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Spoon-leaved Moss (Bryoandersonia Illecebra)
Description of the species
Spoon-leaved Moss (Bryoandersonia illecebra), of the family Brachythecieaceae, is a shiny, green to greenish yellow-brown species of moss with creeping stems and ascending, intertwined branches that form deep mats. It is quite large and striking compared to most moss species, making it relatively easy to find and identify in the field. Its most distinctive feature is the smoothly cylindrical ‘rat-tail’ appearance of its stems and branches (especially when they are dry). Upon very close examination of the stems and branches, one may discern closely overlapping, broad, concave (cupped, like the bowl of a spoon, with the dish opening toward the stem) leaves, up to 2.8 mm in length, covering all surfaces. The leaves narrow abruptly to short, twisted points. These characteristics help to distinguish the species from other large, branchy species of moss that overlap Spoon-leaved Moss in distribution. Some large Brachythecium species, for example, can grow in Spoon-leaved Moss habitat and range, but have more gradually narrowed, flatter, triangular leaves. Furthermore, Brachythecium species tend to taper at their branch tips, whereas Spoon-leaved Moss branches tend to be broad and blunt at their tips.
Throughout most of its range, Spoon-leaved Moss is dispersed as spores (13-17 μm in diameter - small in the range of bryophyte spore size), which are released from tiny (2-3 mm long) capsules, each held above the stems and branches on a rigid, brown, thread-like stalk. To date, however, sporophytes have not been documented in Canadian populations. Spoon-leaved Moss is dioicous, meaning that there are separate male and female plants (the term ‘dioicous’ for bryophytes differs from ‘dioecious’, which applies to vascular plants, reflecting life history differences between the two groups). To date, only female plants have been documented in Ontario (COSEWIC 2003a). Spoon-leaved Moss has no known specialized asexual propagules, but vegetative reproduction through fragmentation is observed in most moss species (e.g. Cleavitt 2005).
Illustrations and more extensive technical descriptions of Spoon-leaved Moss may be found in Robinson (1962), Crum and Anderson (1981), and in COSEWIC (2003a).
Populations and distribution
Spoon-leaved Moss is endemic to eastern North America, where it is most common in the south-eastern United States. Its distribution pattern is typical of many eastern deciduous forest (Carolinian) plant species (e.g. Argus 1992). In the US, it is distributed from New York to Connecticut, Ohio, Indiana, Iowa, Florida, and Texas (Crum & Anderson 1981, Missouri Botanical Garden 2005, New York Botanical Garden 2005) (Figure 1). Within this relatively restricted world range, Spoon-leaved Moss is sufficiently abundant to be ranked G5 (April 1991), indicating that the global population (as well as the US population) is demonstrably secure (NatureServe 2002). The nearest Spoon-leaved Moss population was recorded in Erie, New York, in 1972, about 45 km from Ontario’s Niagara Region population (Missouri Botanical Garden 2005, New York Botanical Garden 2005). However, US populations are more typically located 400-500 km from the nearest Canadian population. N. Cleavitt (personal communication) has observed extensive populations in upstate New York.
Canadian populations of Spoon-leaved Moss are peripheral in the context of the species’ global distribution, in that they mark the species’ northern range limit. The full extent of the Canadian population is in Ontario, where it is ranked S1 (Ontario Natural Heritage Information Centre 2005). All documented locations are in the southern-most part of the province, near the north shore of Lake Erie (Figure 2, Table 1). Three extant populations, one in each of Essex County, Elgin County and Niagara Region (isolated stations separated by at least 170 km), were confirmed in 2002 in association with the COSEWIC (2003a) status report and subsequent designation (Figure 2, Table 1). Field work conducted by Gould (2005) added to the number of colonies known at the Essex and Elgin County sites (Table 1), but the Niagara Region population has not been re-surveyed. The total Canadian population is now estimated to consist of eleven colonies (all healthy in appearance) covering a combined total of about 20m2 (Table 1), which represents an increase of about 6.5 m2 over that reported by COSEWIC 2003a.
Four more populations documented in Elgin and Middlesex Counties within the past 50 years were not found in 2002 despite concerted effort (COSEWIC 2003a). The location of an historical collection made in 1925 (Table 1) cannot be pinpointed, but the record serves to demonstrate the long-term residence of the species in Canada. Another historical record from the Canadian Rocky Mountains has been discounted by recent authorities (Crum & Anderson 1981, New York Botanical Garden 2005, Robinson 1962). Given the global security of Spoon-leaved Moss and its rarity in Canada, Ontario’s population can be assumed to represent less than 1% of the species’ global distribution.
The fact that at least four populations that were recorded in the 1970’s and 80’s were not found in 2002 (COSEWIC 2003a, Table 1) may suggest a declining trend in the number of extant Canadian locations and number of mature individuals in the Canadian population (COSEWIC 2003b). However, a lack of data on the historical sizes and precise locations of ‘lost’ populations and low recent collecting effort in southern Ontario make it impossible to confirm either the existence or the magnitude of decline. Identifying preferred habitat conditions and re-surveying all examples of these conditions at historical locations would help to substantiate or refute the suggested decline. There have also been insufficient observations to characterize the dynamics of local abundance over time.
Spoon-leaved Moss is long-lived and evergreen, making generation time difficult to establish. It does not die at the end of the growing season, or (in areas where the species produces capsules) after successful reproduction. Instead, it continues to grow and produce new reproductive structures year after year. In Canada, where it is not known to reproduce sexually, generation time may be equal to the life span of a colony, which has not been researched. Records show that at least one (Essex County) and possibly two (whether the Elgin population represents a new or previously-recorded population cannot be confirmed) populations have persisted for over 20 years (Table 1), suggesting that it can occupy a site over the long term and is not given to dramatic natural population fluctuation / extirpation over the short term.
Figure 1. Approximate global distribution of the eastern North American endemic Spoon-leaved Moss (indicated by gray shading), from COSEWIC (2003a) (reproduced with permission from Environment Canada).
Figure 2. Collecting locations for Canadian specimens of Spoon-leaved Moss, from COSEWIC (2003a) (reproduced with permission from Environment Canada). Essex and Elgin populations observed in 2002 were confirmed to persist in 2004.
|Sex||Collector / Observer - Date||Total Abundance|
|Confirmed Extant Populations|
|Essex County (Ontario Parks)|
In moist, over-grown field (used for pasture until the mid 1900s) populated by successional cedar-hawthorn scrub and in more mature ash-maple woodland.
|M.J. Oldham - March 1982|
J. Doubt – August 2002
R. Gould & A. Woodliffe – December 2004
(7 colonies, %cover not recorded)
Elgin County (OMNR)
Original habitat description: On soil, roots and decaying branches on deciduous, wooded hillside.
Current habitat description: On clay hummocks and tree bases in a flat moist, regenerating (cleared until 1930s) scrub forest habitat, with broken canopy dominated by hawthorn, crab apple, white spruce, ash and maple habitats within surrounding mature hardwood plantation/forest; also in maturing moist ash-maple-hickory plantation forest.
W.G. Stewart - April 1983
J. Doubt – August 2002
R. Gould & A. Woodliffe – December 2004
Note: Some uncertainty surrounds the 1983 collection. Current observations may not reflect the original location (COSEWIC 2003a).
(1 colony, 90%cover)
(3 colonies, %cover not recorded)
Niagara Region, City of Niagara Falls
(Niagara Peninsula Conservation Authority)
On exposed and elevated (approx. 15 cm from forest floor) root of maple tree, near roadside, in deciduous swamp
|F||J. Doubt - August 2002|
(1 colony, 100% cover)
|Historically documented populations|
Elgin County, Aldborough Twp. (Private)
On sandy humus and litter in wet deciduous woodlot.
W.G. Stewart - April 15, 1973
J. Doubt – July 2001, August 2003
Elgin County, Yarmouth Twp.,(Private)
On soil over cedar roots along stream in swamp of marl and peat / On cedar stump in stream and under grasses on bank of stream
W.G. Stewart - April 1975
W.G. Stewart - May 1980
J. Doubt – July 2001
Elgin County, Southwold Twp., (Private)
On soil, roots and decaying branches on deciduous wooded hillside.
W.G. Stewart – April 1983
J. Doubt – August 2002
On the ground.
|U||T. Drummond -1925-1927|
(but sufficient for exsiccata)
|Canada. Rocky Mts.||U||A.R. Wallace||Unknown|
Description of the species’ needs
Ecological role, biological needs, and limiting factors
Spoon-leaved moss has no known specialized ecological role anywhere in its range. In general, mosses perform many of the same ecological functions as all plants do by cycling nutrients and fixing them to biologically-useful forms. Some specific ecological roles of mosses, such as those in revegetation, soil stabilization, and animal food / shelter have been reviewed by Longton (1984, 1992b) and Slack (1988).
The physiological needs of Spoon-leaved Moss have not been studied, and research is required to define its preferred growing conditions and its range of ecological tolerance. However, casual observations and inferences from other moss species give evidence of some biological needs and potentially limiting factors.
Overview of moss life cycle and terminology
Rain or flood water is required for the sperm of dioicous mosses such as Spoon-leaved Moss to swim to the eggs borne by female plants. The 10 cm maximum range of moss sperm (e.g. Longton 1976, Mishler 1988, Rohrer 1982, Schofield 1985) necessitates close proximity of male and female colonies. Mosses reproduce sexually to produce short-lived (usually several months) spore-bearing structures known as sporophytes that are attached to and dependent on the long-lived (usually many years) leafy green moss gametophytes. In the case of Spoon-leaved Moss, which has small spores and relatively long stalks elevating the spore capsules above the still ‘boundary-layer’ air near the gametophyte, air dispersal is likely (e.g. During 1997, Longton 1997).
Upon contact with a favourable substrate, spores germinate to produce delicate, unspecialized green filaments (protonemata) that are very sensitive to dessication (Wiklund & Rydin 2004). Acidity, such as might be imposed by acid rain or other pollutants, impairs germination, extending this vulnerable period (Wiklund & Rydin 2004). Protonemata, in turn, develop into gametophytes possessing specialized features (including those that botanists use to identify moss species) that allow them to exploit their preferred habitat. Alternatively, air- or flood water- dispersed asexual diaspores may initiate protonemata or sprout directly as new gametophytes. Even as mature gametophytes, mosses are relatively unprotected from their environments. Leaves generally possess no cuticle or epidermal layers; often taking up water and nutrients (and pollutants) directly from all exposed surfaces.
The Spoon-leaved Moss continues to branch and grow until it exhausts the available space or resources. The proliferation of stems and branches forms moss colonies, or patches. Within colonies, stems and branches are intertwined and difficult to separate. They may break in response to disturbance to form multiple (possibly genetically identical) colonies or they may expand and merge with adjacent colonies. For these reasons, it can be difficult to define a moss ‘individual’, and several measures (number of colonies, distribution of colonies, colony dimensions, percent cover occupied by moss within each colony) are required to accurately characterize the extent of a population.
Mosses respond physiologically not only to regional climate and site-scale geology and vegetation, but also to microhabitat factors (e.g. localized patches of distinct substrate chemistry, moisture, shade, temperature, substrate texture, organic debris, and microtopography) that can vary within centimeters. The well-known specificity of some bryophyte species for their preferred microhabitats (Slack 1990, Vitt & Belland 1997) has led researchers to use them as indicators of local environmental factors such as substrate chemistry and air pollution (e.g. Shacklette 1967, Rao 1982, Burton 1990, Glime 1992), which highlights the potential vulnerability of mosses to very small-magnitude chemical changes or very local habitat disturbance (Rao 1982, Lepp & Salmon 1999). It also limits the applicability of conventional mapping and modeling techniques to identify sites likely to support rare moss species, because predictive variables can change on a finer scale than is available in most conventional map products, and may be poorly correlated with broader habitat types.
Summary of biological needs and limiting factors of Spoon-leaved Moss
Although demographic evidence is not available to support hypotheses concerning the relative importance of life history stages to Spoon-leaved Moss persistence (Schemske et al. 1994, Helernum 1998), accumulated observations (COSEWIC 2003a) suggest that diaspore production and dispersal may be the most critical limiting factors for the species in Canada. These observations include the lack or rarity of sporophytes, absence of specialized asexual reproductive structures, perennial stayer life strategy (characterized by relatively low spore output), dioicy (associated with reduced sporophyte production), lack or rarity of male plants in the Canadian population, potential loss (without apparent replacement) of populations, small population size, isolated populations, and severely fragmented habitat.
Rarity in dioicous species (such as Spoon-leaved moss), which produce sporophytes less frequently than monoicous species (Gemmell 1950, Longton 1992a, Longton & Schuster 1983, Mishler 1988), has been linked to their failure to produce sporophytes (Longton 1992a). Factors contributing to this lower reproductive success may be exacerbated at a species’ northern range limit. For example, favourable microhabitats are likely to be smaller and more spatially separated in the northern part of species’ range (Gemmell 1950, Longton 1976, Lesica & Allendorf 1995, Nantel & Gagnon 1999, COSEWIC 2003a), leading to reduced co-occurrence of male and female plants. Furthermore, Bopp (1983) showed that environmental factors linked to latitude (e.g. light intensity, day length, temperature) can affect the production of male and female moss inflorescences, leading to uneven sex ratios and lower sporophyte production (Longton & Schuster 1983). Kallio & Saarnio (1986) also observed reduced sporophyte production in northern climates, whereas vegetative diaspore production (plant fragments, in the case of Spoon-leaved Moss) depend less on seasonal stimuli. The life strategy of Spoon-leaved Moss is also associated with reduced sexual reproduction, in that perennial stayers (During 1979) naturally devote less energy to spore production than to vegetative proliferation (Longton 1992a, 1997), and are known to be underrepresented in diaspore banks (During 1997).
Dispersal range and the relative importance of various dispersal modes of Spoon-leaved Moss have not been studied in any portion of its distributional range. Most moss spores are known to fall close to their parent plants (e.g. Longton 1976, Wyatt 1982), but the high number of spores per capsule and small spore size characteristic of perennial stayers (Longton 1997) suit them well to dispersal over longer distances. Some researchers (e.g. Miles & Longton 1992, Stoneburner et al. 1992) have shown that many spores escape the immediate vicinity, and Pharo et al. (2004) found that many bryophytes have sufficient dispersal and establishment ability to overcome barriers imposed by temperate forest fragmentation in Australia. Very little work has been done on the dispersal modes and dispersal ranges of moss fragments in any species (Cleavitt 2005). Dependence on asexual reproduction implies reduced mobility, and increased efficacy of diaspore establishment (Wiklund & Rydin 2004), yet Mogensen (1981) and Shaw (1993) suggest that long-distance fragment dispersal may occur in some species.
Spoon-leaved Moss populations in the nearby northern United States, where the climate is similar to that of southern Ontario, are a potential source of immigrant propagules (spores or fragments) in Canada. However, the apparent rarity of such a large, distinctive species in south-western Ontario - a once relatively well-collected region (Ireland & Ley 1992, COSEWIC 2003a) despite limited bryological study and access to private land in recent years – may indicate that successful dispersal from the south (or within Ontario) is rare. The possibility of a declining trend in the number of populations in southern Ontario (COSEWIC 2003a) supports the increasing isolation of populations rather than successful dispersal over long distances.
As outlined in the preceding section, mosses such as Spoon-leaved moss respond to their environment on microhabitat, habitat, and regional scales. In general, Spoon-leaved Moss prefers soil substrates, particularly on banks, but sometimes on rocks or tree bases. In Canada, it is usually associated with exposed clay, often avoiding deciduous litter cover by occupying soil hummocks, or tree bases and tree roots.
All extant (and at least some past) Canadian populations were found in close proximity to Helodium paludosum, an infrequent moss species of temperate affinity which also reaches its northern range limit in southern Canada, and which is generally associated with swamps, marshes, and wet meadows. H. paludosum and other bryophyte associates of Spoon-leaved Moss are much wider-spread and more abundant and no useful indicator species are known. Similarly, no rare vascular plants are known to occupy the immediate vicinity of Spoon-leaved Moss populations (R. Gould, K. Frolich, personal communication) in such a way as to provide additional clues to habitat needs.
In its Canadian range, Spoon-leaved Moss is associated with a wide variety of habitat types and moisture regimes (Table 1, Gould 2005), but all confirmed extant populations occur in areas that are at least seasonally moist or flooded. Spoon-leaved moss is found under mature and regenerating deciduous or mixed tree canopies (Table 1). Past and present sites of occurrence vary considerably in overstory age and composition. Perennial stayer life strategy indicates preference for long-term habitat continuity (Longton 1992a, 1997), but Gould (2005) describes a history of deforestation at the species’ Essex and Elgin sites, raising intriguing questions regarding past colonization ability and the species’ capacity to withstand disturbance or successional change. The occurrence of Spoon-leaved Moss in regenerating fields and its apparent disappearance from sites that have become overgrown suggests an affinity for open overstory vegetation.
Spoon-leaved Moss appears not to be associated with rare vegetation or plant community types (e.g. old-growth deciduous forest), and many sites similar, at least superficially, to those at which the species has been found in Essex and Elgin Counties exist across the species’ known Canadian range. If Spoon-leaved moss is as rare as current records suggest, this indicates either: 1) limitation by habitat qualities that are not immediately obvious or 2) limitation by factors other than habitat, such as biology, competitive interactions, or historical events.
As a Carolinian species, spoon-leaved Moss appears to be limited by climate on a regional scale. Only a very small, southern part of Canada supports Carolinian species, and even if this region were pristine, suitable habitats may not be as common as they are near the centre of the species’ range (Lesica & Allendorf 1995, Nantel & Gagnon 1999, COSEWIC 2003a). This natural limitation may leave relatively little leeway for anthropogenic threats to impact Ontario’s small, isolated populations without significantly impacting the Canadian population as a whole.
In section 1.2.1, some potentially limiting biological characteristics of Spoon-leaved moss, such as its reproductive system, dispersal ability, life strategy, and habitat specificity, were summarized. Keeping in mind these limiting biological characteristics, this section outlines the factors that may threaten the species’ stability in Canada. The significance of threats cannot be ranked without more conclusive information on the species preferences, tolerances, and limiting factors.
Many of the threats described below may be classified as specific threats to individual populations. However, it should be noted that there is little evidence of local anthropogenic disturbance accounting for the potential disappearance of Spoon-leaved Moss from sites where it has been documented in the past (COSEWIC 2003a).
Roadside Debris & Roadside Herbicide Application
In Niagara Region, the single documented colony of Spoon-leaved Moss lies within twenty metres of a road, near a littered roadside ditch. There is no trail in the vicinity to draw visitors near to the colony, but given its small size, the population is particularly vulnerable to interference from roadside debris, application of road salt or roadside herbicide application (no herbicide application is currently confirmed to occur on the Niagara Peninsula Conservation Authority lands (K. Frolich, personal communication)).
Concentration of Wildlife Activity
Increased wildlife populations (e.g. deer, wild turkey) have degraded many woodland habitats in southern Ontario and may affect Spoon-leaved Moss or its habitat in Essex if wildlife activity intensifies (R. Gould, personal communication). Gould (2005) has documented some minor wildlife disturbance to part of the Elgin population.
Although no formal assessment of invasive plant species has been done, garlic mustard is present at both Essex and Elgin Spoon-leaved Moss sites, and has become detrimental to most local habitats (R. Gould, personal communication).
Successional habitat change appears to have contributed to the loss of some historical populations of Spoon-leaved Moss (COSEWIC 2003a). While succession may involve natural revegetation of cleared land, it may also be driven by anthropogenic changes in drainage patterns. Although the causes have yet to be researched, several past Spoon-leaved Moss sites are thought to have become drier and/or more densely vegetated since the species was first collected (COSEWIC 2003a). Given its apparently limited reproductive and dispersal ability in Canada, Spoon-leaved Moss may have limited potential to replace populations lost to successional change in once-suitable habitats. Despite the relatively long-term persistence of one population (COSEWIC 2003a, Table 1), and the species apparent adaptation to longer-lived habitats, populations in regenerating stands (Table 1) are vulnerable to extirpation as habitat conditions naturally change over time. Without natural dispersal or intervention to re-establish the species in suitable habitat, the Canadian population as a whole is at risk.
Hydrological changes resulting from global warming trends (Kutner & Morse 1996) and development may affect the moisture regime of plant habitats in southern Ontario, which in the context of limited dispersal ability, may lead to local extirpation of Spoon-leaved Moss without re-establishment of new colonies. Habitat fragmentation may exacerbate the problem by necessitating dispersal over longer distances. On the other hand, the position of Canadian populations of Spoon-leaved Moss on the northern periphery of the species’ range may place it well for climate-related northern range expansion due to migration from the south (N. Cleavitt, personal communication), as has been predicted for some plants (Kutner & Morse 1996), including tree species in the Great Lakes Region (Walker et al. 2002).
Although the habitats of the three known extant populations of Spoon-leaved Moss occupy small, variably wooded habitat fragments in close proximity to human activity (trails, roads, and active agriculture) (COSEWIC 2003a), there is no known specific, immediate threat to the populations. Gould (2005) reports that the small foot and game trails away from the main recreational rail trail (‘Greenway’) adjacent to the Essex County population are used infrequently and thus appear not to present a direct human threat to the moss colonies. COSEWIC (2003a) observed that the site is uninviting to passersby due to dense hawthorn, poison ivy and mosquitoes. Similarly, in Elgin County, the population lies within a few metres of a well-used hiking trail, but there is no evidence of hikers frequently diverting from the trail or of all-terrain vehicle traffic in the area of the colonies.
Habitat destruction and fragmentation, including air quality degradation
While larger-scale, regional threats to Spoon-leaved Moss survival are on-going, they are likely to affect populations and availability of recovery habitat in a more gradual manner than most local threats. These regional threats include habitat destruction and fragmentation due to intense urban, industrial and agricultural development as well as air quality degradation. Air quality reports for Ontario (Ontario Ministry of the Environment 2004) show that the region has some of the highest pollutant levels in the province. Agricultural land-use intensity has been shown to be negatively correlated with bryophyte species richness (Zechmeister & Moser 2001). The intensification of land uses arising from the dense population of southern Ontario has long been cited as a threat to Carolinian habitats and flora in Canada (Maycock 1963, Maycock & Fahselt 1987, Allen et al. 1990, Argus & Pryer 1990, Oldham 1990, Klinkenberg et al. 1990, Argus 1992, Keddy & Drummond 1996, Cadotte & Lovett-Doust 2002).
Stochastic Factors (genetic drift, inbreeding)
The effect of stochastic factors on Spoon-leaved Moss demography has not been studied. The threat imposed by environmental stochasticity (Lande 1993, references cited in Schemske et al. 1994), as well as inbreeding and genetic drift (Barrett & Kohn 1991, Ellstrand & Elam 1993, Young et al. 1996, Lesica & Allendorf 1992) may increase with decreasing population size. All Canadian populations of spoon-leaved moss are relatively small, but the Niagara Region population (200 cm2) is especially vulnerable in this respect. Low genetic diversity resulting from, for example, lack of sexual reproduction and/or founder effect from chance dispersal from U.S. populations (which has not been studied or confirmed in Canadian Spoon-leaved Moss) may also increase species’ vulnerability to stochastic events.
Proposed identification of the critical habitat of Spoon-leaved Moss
The general habitat preferences of Spoon-leaved Moss and descriptions of the habitats it occupies in Ontario, to the extent they are known, have been described in section 1.2.2 (Habitat needs) of this recovery strategy. For current purposes, section 2 of the Species at Risk Act defines critical habitat as “…the habitat that is necessary for the survival or recovery of [Spoon-leaved Moss]” (Environment Canada 2004). The recovery goal, therefore, is integral to the concept of critical habitat in that sufficient habitat must be identified to allow for the recovery goals to be accomplished. The recovery goal for Spoon-leaved Moss (see section 2.2) is to conserve existing populations in the long term and, if possible, to restore the species’ long-term stability and self-sustainability in Ontario by increasing the size of existing populations and/or increasing the number of known occurrences.
Only those three sites that currently support populations of Spoon-leaved Moss in Ontario (Table 1) are known to be suitable for the species’ growth and are thus identified as proposed critical habitat in this recovery strategy. The boundary of the critical habitat cannot be strictly delineated at this time because of the uncertainty as to the size of the surrounding area on which activities could affect change to the habitat. For example, the area within which change in overstory vegetation is likely to affect the moss populations may be smaller than that within which drainage patterns must be maintained. In the interim, however, the minimum area of critical habitat for Spoon-leaved Moss is proposed to include the area occupied by extant populations and the extent of the vegetation community (based on the Ecological Land Classification for southern Ontario) in which it occurs at each site (habitat characteristics of sites are described in Table 1). This boundary should be refined as more information is gained on the factors that may influence habitat suitability and quality.
The vulnerability of the few known populations to local or regional disturbance, in combination with apparent extirpation of populations at sites that have recently undergone natural successional change, suggests that securing the Ontario population also requires the expansion of known populations and/or increasing the number of known populations. To meet this part of the recovery goal, habitat that is not currently occupied by the species (or not currently known to be occupied) may need to be identified as critical habitat in the future as research and recovery proceed. For example, the discovery of additional colonies associated with known populations, or of additional populations will add to the critical habitat and will provide data for critical habitat characterization. An incremental approach to critical habitat identification is therefore recommended for Spoon-leaved Moss. A research schedule to fully identify critical habitat is given in section 1.4.4 of this recovery strategy.
Examples of activities likely to result in destruction of the critical habitat
As outlined in section 1.3 (Threats), no direct, specific threats to Spoon-leaved Moss habitat at known extant sites are currently known or anticipated. However, Spoon-leaved Moss possesses specific points of vulnerability with respect to activities characteristic of prevailing land use. With this in mind, activities that are likely to result in destruction of the critical habitat include (but are not limited to):
- Hydrological change (increasing or decreasing moisture levels, alteration of seasonal moisture regime, changes in water flow patterns, even on a very small scale) resulting from water use / re-direction on adjacent land, which may impact populations directly or trigger successional change in favour of overstory vegetation that alters growing conditions (e.g. light, moisture, temperature) in the understory;
- Contamination of, or other chemical change in, moss substrate or run-off from adjacent land;
- Trampling by foot access, or other recreational activity, or by wildlife;
- Removal (intentional or unintentional) of overstory and/or ground vegetation by humans or wildlife, except for the purposes of habitat enhancement;
- Removal or disturbance of substrate;
- Overgrowth by invasive, competitive plant species;
- Accumulation of roadside garbage;
- Use of herbicides for weed and woody plant control (in the case of the population in Niagara Region); and,
- Application of salt to roads adjacent to sites.
Existing and recommended approaches to habitat protection
Spoon-leaved Moss is Endangered in Canada, meaning that it faces imminent extirpation or extinction (COSEWIC 2003b) and has been appended to the list of Wildlife Species at Risk (Schedule 1) of the Species at Risk Act. It is also designated Endangered on the list of Species at Risk in Ontario (Ontario Ministry of Natural Resources 2004), and is regulated under the provincial Endangered Species Act (Ontario Ministry of Natural Resoures 2005).
All sites currently identified as critical habitat are protected at this time. The Ontario Ministry of Natural Resources owns and manages the property where the Elgin County population occurs, and the site in Niagara Region is owned and managed by the Niagara Peninsula Conservation Authority. At the time of the COSEWIC (2003a) status report, the Essex County site was privately owned, but has since been acquired by Ontario Parks with the assistance of the Nature Conservancy of Canada (B. Huis, R. Gould, personal communication). Current management plans do not account for Spoon-leaved moss (Poirier et al. 1982), but amendments are expected as management plans are developed (K. Vlasman, R. Gould, personal communication).
Despite the proximity of Spoon-leaved Moss populations to recreational and agricultural activity,it seems likely that any infrastructure placed at the sites to prevent access from nearby trails or roads would only serve to draw attention to the populations (thereby increasing traffic to the sites) and may critically alter habitat quality. Broad strategies of monitoring, management, and research are therefore recommended (sections 1.3.4 and 2.2.3). For example, habitat conditions at the sites should be monitored for threats, so they can be managed as they arise to prevent the loss or destruction of critical habitat. Research (including surveys) must precede the identification of additional critical habitat and its protection. Protected areas within the distributional range of Spoon-leaved Moss should be targeted for preliminary research aimed at increasing the number/size of populations through inventory, or introduction.
Schedule of studies
The schedule of studies (Table 2) outlines steps in the incremental identification of critical habitat for Spoon-leaved Moss. The activities are listed in priority order. The results of initial activities may necessitate modification of the order or nature of subsequent activities. These research activities are interdependent with the recovery approaches outlined in section 2.2.3 of this report and the schedules (activities listed in Tables 2 and 3) should be considered in combination with each other.
|Description of Research Activity||Rationale|
|Seek undocumented colonies of Spoon-leaved Moss in protected areas where populations are known to reside and at historic sites of occurrence||Confirm current area of occupancy of extant and historically documented sites (identify direct critical habitat)|
|Monitor populations of Spoon-leaved Moss (for example through fixed-point photography, colony mapping, colony tracing) to gather data on temporal variability in abundance and distribution (and therefore critical habitat) within sites||Modify area of critical habitat based on area within which population is likely to vary over time|
|Seek and monitor undocumented populations off protected areas and characterize their habitats, especially near previously-documented occurrences||Identify additional critical habitat|
|Fully characterize the habitats and microhabitats of existing populations||Quantify habitat variables for a detailed understanding of growing conditions where colonies occur for habitat modeling. Further refine critical habitat.|
|Characterize habitats and microhabitats of populations in the northern United States||Take advantage of increased abundance (more data points) to characterize species’ habitat preferences in a climatically similar region for habitat model; identify potential source populations should re-introduction become desirable|
|Apply habitat mapping and modeling; correlate with protected areas and land use / management activities||Identify potential critical habitat for seeking (or introducing, if necessary) undocumented populations|
|Conduct spore establishment and/or transplant experiments||Determine suitability of unoccupied potential critical habitat|
Actions already completed or underway
Gould (2005) began implementing the schedule of studies by conducting field surveys that resulted in an increase in the known area directly occupied by Spoon-leaved Moss (and therefore critical habitat) for the populations in Essex and Elgin Counties beyond that reported by COSEWIC (2003a) (Table 1). All managers of affected sites are aware of the locations and significance of Spoon-leaved Moss. No other recovery activities have been initiated.
NOTE: “Sex” refers to whether the collections represented female (F) plants, or could not be examined / determined (U) (no male plants or sporophytes have ever been documented in Canadian populations, although not all collections have been examined). Note that unsuccessful searches at historical collecting locations should be interpreted in the context of the available detail concerning collecting location (refer to COSEWIC 2003a and herbarium labels), which was generally low.
- Date Modified: