Multi-species Action Plan for Gros Morne National Park of Canada
Species at Risk Act
Action Plan Series
Table of Contents
- Recommendation and Approval Statement
- Executive Summary
- 1. Context
- 2. Recovery Objectives and Measures
- 3. Critical Habitat
- 3.1 Identification of Critical Habitat for Piping Plover, melodus subspecies
- 3.2 Proposed Measures to Protect Critical Habitat
- 4. Evaluation of Socio-Economic Costs and of Benefits
- 5. Measuring Progress
- 6. References
- Appendix A: Effects on the Environment and Other Species
Parks Canada Agency. 2016. Multi-species Action Plan for Gros Morne National Park [Final Version]. Species at Risk Act Action Plan Series. Parks Canada Agency, Ottawa. iv + 19 pp.
For copies of the action plan, or for additional information on species at risk, including COSEWIC Status Reports, residence descriptions, recovery strategies, and other related recovery documents, please visit the SAR Public RegistryFootnote 1.
Cover illustration: Darroch Whitaker, Parks Canada © 2013
Également disponible en français sous le titre
« Plan d’action multi-visant des espèces dumultiples dans le parc national du Canada du Gros- Morne du Canada »
© Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment and Climate Change, 2016. All rights reserved.
Catalogue no. CW69-21/12-2016E-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 action plan. The Vice-president, Operations, Eastern Canada, upon recommendation of the relevant Field Unit Superintendent, hereby approves this document indicating that the relevant Species at Risk Act requirements related to action plan development have been fulfilled in accordance with the Act.
Superintendent, Western Newfoundland and Labrador Field Unit
Parks Canada Agency
Vice-president, Operations, Eastern Canada
Parks Canada Agency
The federal, provincial, and territorial government signatories under the Accord for the Protection of Species at Risk (1996)Footnote 2 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 action plans for species listed as Extirpated, Endangered, and Threatened for which recovery has been deemed feasible. They are also required to report on progress five years after the publication of the final document on the SAR Public Registry.
Under SARA, one or more action plan(s) provides the detailed recovery planning that supports the strategic direction set out in the recovery strategy for the species. The plan outlines what needs to be done to achieve the population and distribution objectives (previously referred to as recovery goals and objectives) identified in the recovery strategy, including the measures to be taken to address the threats and monitor the recovery of the species, as well as the proposed measures to protect critical habitat that has been identified for the species. The action plan also includes an evaluation of the socio-economic costs of the action plan and the benefits to be derived from its implementation. The action plan is considered one in a series of documents that are linked and should be taken into consideration together with the COSEWIC status report, the recovery strategy, and other action plans produced for these species.
The Minister responsible for the Parks Canada Agency (the Minister of the Environment and Climate Change) is the competent minister under SARA for the individuals, residences and critical habitat of listed species in Gros Morne National Park and has prepared this action plan to implement the recovery strategies, as per section 47 of SARA. To the extent possible, it has been prepared in cooperation with Environment and Climate Change Canada, Fisheries and Oceans Canada, the Province of Newfoundland and Labrador, the Qalipu Mi’kmaq First Nation Band, and the Miawpukek First Nation, as per section 48(1) of SARA.
Implementation of this action plan is subject to appropriations, priorities, and budgetary constraints of Parks Canada and other participating jurisdictions and organizations.
Thanks are extended to the Qalipu Mi’kmaq First Nation Band, the Miawpukek First Nation, Environment Canada, and the Newfoundland and Labrador Department of Environment and Conservation for reviewing a draft of this action plan. Parks Canada would also like to thank Natureserve Canada and the Atlantic Canada Conservation Data Centre for providing data and information used in assessing the status of species in Gros Morne National Park.
The Multi-species Action Plan for Gros Morne National Park of Canada applies to lands and waters occurring within the boundaries of Gros Morne National Park of Canada (GMNP). The plan meets the requirements for action plans set out in the Species At Risk Act (SARA s.47) for species requiring an action plan and that regularly occur in these sites. Measures described in this plan will also provide benefits for other species of conservation concern that regularly occur at GMNP.
Where it has been determined that the sites can conduct management activities to help recover and/or manage a species, site-specific objectives are identified in this plan and represent the site’s contribution to objectives presented in federal recovery strategies and management plans. Species at risk, their residences, and their habitat are protected by existing regulations and management regimes in national parks and national historic sites as well as by SARA. Additional measures that will contribute to the survival and recovery of the species at the sites are described in this plan. These measures were identified based on threats and actions outlined in federal and provincial status assessments and recovery documents, as well as knowledge of the status and needs of each species at each site. Population monitoring measures are also identified for the species for which management activities at the sites can contribute to recovery.
Critical habitat in Gros Morne National Park was identified in the Recovery Strategies for Piping Plover and American Marten, and Parks Canada has legally protected these parcels of critical habitat. Piping plovers began nesting at Western Brook Beach in Gros Morne National Park in 2012, and this site is identified as critical habitat in this action plan. Additional measures to protect critical habitat in the Park are presented in this action plan.
Measures proposed in this action plan will have limited socio-economic impact and place no restrictions on land use outside of Gros Morne National Park. Indirect costs are expected to be minimal, while benefits will include positive impacts on park ecological integrity, enhanced visitor opportunities, greater awareness and appreciation of the value of biodiversity to Canadians, and opportunities for engagement of local communities and Aboriginal groups.
Gros Morne National Park of Canada (hereafter Gros Morne National Park, the Park or GMNP) was established in 1973 and protects 1,805 km² of the Great Northern Peninsula of Newfoundland (Figure 1). The Park was established to protect representative examples of the Western Newfoundland Highlands and St. Lawrence Lowlands natural regions. It is characterized by complex relief including large areas of coastal plain, deep fiords and valleys created by glaciation, steep slopes that rise from sea level to elevations exceeding 700 m, and the Long Range Plateau. Boreal forest dominated by Balsam Fir and Black Spruce covers 44% of the Park, while Arctic-alpine habitat and barrens (35%), wetland (11%) and fresh water (9%) ecosystems are also important. Most of the western boundary of the park extends to the low tide line and spans a 60 km section of the Gulf of St. Lawrence coast. Eight communities located in enclaves within or adjacent to the Park are home to approximately 4,000 people. In 1987 the Park was designated as a UNESCO World Heritage Site in recognition of its exceptional natural beauty and outstanding examples of major stages in the Earth’s geological evolution.
Maintenance and restoration of ecological integrity is the first priority of national parks (Canada National Parks Act (CNPA) s.8(2)). Species at risk, their residences, and their habitat are therefore protected in Canada’s national parks by existing national park regulations and management regimes as well as by SARA. In addition, the Species at Risk Act (SARA) prohibitions protecting individuals and residences apply automatically when a species is listed, and all critical habitat in national parks must be legally protected within 180 days of being identified.
Recovery measures for species at risk will be integrated within the framework of Parks Canada’s ongoing ecological integrity programs. National parks maintain comprehensive, scientifically rigorous ecological integrity monitoring and restoration programs that are organized according to the major ecosystems present in the Park. The recovery measures described in this action plan are therefore organized in the same manner. Parks Canada’s ecological integrity programs make contributions to the recovery of species at risk by providing inventory and monitoring data, and through the implementation of habitat restoration projects and other conservation action on the ground. The species-directed measures outlined in this plan will in turn contribute to maintaining and improving the ecological integrity of Gros Morne National Park by improving the conservation status of native species and their habitat. Species at risk information will also be integrated into the Park’s comprehensive visitor experience, education and outreach programs, helping to improve awareness, appreciation, and support for recovery efforts in Gros Morne National Park and beyond.
A number of federal and provincial recovery strategies and plans, management plans, and action plans have been prepared for species considered in this action plan. Along with status assessments, those documents provide guidance for the recovery of individual species, including strategic directions, recovery objectives, critical habitat, and threats. This action plan was developed and will be implemented in a manner that is consistent with those recovery documents, and should be viewed as part of this body of linked strategies and plans.
1.1 Scope of the Action Plan
The geographic scope of this action plan includes all lands and waters within the boundary of Gros Morne National Park, as described in Schedule 1 of the CNPA (Figure 1). This multi-species action plan has been written specifically for Gros Morne National Park because the Parks Canada Agency (PCA) is legally responsible for species at risk on PCA lands, has the ability to take direct conservation action, and deals with different threats, legislation, and management priorities than areas outside the Park.
Figure 1. Geographic scope for the Multi-species Action Plan for Gros Morne National Park of Canada. The park is located in western Newfoundland and includes lands and waters totaling 1,805 km².
This action plan addresses SARA-listed species that regularly occur in GMNP which require an action plan under SARA (s.47), as well as other species of conservation concern (Table 1). This approach both responds to the legislated requirements of the SARA and provides the Parks Canada Agency with a comprehensive plan for species conservation and recovery at these sites. The plan will be amended as required to meet SARA requirements for action planning.
Table 1. Species included in the Multi-species Action Plan for Gros Morne National Park.
|Species||Scientific Name||COSEWIC Assessment||SARA Status||Provincial Status|
|American Eel||Anguilla rostrata||Threatened||Not listed||Vulnerable|
|Bucephala islandica||Special Concern||Special Concern||Vulnerable|
|Catharus mimimus||Not assessed||Not listed||Threatened|
|Histrionicus histrionicus||Special Concern||Special Concern||Vulnerable|
|Little Brown Myotis||Myotis lucifugus||Endangered||Endangered||Not listed|
|Mountain Fern||Thelypteris quelpaertensis||Not assessed||Not listed||Vulnerable|
|Northern Myotis||Myotis septentrionalis||Endangered||Endangered||Not listed|
|Olive-sided Flycatcher||Contopus cooperi||Threatened||Threatened||Threatened|
|Rusty Blackbird||Euphagus carolinus||Special Concern||Special Concern||Vulnerable|
|Short-eared Owl||Asio flammeus||Special Concern||Special Concern||Vulnerable|
2. Recovery Objectives and Measures
The opportunity for Parks Canada to undertake management actions at Gros Morne National Park that will contribute to the local and national recovery of each species was assessed. Park-specific population and distribution objectives have been developed to identify the contribution that the Park can make towards achieving the national objectives presented in national recovery strategies and management plans (Table 2). Because they are directly linked to population and distribution objectives, monitoring activities are reported in Table 2 rather than in the table of recovery measures (Table 3). In some cases the opportunity for Gros Morne National Park to contribute to the recovery of a species will be relatively small, for example due to the distribution of the species in Canada or because the primary threats it faces occur outside the Park. In these cases site-specific objectives and conservation actions may be limited to protection measures in place under the CNPA and SARA, population monitoring, and habitat maintenance and restoration through the existing park management regime.
|National objectives (from recovery strategy or management plan)Table 2 note 1||Population & Distribution objectives for GMNP (contribution to national goal)||Trend in GMNP over last 5 years (2008–2013)||Population monitoringTable 2 note 2||General Information and Broad Park Approach|
|Piping Plover – melodus|
|(1) Maintain at least 255 pairs in Atlantic Canada, increasing to 310 pairs over time;|
(2) fledge at least 1.65 chicks per pair
|Maintain productivity of 1.65 chicks per pair per year, calculated as a 5 year running average||Unknown: Population zero 1975–2008, 1-2 pairs 2009-2013; productivity 1.67 fledglings per pair per year (2009–2013)||Suitable habitat is surveyed each spring; once a pair is found productivity is monitored following Parks Canada's Piping Plover monitoring protocol||Mitigate disturbance of breeding pairs, which is identified as a high-level threat (Environment Canada 2012b). Each spring all suitable breeding habitat is surveyed and when a nesting pair is observed the section of beach is closed to the public until chicks are 28 days old. Interpretive panels and signage are used to promote compliance with beach regulations (e.g., dogs on leash) and, when closures occur, to redirect visitors to open beaches.|
|American Marten – Newfoundland population|
|(1) Increase the wild population to establish a stable & self-sustaining population|
(2) Maintain existing populations & establish in adjacent areas where the potential for occupancy is high
|Short term goal: Maintain occupancy of potential marten habitat at current level.|
Long term goal: Maintain or increase occupancy of potential marten habitat
|Increasing: Population of marten in GMNP presumed extirpated through 1990s, estimated as <5 in 2001–2002 and 15–20 in 2012||Monitoring will consist of presence (occupancy) detection in suitable habitat units using winter track transects supplemented with observations obtained through hair trapping, incidental sightings and citizen science monitoring||Key threats are incidental mortality from snaring and trapping and habitat loss and degradation (Environment Canada 2013b). These are relevant in GMNP because residents are permitted to snare Snowshoe Hare and because overbrowsing by moose may have led to habitat degradation.|
|Red Crossbill – percna|
|Interim goal: to restore species to a self-sustaining population level able to withstand stochastic events||No objective established: though occasionally observed this species is not known to regularly occur in GMNP||Red Crossbill has not been observed in GMNP during the past 5 years||Continue winter bird surveys under the Park ecological integrity monitoring program (includes broadcast of Red Crossbill vocalizations)||Red Crossbill are transient breeders and may never have been common in GMNP; Focus on monitoring (Environment Canada 2012a) unless and until a population is identified in GMNP.|
|Red Knot – rufa|
|Not applicable (Recovery Strategy not posted at time of writing)||No objective established: low numbers pass through GMNP on migration, so park is of limited importance to the species' national recovery||Unknown: stopover site identified in 2010 and has been monitored since; Possibly declining due to population-wide trend||Monitor Belldowns Point stopover site during fall migration using Environment Canada’s Atlantic Canada Shorebird Survey protocol||Belldowns Point was recently identified as a stopover site (August to October). Disturbance at stopovers is considered a low-level threat (Garland and Thomas 2009) that can be mitigated through compliance with existing park regulations (dogs on leash, ATV prohibitions, etc.).|
|Not applicable (Recovery Strategy not posted at time of writing)||No objective established: no threats known in park and GMNP is of limited importance to the species' national recovery||Unknown; species still widespread in park||Opportu-|
nistically record observations and any changes to the status of species in GMNP
|Breeds in forests throughout GMNP; continue to protect and maintain habitat.|
|Barrow's Goldeneye - eastern pop.|
|From Management Plan: (1) Maintain and or increase population size & range. (2) Maintain ≥6,800 individuals over next 10 years.||No objective established: Status in GMNP uncertain though park is likely of limited importance to the species' national recovery||Unknown; small numbers winter along coast each year; breeding status unknown||Opportu-|
nistically record observations and any changes to the status of species in GMNP
|Barrow's Goldeneye may breed in the highlands of GMNP (Environment Canada 2013a); focus is on clarifying breeding status in GMNP.|
|Harlequin Duck - eastern pop.|
|From Management Plan: Increase winter population to 3,000 including ≥1,000 breeding-aged females in 3 out of 5 years||No objective established: no threats known in park and GMNP is of limited importance to the species' national recovery||Stable based on regular surveys since 1997||Continue Harlequin Duck population size and productivity surveys at 5-year intervals under the GMNP ecological integrity monitoring program||Existing park management regime appears to be sufficient; continue to protect and maintain habitat to support current population (Environment Canada 2007).|
|Not applicable (Management Plan not posted at time of writing)||No objective established: no threats known in park and GMNP is of limited importance to the species' national recovery||Unknown||Opportu-|
nistically record observations and any changes to the status of species in GMNP
|Continue to protect and maintain habitat .|
|Not applicable (Management Plan not posted at time of writing)||Unknown||Opportu-|
nistically record observations and any changes to the status of species in GMNP
|Occasionally breeds in the park; continue to protect and maintain habitat (Schmelzer 2005).|
|Little Brown Myotis|
|Not applicable (Recovery Strategy not posted at time of writing)||Unknown||Complete inventory initiated in 2013; develop protocol to monitor trends in occurrence and activity levels||Status in GMNP poorly understood; immediate need is baseline data on distribution and relative abundance, as well as protection of any roosts in park buildings. Measures related to white nose syndrome will be considered if hibernacula are found in GMNP.|
|Not applicable (Recovery Strategy not posted at time of writing)||Unknown||Complete inventory initiated in 2013; develop protocol to monitor trends in occurrence and activity levels||Status of in GMNP poorly understood; immediate need is baseline data on distribution and relative abundance, as well as protection of any roosts in park buildings. Measures related to white nose syndrome will be considered if hibernacula are found in GMNP.|
|Not applicable||No objective established: no threats known in park and species is not listed under SARA||Unknown; was stable based on 2002/2004 surveys||Conduct monitoring as described in the 2011 NL Management Plan (5 subplots every 5 years, complete census every 10 years; Wildlife Division 2011)||Continue to protect and maintain habitat to support current population; monitor population periodically to meet stewardship responsibility.|
|Not applicable||No objective established: no major threats known in park and GMNP is of limited importance to the species' national recovery||Unknown||Monitor occurrence and relative abundance of adult eels in major watersheds of GMNP||Distribution and abundance in GMNP poorly understood and needs clarification; Continue to protect and maintain habitat; opportu-|
nistically remediate impassable culverts during road maintenance (Wildlife Division 2010a)
|Gray-cheeked Thrush - Nfld pop.|
|Not applicable||No objective established: this species is not listed under SARA and status in GMNP poorly understood||Unknown; has declined in GMNP since 1970s (SSAC 2010)||Opportu-|
nistically record sightings and any changes to the status of species in GMNP
|Continue to protect and maintain habitat; Given the dearth of information GMNP should support research where possible (Wildlife Division 2010b)|
Table 2 notes
- Table 2 note 1
National objectives from recovery strategies or management plans available on or before April 7, 2014.
- Table 2 note 2
Where population and distribution objectives have been established for GMNP, monitoring is designed to directly measure success in achieving those goals; otherwise baseline population monitoring efforts necessary for park stewardship, management and reporting are described.
2.1 Measures to be Taken and Implementation Schedule
Measures that are proposed to achieve the site-based population and distribution objectives, along with any measures required to protect the species and to learn more about them, are presented in Table 3. For each measure, timelines, targets, and desired outcomes were established, and the approach by which progress will be measured was determined.
In addition to the implementation of conservation measures that contribute to species recovery, Parks Canada has an important role in promoting awareness and appreciation of species at risk. Providing opportunities for the public to learn about and experience national parks is a central component of Parks Canada’s mandate. Thus national parks afford an opportunity and an imperative for engaging the public in species at risk recovery, so a suite of public outreach, education, and visitor activities was developed as part of the action planning process (Table 4). These will engage audiences using a broad range of approaches and levels of participation, including passive media such as interpretive panels and print publications, interactive outlets such as public events and on-demand electronic information, and hands-on activities where the public can participate in monitoring or recovery.
|Species||Measure number||Measure description||Desired outcome||How will progress toward the outcome be measured?||Threat or recovery measure addressed||Timeline|
|Piping Plover||1||Reduce human disturbance of breeding plovers: Take steps to reduce disturbance of breeding plovers, including use of interpretive panels and signage to promote compliance with disturbance mitigation measures (e.g. dogs on leash) and, if warranted, area closures in the vicinity of nests coupled with signage to redirect visitors to nearby open beaches||Annual productivity is ≥1.65 chicks per pair per year (calculated as a 5 year running average)||Each year productivity of each plover pair is monitored following Parks Canada's Piping Plover monitoring protocol||Reduce human disturbance of breeding pairs (Environment Canada 2012b)||Ongoing|
|Red Knot||2||Visitor awareness about shorebird stopovers: Install interpretive panels and signage at Belldown's Point and other stopover sites identified in future||Information on site importance to shorebirds and park regulations is available to visitors to stopover sites to encourage compliance and minimize human disturbance||Appropriate information panels and signage is in place at stopover sites and maintained through time||Reduce human disturbance at stopover sites (a low-level threat in GMNP; see also Garland and Thomas 2009)||Ongoing|
|American Marten||3||Snaring Regulations: Develop initiatives to promote compliance with brass / picture cord snare wire regulations in GMNP and adjacent areas||No stainless steel snare wire is used in GMNP||Compliance is monitored by field staff & park wardens||Reduce risk of incidental mortality during snowshoe hare snaring (high level threat; Environment Canada 2013)||Ongoing|
|American Marten||4||Habitat Mapping: update GIS land cover maps for GMNP, then, in conjunction with island-wide efforts, use updated classification to map suitable and critical habitat for marten||Marten habitat in GMNP is mapped by 2015||(1) Updated GIS landcover data is available by 2015|
(2) Map of suitable marten habitat is produced by 2016
|Map critical habitat and other suitable habitat throughout GMNP||2016|
|American Marten||5||Moose population management: Reduce moose populations and maintain them at the target density of 1-2 moose/ km²||Moose population density is reduced by 2018 and is maintained at between 1 and 2 moose/km-sq by 2023||Aircraft-based moose population surveys conducted at 5 year intervals||Habitat loss and degradation (Parks Canada 2011, Environment Canada 2013b)||Ongoing|
|Little Brown Myotis & Northern Myotis||6||Bat Inventory: assess distribution and relative abundance of bats in GMNP using digital ultrasonic activity recorders||The distribution and relative abundance of bat species in GMNP is understood and a long-term bat monitoring protocol developed by 2016||Data on the activity levels of bats, assessed by recording species-specific rates of calling, will be available and an associated report and monitoring protocol is available||Clarify population status in GMNP||2013–2016|
|Little Brown Myotis||7||Bat Best Management Practices: Develop and implement BMPs for maintenance of infrastructure used by roosting bats||Bat BMPs are available and in use by 2016||BMPs are available by Spring 2016||Protection of individuals and residences||2016|
|Barrow's Goldeneye||8||Breeding status of Barrow’s Goldeneye: Monitor use of nest boxes by Barrow's Goldeneye||Breeding status in GMNP is clarified by 2018||12 boxes were deployed in 2013; data and a report on occupancy of nest boxes by Barrow’s Goldeneye from 2014–2018 will be available||Clarify breeding status in GMNP (medium priority research need; Environment Canada 2013a)||As resources allow|
|American Eel||9||Mitigate barriers to fish passage: Implement BMPs for fish passage at road crossings when culverts are replaced during road maintenance||All new / replaced culverts in GMNP are passable to eels||Assessment of proportion of culverts that are passable to fish following installation or replacement||Loss of freshwater habitat due to anthropo-|
genic barriers (Wildlife Division 2010a)
|MeasureTable 4 note 1||Measure number||Desired outcome||Proposed MeasuresTable 4 note 2||How will progress toward the outcome be measured?|
|Develop & implement media strategy||1||At least one media story highlighting species at risk in GMNP each year|
|Contribute to in-park school programming||2||School students in region are aware of species at risk conservation in GMNP|
|Incorporate species at risk monitoring and recovery into visitor experience opportunities||3||Foster connection to place by incorporating species-at-risk content into visitor experience opportunities|
|Provide species at risk information throughout park||4||Park visitors learn about species at risk through a diverse suite of non-personal media (e.g., interpretive panels, website content, social media platforms, visitor guide)|
Table 4 notes
- Table 4 note 1
All measures will be implemented on an annual, ongoing basis and apply to all species at risk occurring in the Park.
- Table 4 note 2
Actual measures may vary from year-to-year based on available resources, opportunities, and emerging program needs.
3. Critical Habitat
Critical habitat is “the habitat that is necessary for the survival or recovery of a listed wildlife species and that is identified as the species’ critical habitat in the recovery strategy or in an action plan for the species” (SARA s.2(1)). Critical habitat is identified in this action plan to the extent possible for species for which i) a recovery strategy has been posted on the SARA public registry, ii) the recovery strategy does not identify all critical habitat required to meet the population and distribution objectives, and iii) there is sufficient information available to identify critical habitat in the Park (Table 5).
|Species||Is critical habitat identified in the recovery strategy?||Is critical habitat identification complete?||Is critical habitat identified in this action plan?|
|Piping plover, melodus subsp.||Yes, in GMNP and elsewhere||Yes, critical habitat is fully identified in the recovery strategy. However, as the population objectives have not been met additional critical habitat will be identified if new sites having suitable habitat are occupied by nesting pairs||Yes, Piping Plovers nested on Western Brook Beach in 2012 & 2013, making this site critical habitat based on the identification criteria in the recovery strategy|
|American Marten, Newfoundland population||Yes, in GMNP and elsewhere||No, the critical habitat identified in the recovery strategy is not sufficient to meet national population and distribution objectives||No, no new information exists with which to identify additional critical habitat in this action plan. The Schedule of Studies outlined in the recovery strategy is ongoing|
|Red Crossbill, percna subsp.||No||No, critical habitat has not been identified||No, sufficient information is not available to identify critical habitat. The schedule of studies in the recovery strategy and action plan is ongoing|
Critical habitat has been identified in Gros Morne National Park in SARA recovery strategies for American Marten and Piping Plover. This includes 3 parcels of American Marten critical habitat along the western boundary of the Park, which total 5,380 ha (Environment Canada 2013b), and one parcel of Piping Plover critical habitat at Shallow Bay Beach (Environment Canada 2012b). SARA prohibitions protecting these parcels of marten and plover critical habitat have been enabled by publication of descriptions of the habitat in the Canada Gazette. This action plan identifies one new parcel of Piping Plover critical habitat at Western Brook Beach. As of April 2014 it is not possible to identify additional critical habitat in the Park. Any data or information received after that date was not considered for this action plan but will be considered for critical habitat identification in the future. Where critical habitat identification is not complete it will be identified in an upcoming or revised action plan or updated recovery strategy; refer to the schedule of studies in the marten and crossbill recovery strategies for further detail (Environment Canada 2012a, 2013b).
3.1 Identification of Critical Habitat for Piping Plover, melodus subspecies
3.1.1 Geographic Location
The beach at the mouth of Western Brook (Latitude 49.826° N, Longitude 57.860° W; NTS map 12 H/13, Edition 3 ) is identified as critical habitat for Piping Plovers. Critical habitat is bounded to the north by Western Brook; to the south by the northeast boundary of an inholding of private and provincial land, as described in the park boundary survey (Canada Lands Survey Record 69288; see Detail J [Western Brook Fish Landing and Staging Area]); elsewhere the boundary is based on the biophysical attributes provided below. Shorelines on the north side of Western Brook and to the south of the critical habitat, including the inholding of private and provincial land, do not contain the appropriate biophysical attributes and are not identified as critical habitat.
3.1.2 Biophysical Attributes
The biophysical attributes of Western Brook Beach are consistent with the critical habitat identified in the recovery strategy (Environment Canada 2012):
Suitable habitat occurs in areas of early successional habitat characterized by a lack of dense vegetation on wide sand, gravel, or cobble beaches, sandspits, or peninsulas in marine coastal areas. Within these areas, suitable habitat is the area of the coastal zone extending from the low water mark and intertidal zone, up to the crest or peak of the vegetated dune (typically identified by the presence of marram/beach grass or other dune vegetation), and roughly approximated by the following habitat attributes: gently sloping foredunes; beach widths that afford protection from flooding at normal high tides; substrates of sand, gravel or cobble, or some combination of these; and foredunes that are either sparsely vegetated or relatively free of vegetation.
Critical habitat includes the entire area of suitable habitat including the intertidal zone from the low water mark, sand or mud flats and upper beach that normally include dune vegetation up to the crest or peak of the vegetated dune. Breaches that cross from the ocean to bays, low back shores, landward extensions of washovers, washover fans, sand fans, and river outlets are considered extensions of the beach habitat and therefore are critical habitat. When a distinct dune crest does not exist (i.e. where a dune is not present), the landward boundary of critical habitat extends to the line of permanent non-beach vegetation (e.g. marsh or bog vegetation, shrubs, trees, farmland) or another permanent physical structure (e.g. road, bridge, culvert, river).
3.1.3 Examples of activities likely to result in destruction of Piping Plover critical habitat in Gros Morne National Park
Any anthropogenic activity which alters or disturbs the key habitat attributes described in section 1.3.1 above is considered an activity likely to result in the destruction of Piping Plover critical habitat. Also, any activity that reduces access to habitat by plovers or reduces the functionality of habitat for plovers is considered a destruction of critical habitat. Examples of activities which are likely to result in the destruction of Piping Plover critical habitat in Gros Morne National Park include:
- off-road, all-terrain, or motorized vehicle use;
- coastal development occurring in plover habitat or in other habitats closely associated with plover habitat, including construction of cottages, homes, or tourist accommodations, boardwalks, and trails;
- beach nourishment;
- beach stabilization;
- sand mining and extraction;
- beach cleaning or raking activities that remove elements of natural habitat; and
- deliberate or accidental discharge of oil and toxic chemicals.
3.2 Proposed Measures to Protect Critical Habitat
Critical habitat identified in this and other recovery documents within Gros Morne National Park of Canada is legally protected from destruction under section 58(1) of the SARA.
4. Evaluation of Socio-Economic Costs and of Benefits
The Species at Risk Act requires the responsible federal minister to undertake “an evaluation of the socio-economic costs of the action plan and the benefits to be derived from its implementation”.
The cost of implementing this plan will be low and will be borne by Parks Canada. Many of the proposed measures will be integrated into the operational management of Gros Morne National Park and there will be few new costs. These costs to Government will be covered by reallocation of existing funds so will not result in additional costs to society.
No major socio-economic costs to park visitors, partners, stakeholders or Aboriginal groups are expected as a result of this action plan. The action plan applies only to lands and waters in Gros Morne National Park, and does not bring any restrictions to land use outside the Park. While minor restrictions may be placed on visitor activities on park lands and waters to protect and recover species at risk, implementation of this plan is expected to have an overall net benefit to visitor opportunities.
Measures presented in this action plan for Gros Morne National Park will contribute to meeting recovery strategy objectives for three species. For American Marten (Newfoundland population), this action plan will contribute to increasing the wild population and allow it to expand its range into currently unoccupied habitat. For Piping Plover (melodus subspecies) this plan will contribute to breeding productivity. For Red Crossbill (percna subspecies) this plan will help safeguard potential habitat from degradation by non-native moose and will support population monitoring objectives. This plan will also benefit other species of conservation concern that are found in Gros Morne National Park, including Red Knot (rufa subspecies), Barrow’s Goldeneye (eastern Population), Little Brown Myotis, Northern Myotis, and American Eel.
These measures are expected to have an overall positive impact on the ecological integrity of Gros Morne National Park, for example through improvements to forest health, and to enhance opportunities for appreciation of the Park and the species by visitors and the general public. This action plan includes measures which could result in benefits to Canadians, such as positive impacts on biodiversity and the value individuals place on preserving biodiversity, as well as protection and enhancement of ecosystem services such as maintenance of fuelwood resources for domestic timber harvesters. The proposed measures seek a balanced approach to reducing or eliminating threats to species at risk populations and habitats, and include protection of individuals and their habitat, potential species re-establishment, and increasing public awareness and stewardship.
Potential economic benefits of the recovery of the species at risk found in Gros Morne National Park cannot be easily quantified, as many of the values derived from wildlife are non-market commodities that are difficult to appraise in financial terms. Wildlife, in all its forms, has value in and of itself, and is valued by Canadians for aesthetic, cultural, spiritual, recreational, educational, historical, economic, medical, ecological and scientific reasons. The conservation of wildlife at risk is an important component of the Government of Canada’s commitment to conserving biological diversity, and is important to Canada’s current and future economic and natural wealth.
Implementing this action plan is expected to have benefits for park visitors, local residents and Aboriginal groups. These include opportunities to learn about and take part in the recovery of culturally important species at risk, opportunities for Aboriginal groups to become involved in conservation issues in the Park, and greater awareness of Aboriginal values and culture in the region. Benefits and opportunities for involvement should be relatively evenly distributed across Aboriginal and non-Aboriginal members of local communities and will be available to all park visitors.
5. Measuring Progress
Reporting on implementation of this action plan (under s. 55 of SARA) will be done by assessing progress towards implementing the measures presented in Tables 3 and 4.
Reporting on the ecological impacts of the action plan will be done by assessing progress towards meeting the site-based population and distribution objectives presented in Table 2.
Environment Canada. 2006. Recovery Strategy for the Red Crossbill, percna subspecies (Loxia curvirostra percna), in Canada. Species at Risk Act Recovery Strategy Series. Environment Canada, Ottawa, vii + 29 pp.
Environment Canada. 2007. Management Plan for the Harlequin Duck (Histrionicus histrionicus) Eastern Population, in Atlantic Canada and Québec. Species at Risk Act Management Plan Series. Environment Canada. Ottawa. vii + 32 pp.
Environment Canada. 2011. Atlantic Canada Piping Plover Conservation Guidance Manual. Internal Canadian Wildlife Service Report Series May 2011. Canadian Wildlife Service, Atlantic Region. 64 pp.
Environment Canada. 2012a. Action Plan for the Red Crossbill, percna subspecies (Loxia curvirostra percna) in Canada. Species at Risk Act Action Plan Series. Environment Canada, Ottawa. iii + 21 pp.
Environment Canada. 2012b. Recovery Strategy for the Piping Plover (Charadrius melodus melodus) in Canada. Species at Risk Act Recovery Strategy Series. Environment Canada, Ottawa, v + 29 pp.
Environment Canada. 2013a. Management Plan for the Barrow’s Goldeneye (Bucephala islandica), Eastern Population, in Canada. Species at Risk Act Management Plan Series. Environment Canada, Ottawa. iv + 16 pages.
Environment Canada. 2013b. Recovery Strategy for the American Marten (Martes americana atrata), Newfoundland population, in Canada. Species at Risk Act Recovery Strategy Series. Environment Canada, Ottawa, xi pp. + appendix.
Garland, S. and P. Thomas. 2009. Recovery Plan for Red Knot, rufa subspecies (Calidris canutus rufa), in Newfoundland and Labrador. Wildlife Division, Department of Environment and Conservation, Government of Newfoundland and Labrador, Corner Brook, NL. iv + 12 pp.
Parks Canada, 2009. Gros Morne National Park of Canada Management Plan. Parks Canada, Rocky Harbour, NL. xii + 61 pages.
Parks Canada, 2011. Hyperabundant moose management plan for Gros Morne National Park. Parks Canada, Rocky Harbour, NL.
Schmelzer, I. 2005. A management plan for the Short-eared owl (Asio flammeus flammeus) in Newfoundland and Labrador. Wildlife Division, Department of Environment and Conservation. Corner Brook, NL.
SSAC 2010. The status of Gray-cheeked Thrush (Catharus minimus) in Newfoundland and Labrador. Newfoundland and Labrador Species Status Advisory Committee, Report No. 24.
Wildlife Division. 2010a. Management Plan for the American Eel (Anguilla rostrata) in Newfoundland and Labrador. Department of Environment and Conservation, Government of Newfoundland and Labrador, Corner Brook. Canada. v + 29 pp.
Wildlife Division. 2010b. Management Plan for the Gray-cheeked Thrush (Catharus minimus) in Newfoundland and Labrador. Department of Environment and Conservation, Government of Newfoundland and Labrador, Corner Brook, Canada. iii + 19 pp.
Wildlife Division. 2011. Management Plan for the Mountain Fern (Thelypteris quelpaertensis) in Newfoundland and Labrador. Wildlife Division, Department of Environment and Conservation, Government of Newfoundland and Labrador, Corner Brook, Canada. iii + 14 pp.
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 achievement of any of the Federal Sustainable Development Strategy’sFootnote 3 (FSDS) goals and targets.
Recovery planning is intended to benefit species at risk and biodiversity in general. However, it is recognized that recovery measures may also inadvertently lead to environmental effects beyond the intended benefits. The planning process, which is based on national guidelines, directly incorporates consideration of all environmental effects, with a particular focus on possible impacts on non-target species or habitats. The results of the SEA are incorporated directly into the plan itself, and are summarized below.
Overall, it is anticipated that implementation of this action plan will have a beneficial impact on non-target species, ecological processes, and the environment in Gros Morne National Park. This plan puts into practice measures presented in recovery strategies for Piping Plover (melodus subspecies), American Marten (Newfoundland population), and Red Crossbill (percna subspecies), all of which were subject to SEAs during the development of those documents (Environment Canada 2006, 2012b, 2013b). Further, this action plan was developed to benefit all species at risk that regularly occur in Gros Morne National Park. Consequently all of these species were considered in the planning process, any potential secondary effects were evaluated and mitigated, and, where appropriate, measures were designed to benefit multiple species. The planning process was also guided by priorities identified in the Park’s ecological integrity monitoring program, the Park’s management plan (Parks Canada 2009), and the Park’s hyperabundant species management plan (Parks Canada 2011). As a result, measures outlined in this plan address key management priorities aimed at improving the broader ecological health of the Park. This includes improvement of forest health though moose management, as well as mitigation of existing and anticipated environmental impacts such as the restoration of stream connectivity in the Park. Finally, this plan outlines stewardship actions, educational programs, and awareness initiatives involving park visitors, local residents, Aboriginal organizations, and the general public. This will lead to greater appreciation, understanding, and action towards the conservation and recovery of species at risk in general.
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