and Salt Spring Islands; however, it is not known whether rodents eat wild Gray’s Desert-parsley plants (COSEWIC 2008). Seed predation by insects has also been observed but the species responsible has not been identified. Evidence of defoliation by Anise Swallowtail Butterfly larvae was observed in the Mount Maxwell population (COSEWIC 2008).
The effect of herbivory on seed production and reproduction is unknown. Frequent loss of small numbers of seeds will have a smaller impact on population dynamics than larger, more infrequent grazing (Menges et al. 2004). This threat is considered a medium level of concern because while all three populations showed some evidence of grazing, with either leaves or flowering stems missing, not all subpopulations showed evidence of grazing (Maslovat 2010).
The recreational activities of rock climbing and hiking threaten subpopulations of Gray’s Desert-parsley on Salt Spring Island. The steep cliffs of Mount Maxwell on Salt Spring Island are a popular for recreational rock climbing (Gessinger pers. comm. 2010). Hiking and rock climbing may trample plants, dislodge plants, compact the soil, and increase erosion. A climbing rope was attached to a tree within the habitat of one Gray’s Desert-parsley subpopulation on Mount Maxwell, Salt Spring Island. This is the only location where fewer plants were found in 2010 than in previous surveys (19 compared to 45) (Maslovat 2010). Although rock climbing may occur at other locations with Gray’s Desert-parsley, there was no direct evidence of this during 2010 surveys. There is also no evidence of rock climbing in Gray’s Desert-parsley habitat on Galiano Island (Millard pers. comm. 2010 and Crowe pers. comm. 2010). Consequently, this threat is considered a low level of concern.
4.2.2. Alien, invasive or introduced species
Habitat degradation caused by invasive alien plants may threaten Gray’s Desert-parsley, although the steep and rocky habitat generally has few microsites where invasive alien plants can establish. The invasive alien shrub, Scotch Broom (Cytisus scoparius), is present in large numbers at the top of the ridge above Gray’s Desert-parsley occurrences on Galiano Island and is present in low numbers in one subpopulation on Mount Maxwell, Salt Spring Island (COSEWIC 2008; Millard pers. comm. 2010; Maslovat 2010). Invasive alien herbaceous species are also present including grasses: Barren Brome (Bromus sterilis), Sweet Vernal Grass (Anthoxanthum odoratum) and Hedgehog Dogtail (Cynosurus echinatus); and forbs: Tower Mustard (Arabis glabra), Spreading Hedge-parsley (Torilis arvensis) and Common Vetch (Vicia sativa). The establishment of invasive alien plants in the small microsites where Gray’s Desert-parsley occurs may pre-empt germination and seedling growth, limiting future recruitment. Establishment of invasive alien shrubs in adjacent areas may also increase shade in the habitat and further limit Gray’s Desert-parsley growth and recruitment. Overall, this threat is considered a low level of concern.
Pollution caused by dumping of garden waste material or garbage over cliffs where Gray’s Desert-parsley grows can threaten this species. The top of some of the steep cliffs occupied by Gray’s Desert-parsley are easily accessed by roads. One subpopulation on Mount Maxwell, Salt Spring Island is littered with garbage (including bicycles, appliances, beer bottles, etc.) that has been dumped from the summit. Although the garbage lands primarily on the slope below the plants, it may dislodge or damage plants as it ricochets off the cliff face or smother the plants if it lands directly on them. This subpopulation is the same one at risk from rock climbing and is the only population to have a smaller total number of plants than in previous surveys. A small part of the Galiano population occurs on private property and it is possible, although unlikely, that garden waste could be dumped over the top of the cliffs that support Gray’s Desert-parsley. Garden waste may contain invasive alien plants, seeds, or insects and can spread these species into the habitat of Gray’s Desert-parsley. Gray’s Desert-parsley plants could also be smothered by garden waste thereby inhibiting growth and potentially killing the plants. Consequently, this threat poses a low level of concern.
4.2.4. Biological Resource Use
Collection of Gray’s Desert-parsley for horticultural purposes poses a minor threat to this species’ survival. Gray’s Desert-parsley is an attractive plant that does well in ornamental gardens. It is not known whether seeds or plants are being currently collected for horticulture. Unless this practice is initiated by a nursery or other large-scale propagator, it is unlikely to have a serious negative effect on the population. Therefore, this threat is a considered a low level of concern.
5. Population and Distribution Objectives
In Canada, Gray’s Desert-parsley grows in shallow, well-drained, rocky soils primarily on southwest facing cliffs or in extremely steep terrain in Garry Oak and associated ecosystems and as such had a naturally highly restricted range. Within this range, herbivory, encroachment of invasive alien plants, and human disturbance has likely resulted in population reductions (COSEWIC 2008; Maslovat 2010). There are currently three known Gray’s Desert-parsley populations in Canada, all of which have over 50 individuals (COSEWIC 2008; Maslovat 2010).
In general, it is believed that multiple populations and thousands of individuals are likely required to attain a high probability of long-term persistence for a species (Reed 2005; Brook et al. 2006; and Traill et al. 2009). In an analysis of several published estimates of minimum viable population (MVP) sizes, Traill et al. (2007) found that the median population size required for plants to achieve a 99% probability of persistence over 40 generations was approximately 4,800 individuals (but see Flather et al. 2011; Garnett and Zander 2011; and Jamieson and Allendorf 2012 for critical evaluations of the analyses and the applicability of the results). Such information provides a useful guide, but developing specific quantitative and feasible objectives must consider more than just generalized population viability estimates, including the historic number of populations and individuals, the carrying capacity of extant (and potential) habitat, the needs of other species at risk that share the same habitat, and whether it is possible to establish and augment populations of the species (Parks Canada Agency 2006; Flather et al. 2011; Jamieson and Allendorf 2012). Because not enough of this information is available for Gray’s Desert-parsley, it is currently not possible to determine to what extent recovery is feasible and, therefore, it is not possible to establish quantitative long-term objectives.
Recovery planning approaches (see Section 6) are designed to respond to knowledge gaps so that long-term, feasible, and quantitative recovery objectives regarding size and number of populations can be set in the future. There is no evidence to suggest that any populations of Gray’s Desert-parsley have been lost over time, especially since the species is distinctive and relatively easy to identify. Therefore, there is no justification for the recovery objectives to include establishing new populations. At this time it is possible to set short-term objectives that focus on maintaining the three extant Canadian populations:
Objective 1: Maintain the three extant populations of Gray’s Desert-parsley.
Objective 2: Prevent declines in the known distribution of Gray’s Desert-parsley populations in Canada.
6. Broad Strategies and General Approaches to Meet Objectives
The following are broad strategies and approaches to meet the population and distribution objectives for Gray’s Desert-parsley:
- Population research and monitoring: monitor population trends, habitat attributes, and threats, and conduct population demographic research;
- Population restoration: restore extant populations to recover the Canadian population of the species;
- Habitat and species protection: protect existing populations and their habitat from destruction by developing mechanisms/instruments for protection;
- Stewardship: engage and involve landowners and land managers in recovery activities and decisions for Gray’s Desert-parsley; and
- Public education and outreach: increase public awareness of the species, its needs and conservation value.
6.1. Strategic Direction for Recovery
|Threat or Limitation||Priority||Broad Strategy to Recovery||General Description of Research and Management Approaches|
|Knowledge gaps concerning population trends and augmentation techniques.||High||Population Monitoring|
|Knowledge gaps and limitations regarding population demography|
Encroachment by invasive alien plants
Grazing by vertebrates
|Encroachment by invasive alien plants|
Dumping garden waste or garbage
Grazing by vertebrates
|Medium||Public education and outreach|
|Medium||Habitat and species protection|
6.2. Narrative to Support the Recovery Planning Table
Gray’s Desert-parsley is extremely rare in Canada and a first priority for recovery will be to conserve and restore existing populations and their habitat. Diligence must be exercised in preventing extirpations due to preventable causes. A top priority of recovery will be to steward the land to ensure proper environmental conditions for plant growth and establishment as this is the most straightforward and cost-effective way of ensuring the species’ persistence. Stewardship activities include following best management practices to control invasive alien plants and grazing and to manage recreational activities. In addition, further research is required to better understand the degree of threat from grazing and invasive alien plants and to refine techniques for effective management and restoration of Gray’s Desert-parsley habitat. Population restoration through augmentation will only be considered if population and distribution objectives cannot be met through stewardship.
Careful monitoring is also an important component of recovery for a number of reasons. Monitoring is necessary to ensure the effects of restoration and management techniques are contributing to recovery and are not unduly affecting on non-target species, communities, or ecological processes. Further, additional monitoring data is required to determine long term population objectives for Gray’s Desert-parsley and to identify population criteria (size/distribution) that would trigger immediate re-evaluation of recovery priorities and activities. In addition, regular population monitoring is needed to track the current viability of the species and its response to threats.
There are significant knowledge gaps related to population dynamics including seed bank longevity, demography, reproduction, and recruitment rates of Canadian populations of Gray’s Desert-parsley and these knowledge gaps hamper the ability to set long term objectives. Further research is required so that long-term, feasible, and quantitative recovery objectives regarding size and number of populations can be set in the future. It is also unknown whether there are more Galiano subpopulations that could not be observed by boat surveys and require additional surveys of the cliff faces where access is challenging and additional surveys would be beneficial to accurately determine the size and viability of the current population.
7. Critical Habitat
Areas of critical habitat for Gray’s Desert-parsley are identified in this recovery strategy. Critical habitat is defined in the Species at Risk Act as
habitat that is necessary for the survival or recovery of a listed wildlife species and that is identified as the species’ critical habitat in a recovery strategy or in an action plan for the species (Subsection 2(1)). Habitat for a terrestrial wildlife species is defined in the Species at Risk Act as
…the area or type of site where an individual or wildlife species naturally occurs or depends on directly or indirectly in order to carry out its life processes or formerly occurred and has the potential to be reintroduced (Subsection 2(1)).
7.1. Identification of the Species’ Critical Habitat
7.1.1. Geographical Location
Critical habitat for Gray’s Desert-parsley is identified in this recovery strategy to the extent possible based on the best available information. This habitat is believed to be sufficient for the recovery of the Gray’s Desert-parsley. However, more precise boundaries may be mapped (in particular if grazing pressure is removed), and additional critical habitat may be added in the future if additional research supports the inclusion of areas beyond those currently identified.
Within the geographical boundaries identified in Figures 5 through 8, critical habitat for the survival of Gray’s Desert-parsley populations consists of the slope (Maslovat 2010) matching the biophysical attributes described in Section 7.1.2. The entire cliff face is required to maintain the seed banks, and dispersal sites required for the survival of the population.
7.1.2. Biophysical Attributes
The habitat of Gray’s Desert-parsley in Canada occurs in Garry Oak and associated ecosystems on the Gulf Islands along the southeast coast of British Columbia. The habitat is characterized as open areas with an occasional stunted tree or shrub and Gray’s Desert-parsley plants usually occur in small pockets of soil or crevices scattered throughout steep or vertical, southwest facing cliffs (COSEWIC 2008). Field investigations at Galiano Island, Maxwell Point, and Mount Maxwell (Salt Spring Island) were used to further characterize the habitat of Gray’s Desert-parsley (Maslovat 2010).
The habitat for Gray’s Desert-parsley is based on locations where the plants currently grow, but may be different from the habitat preferred by this species if grazing pressure were removed. Consequently, it is difficult to provide a description of critical habitat attributes for Gray’s Desert-parsley that is both inclusive and specific. The critical habitat attributes below cover the range attributes found at the known locations and may not exclude some habitat types that are unsuited to the species. Therefore, critical habitat identification is based on the recorded Gray’s Desert-parsley patches not the presence of the following attributes:
- Full sun to part shade (plants are tolerant of shade cast by trees and shrubs growing in adjacent deeper soils).
- Southwest facing slopes (cliff faces or extremely steep terrain; aspect 190°-310°).
- Low elevation (0 to 600 metres above sea level).
- Shallow, well-drained, rocky soil or talus (Gray’s Desert-parsley establishes on rock ledges, under rock overhangs, in crevices or on accumulations of loose talus).
Figure 4. Area 1027_01 (~11.6 ha) within which critical habitat for Gray’s Desert-parsley is found at Galiano Island, on non-federal lands. The identified critical habitat within this area is ~ 3.9 ha.
Figure 5. Area 1027_02 (~4.5 ha) within which critical habitat for Gray’s Desert-parsley is found at Maxwell Point, on non-federal lands. The identified critical habitat within this area is ~ 0.26 ha.
Figure 6. Areas 1027_03 (~0.2 ha) and 1027_04 (0.31 ha) within which critical habitat for Gray’s Desert-parsley is found at Mount Maxwell, on non-federal lands. The identified critical habitat within these areas is 0.01 ha and 0.04 ha, respectively.
Figure 7. Area 1027_05 (~34 ha) within which critical habitat for Gray’s Desert-parsley is found at Mount Maxwell, on non-federal lands. The identified critical habitat within this area is ~ 4.6 ha.
7.2. Activities Likely to Result in the Destruction of Critical Habitat
Examples of activities likely to destroy critical habitat are provided below (Table 5). Destruction of critical habitat will result if any part of the critical habitat is degraded, either permanently or temporarily, such that it would not serve its function when needed by the species. Destruction may result from single or multiple activities at one point in time or from the cumulative effects of one or more activities over time.
|Activity||Effect of activity on critical habitat||Most likely locations|
|Damaging recreational use (e.g., rock climbing, hiking)||Increased erosion, loss of growing substrate for existing and future plants.|
Soil compaction leading to altered moisture availability (decreased infiltration and increased runoff).
In addition, this activity is likely to introduce or spread invasive alien plant species. Invasive alien plants compete with Gray’s Desert-parsley and alter the availability of light, water, and nutrients in the habitat, such that the habitat would not provide the necessary habitat conditions required by Gray’s Desert-parsley.
|Land conversion by human development (e.g., development or modification of existing structures and roads)||Indirect effects of shading (e.g., by introduced plants or nearby structures), and altered moisture regime (e.g., impounded drainage, or reduced water flow to the plants through ditching or diversion of subsurface water by built structures) can alter the habitat of Gray’s Desert-parsley.||Galiano Island|
|Dumping of garbage or garden waste||Dumped material can cover habitat needed for germination and growth resulting in a loss of growing substrate for existing and future plants. Depending on the nature of the dumped items, pollutants may also be introduced into the environment, making it unsuitable for Gray’s Desert-parsley.|
Dumped garden waste is likely to introduce invasive alien plants and may introduce alien insects. Invasive alien plants compete with Gray’s Desert-parsley and alter the availability of light, water, and nutrients in the habitat. Alien insects could consume and/or damage Gray’s Desert-parsley plants.
8. Measuring Progress
The performance indicators presented below provide a way to define and measure progress toward achieving the population and distribution objectives. Progress towards recovering Gray’s Desert-parsley in Canada will be assessed using the following measures for each of the population and distribution objectives:
Objective 1: Maintain the three extant populations of Gray’s Desert-parsley.
- By 2018, best management practices are developed and implemented for all populations.
- The populations remain extant.
- By 2023, all three existing populations show a stable or increasing trend in population size.
Objective 2: Prevent declines in the known distribution of Gray’s Desert-parsley populations in Canada.
- There is no decrease in the known distribution (extent of occurrence and area of occupancy) of Gray’s Desert-parsley in Canada.
9. Statement on Action Plans
One or more action plans will be completed by 2018.
B.C. Conservation Data Centre. 2011. B.C. Species and Ecosystems Explorer. B.C. Ministry of Environment. Web site: http://a100.gov.bc.ca/pub/eswp/ [accessed September 2011].
Brook, B.W., L.W. Traill, and J.A. Bradshaw. 2006. Minimum viable population sizes and global extinction risk are unrelated. Ecology Letters 9:375-382.
COSEWIC. 2008. COSEWIC assessment and status report on the Gray's Desert-parsley, Lomatium grayi in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vi + 27 pp.
Crowe, T, pers. comm. 2010. correspondence to C. Maslovat. Species at Risk Program Coordinator, Galiano Conservancy Association, Galiano Island, B.C.
Douglas, G.W., G.B. Straley, D. Meidinger, and J. Pojar. 1998. Illustrated Flora of British Columbia: Volume 1 Gymnosperms and Dicotyledons (Aceraceae through Asteraceae). B.C. Ministry of Environment, Lands and Parks and Ministry of Forests. Victoria, BC. v + 436 pp.
Flather, C.H., G.D. Hayward, S.R. Beissinger, and P.A. Stephens. 2011. Minimum viable populations: is there a ‘magic number’ for conservation practitioners? Trends in Ecology and Evolution 26:307-316.
Garnett, S.T., and K.K. Zander. 2011. Minimum viable population limitations ignore evolutionary history. Trends in Ecology and Evolution 26(12): 618-619.
Geist, V. 1960. Feral Goats in British Columbia. The Murrelet 41(3):34–40. Web site: http://jstor.org/stable/3534151 [accessed March 2010]
Gessinger, S, pers. comm. 2010 correspondence to C. Maslovat. Rock climber, Salt Spring Island, B.C.
GOERT (Garry Oak Ecosystems Recovery Team). 2002. Recovery strategy for Garry Oak and associated ecosystems and their associated species at risk in Canada: 2001–2006. Draft 20 February 2002. Garry Oak Ecosystems Recovery Team, Victoria, B.C. x + 191 pp. Government of Canada. 2009. Species at Risk Act Policies: Overarching Policy Framework [Draft]. ii + 38pp. Web site: http://www.sararegistry.gc.ca/document/default_e.cfm?documentID=1916 [accessed June 2010].
Jamieson, I.G., and F. W. Allendorf. 2012. How does the 50/500 rule apply to MVPs? Trends in Ecology and Evolution, Online, 1566: 1-7.
Janszen, H. and H. Roemer. 2002. Draft Fieldwork Report on Field Survey of Known and Potential Sites for Lomatium grayi. Garry Oak Ecosystems Recovery Team, Victoria, B.C.
Lea, T. 2006. Historical Garry Oak Ecosystems of Vancouver Island, British Columbia, pre-European Contact to the Present. Davidsonia 17:34–50.
Linton, P, pers. comm. 2010. correspondence to C. Maslovat. Volunteer ecological reserve warden, Mount Maxwell, B.C. Parks, Victoria, B.C.
Maslovat, C. 2010. Towards a Recovery Strategy for the Gray’s Desert-parsley (Lomatium grayi) in Canada. Parks Canada Agency, Ottawa, O.N. v + 46 pp.
Menges, E.S., E.O. Guerrant Jr., and S. Hamze. 2004. Effects of seed collection on the extinction risks of perennial plants. Pp. 305-324. in E.O. Guerrant Jr., K. Havens, and M. Maunder (eds.). Ex Situ Plant Conservation: Supporting Species Survival in the Wild, Island Press, Washington.
Millard, Ken, pers. comm. 2010. correspondence to C. Maslovat. Galiano Conservancy Association, Galiano Island, B.C.
NatureServe. 2011. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Web site: http://www.natureserve.org/explorer. [accessed September 2011].
Parks Canada Agency. 2006. Recovery Strategy for Multi-Species at Risk in Garry Oak Woodlands in Canada. Pp. x +59. in Species at Risk Act Recovery Strategy Series, Ottawa, Ontario.
Reed, D.H. 2005. Relationship between population size and fitness. Conservation Biology 19:563-568.
Traill, L.W., C.J.A. Bradshaw, and B.W. Brook. 2007. Minimum viable population size: A meta-analysis of 30 years of published estimates. Biological Conservation 139:159-166.
Traill, L.W., B.W. Brook, R.R. Frankham, and C.J.A. Bradshaw. 2009. Pragmatic population viability targets in a rapidly changing world. Biological Conservation 143:28–34.
Appendix A: Effects on the Environment and Other Species
A strategic environmental assessment (SEA) is conducted on all SARA recovery planning documents, in accordance with the Cabinet Directive on the Environmental Assessment of Policy, Plan and Program Proposals. The purpose of a SEA is to incorporate environmental considerations into the development of public policies, plans, and program proposals to support environmentally sound decision-making and to evaluate whether the outcomes of a recovery planning document could affect any component of the environment or any of the Federal Sustainable Development Strategy’s goals and targets.
Recovery planning is intended to benefit species at risk and biodiversity in general. However, it is recognized that strategies may also inadvertently lead to environmental effects beyond the intended benefits. The planning process, based on national guidelines, directly incorporates consideration of all environmental effects, with a particular focus on possible impacts upon non-target species or habitats. The results of the SEA are incorporated directly into the strategy itself, but are also summarized below in this statement.
The range of Gray’s Desert-parsley overlaps with a suite of other rare and at risk plants and invertebrates, the totality of which comprise one of the most unique species assemblages known in Canada (GOERT 2002, Table 6). Actions taken to recover Gray’s Desert-parsley should also benefit these species by improving habitat for them. Restoration of the habitat of Gray’s Desert-parsley will be beneficial to species associated with this habitat, which are also affected by competition from invasive alien plants, grazing pressures, and/or recreational activities. Actions taken to aid in the recovery of this species should, if conducted in an appropriate manner (e.g., in an open, informative manner), provide benefits for all at risk species and habitats. This can be accomplished by increasing public awareness of the negative environmental consequences associated with invasive alien species, the threats recreational activities can pose to species at risk, the need to maintain natural ecological processes (e.g., if fire is identified as being a component of the management for some locations that Gray’s Desert-parsley occurs), and of the need to protect natural habitats from the impacts of adjacent developments.
However, actions to assist in the recovery of Gray’s Desert-parsley could negatively impact other species at risk if the actions result in excessive disturbance of the Gray’s Desert-parsley habitat (e.g., when removing invasive alien plants or installing fencing to exclude grazers). Any on-site activity has the potential to affect other species at risk through trampling or the inadvertent translocation of invasive alien plant seeds; therefore, care must be taken to avoid indirect impacts. If fire is identified as being a necessary component of the restoration of habitat at some locations where Gray’s Desert-parsley occurs, care must be taken to ensure that the natural disturbance is contained within a targeted area and the fire does not inadvertently promote the growth of an invasive alien plant species.
The potential for negative effects can be mitigated or eliminated at the project level phase through proper field procedures and/or strong collaboration with key conservation partners such as the Garry Oak Ecosystems Recovery Team and appropriate government agencies. Some recovery strategy activities may require project level environmental assessment under the Canadian Environmental Assessment Act. Any activities found to require project-level environmental assessments will be assessed at that time pursuant to the provisions of the Act.
|Scientific name||Common name||B. C. provincial rank**||COSEWIC status||SARA status||Location||Probability of being affected|
|Allium amplectens||Slimleaf Onion||S3||Not assessed||Not assessed||Mount Maxwell Maxwell Point||Possible|
|Callophrys mossii mossii||Moss’ Elfin||S2S3||Not assessed||Not assessed||Mount Maxwell Maxwell Point||Unlikely|
|Clarkia purpurea ssp. quadrivulnera||Small-flowered Godetia||S1||Upcoming assessment||Not assessed||Mount Maxwell Maxwell Point||Unlikely|
|Entosthodon fascicularis||Banded Cord-moss||S2S3||Special Concern||Special Concern||Mount Maxwell Maxwell Point||Unlikely|
|Erynnis propertius||Propertius Duskywing||S2S3||Not assessed||Not assessed||Mount Maxwell Maxwell Point Galiano Island||Unlikely|
|Idahoa scapigera||Scalepod||S2||Not assessed||Not assessed||Mount Maxwell Maxwell Point||Possible|
|Lomatium dissectum var. dissectum||Fern-leaved Desert-parsley||S1||Not assessed||Not assessed||Mount Maxwell Maxwell Point||Possible|
|Plagiobothrys tenellus||Slender Popcornflower||S1||Threatened||Threatened||Galiano Island||Unlikely|
|Syntrichia laevipila||Twisted Oak Moss||S2S3||Special Concern||Special Concern||Mount Maxwell Maxwell Point||Unlikely|
|Viola praemorsa ssp. praemorsa||Yellow Montane Violet||S2||Endangered||Endangered||Mount Maxwell Maxwell Point||Unlikely|
|Yabea microcarpa||California Hedge-parsley||S1S2||Not assessed||Not assessed||Mount Maxwell Maxwell Point||Unlikely except possible at Maxwell Point.|
This recovery strategy benefits the environment by promoting the conservation and recovery of the Gray’s Desert-parsley, a natural component of biodiversity. Activities required to meet recovery objectives are unlikely to result in any important negative environmental effects, as they are limited to habitat rehabilitation, research activities, fostering stewardship, increasing public awareness, improving knowledge on habitat requirements and population threats, and conducting habitat/species mapping, inventory, and restoration. In addition, it is likely that habitat restoration for Gray’s Desert-parsley will benefit other co-occurring native species which occupy the same habitat.
In summary, the SEA process has concluded that this recovery strategy will likely have several positive effects on the environment and other species. There are no obvious adverse environmental effects anticipated with the implementation of this recovery strategy.
-  http://www.registrelep.gc.ca/default_e.cfm
-  COSEWIC (Committee on the Status of Endangered Wildlife in Canada)
-  Distribution is measured by the extent of occurrence (currently about 50km2) and area of occupancy (currently estimated at 2km2; COSEWIC 2008). If new populations are discovered, these baseline figures should be updated as required.
Priorityreflects the degree to which the approach contributes directly to the recovery of the species or is an essential precursor to an approach that contributes to the recovery of the species.
-  http://www.ec.gc.ca/dd-sd/default.asp?lang=En&n=F93CD795-1
- Date Modified: