- Open Access
More fishers and fewer martens due to cumulative effects of forest management and climate change as evidenced from local knowledge
© The Author(s). 2017
- Received: 26 June 2017
- Accepted: 3 September 2017
- Published: 7 September 2017
Monitoring of fur-bearing species populations is relatively rare due to their low densities. In addition to catch data, trappers’ experience provides information on the ecology and status of the harvested species. Fisher (Pekania pennanti) and American marten (Martes americana) are mustelids that are sensitive to forest management and therefore considered to be ecological indicators of forest health. Fisher populations have increased in eastern North America since the early 2000s and this could have resulted in a northeastern extension of the species’ range and increased overlap with marten’s range. Moreover, habitats of both species are subject to natural and anthropogenic disturbances. The objective of this study was to document the knowledge held by local trappers in the northern area of sympatry between fisher and marten to identify factors that could explain variation in populations of the two species and interactions between them.
Forty-one semi-directed interviews with Indigenous and non-Indigenous trappers in the Abitibi-Témiscamingue region of western Quebec (Canada), at the northern limit of the overlapping ranges of the two mustelid species.
Trappers highlighted the lack of exclusivity of marten and fisher to coniferous forests, although marten is more closely associated with them than is fisher. Fisher apparently also takes advantage of open environments, including agroforestry systems. Moreover, climate change increases the frequency of freeze-thaw events that cause the formation of an ice crust on the snow surface, which favors fisher movements.
The fisher was identified as a competitor and even a predator of the marten. Furthermore, the fisher is less affected than the marten by forest management, and it also seems to benefit from climate change to a greater extent.
- Aboriginal people
- Anthropogenic disturbances
- Snow conditions
Fur-bearing mammals are considered to be particularly sensitive to habitat loss and fragmentation [1–4]. Their habitats have been affected especially by major changes that are incurred through human activities, such as forest harvesting and agricultural development [5, 6]. Climate change could further modify or reduce the quality of available habitats [7, 8]. Yet climate change and anthropogenic disturbances such as forest harvesting may also increase access to new territories by modifying biotic and abiotic factors that otherwise would limit a species’ potential to utilize a territory . Given that climate change and anthropogenic disturbances occur over long periods of time, resulting in complex cumulative impacts, they are often difficult to understand and to document [10, 11].
Populations of fur-bearing animals typically exhibit low densities. Consequently, monitoring these species to document their status is relatively rare [12, 13]. Sales of trapped pelts have long been used by wildlife managers to track fluctuations in the abundance of certain wildlife populations [14–16]. However, from one year to the next, fur sales can be influenced by animal population status and trapping efforts, which depend upon numerous social (e.g., employment-trapping conciliation, trappers’ health status), economic (e.g., variation in fur prices, available material resources), and environmental (e.g., weather, local habitat disturbance) factors [17–19]. Beyond information that is provided by fur sales, the experience of trappers and the knowledge that they accumulate over many trapping seasons is an invaluable, frequently untapped source of information, which would enrich our understanding of species with relatively low densities, such as mustelids [20–22].
The growing interest in local knowledge is due, among other things, to the potential saving on time and money needed to gather the scientific information required to meet environmental challenges [23, 24]. In addition to the number of individuals that are caught, trappers’ experience allows us to learn more about the ecology of exploited species [22, 25]. Trappers continuously monitor population dynamics as well as natural and anthropogenic forest disturbances. Trappers have developed a solid expertise regarding ecosystem responses, including wildlife responses to habitat changes, over broad spatiotemporal scales [26, 27]. Knowledge on habitat requirements of those species which are most sensitive to forest practices, from both local and scientific sources, is essential for the conservation of key habitats .
Both fisher (Pekania pennanti) and American marten (Martes americana) are mustelids trapped for their fur that play a key role in forest social-ecological systems in eastern North America. They are sensitive to forest management prescriptions and considered to be ecological indicators of forest health [1, 29, 30]. American marten is one of the species most frequently sought by trappers because of its ease of capture and the high market value that is placed upon its fur [20, 31, 32]. In addition, marten and fisher are important in some Indigenous cultures, notably those of the Anishnaabeg  and the Cree . These species can be considered as cultural keystone species that are essential in maintaining the complexity of socio-ecological systems .
During the 1970s, the fisher experienced periods of low abundance in North America . This was attributed to over-exploitation of its fur and habitat loss . Since the early 2000s, the populations appear to have recovered and the interest of trappers in the fisher has intensified, resulting in a substantial increase in fisher pelt sales, especially in Quebec . Sales of fisher pelts apparently indicate that their geographical distribution could be expanding towards the northeast. This change in fisher distribution would thus result in greater overlap with marten’s range in habitats that are undergoing natural  or anthropogenic disturbances [6, 38]. The objective of this study was to document the local knowledge of trappers in western Quebec (Canada), where distributions of fisher and marten are sympatric, to identify factors that could explain variation in populations of the two species and the interactions between them.
Fisher and marten are two species that are endemic to North America. The geographic distribution of the fisher is the least extensive of the two species, and straddles the southern portion of marten’s range . Fisher is found mainly in temperate and boreal forests of North America. Since the mid-1800s, the geographic distribution of the fisher has decreased considerably, primarily due to changes associated with the Little Ice Age (ca. 1250–1750 CE) in eastern North America .
The sugar maple-yellow birch bioclimatic domain occupies the northernmost part of the temperate deciduous zone. The main overstory species are sugar maple (Acer saccharum Marsh.), yellow birch (Betula alleghaniensis Britton), red oak (Quercus rubra L.), eastern hemlock (Tsuga canadensis [L.] Carrière), white pine (Pinus strobus L.) and red pine (Pinus resinosa Aiton). Després et al.  have shown that frequent and small gaps are the main natural disturbance agents in this area. In this bioclimatic domain, fisher represents 40% of the combined sales of marten and fisher pelts (10-year average, 2006 to 2015) .
The balsam fir-yellow birch domain corresponds to the transition between the northern temperate zone and the boreal zone. The main tree species are yellow birch and conifers, such as balsam fir (Abies balsamea [L.] Mill.), white spruce (Picea glauca [Moench] Voss), pines (Pinus spp.), and eastern white cedar (Thuja occidentalis L.). Spruce budworm (Choristoneura fumiferana) outbreaks and catastrophic wildfires are the two main natural disturbances [45, 46]. In this sub-domain, fisher constitutes 17% of the combined sales of marten and fisher pelts.
The balsam fir-white birch domain occupies the southern part of the boreal zone. The forest landscape is dominated by fir and white spruce stands, with paper birch (Betula papyrifera Marshall), trembling aspen (Populus tremuloides Michx.), black spruce (Picea mariana [Mill.] Britton, Sterns & Poggenb), jack pine (Pinus banksiana Lamb.), eastern larch (Larix laricina [Du Roi] K. Koch), and white cedar. As is the case in the balsam fir-yellow birch domain, spruce budworm and fire are the main natural disturbances [47–49]. In this domain, marten dominates fur sales, with fisher accounting for about 8% of combined sales. In the three bioclimatic domains, logging has become a major source of disruption over the last few decades (e.g., ).
Despite a sharp downturn in fur prices over the past few decades, together with habitat loss and the development of fur farms, trapping activities still generate substantial revenues [18, 32]. The province of Quebec registers the highest sales of American marten (15 to 30%) and fisher (25 to 33%) pelts in Canada . In Quebec, about 8000 trapping licenses have been purchased annually since 2010 . Commercial trapping is practiced in three categories of territory: structured (traplines), unstructured (open access) and restricted access to Indigenous people only. Abitibi-Témiscamingue is one of the most popular regions for trapping in Quebec; in 2012, the economic benefits (gross domestic product, tax revenues) generated by trappers, weighted by population, were the highest in the province .
Recruitment of participants
Trapping is an activity that requires knowledge of the biology and ecology of furbearers. This knowledge develops with experience over the years. The use of land and natural resources thus fuels trappers’ knowledge . To ensure the sustainability of their harvests, trappers must pay particular attention to the sampling effort that they deploy under changing environmental conditions . Traplines are thus considered to be integral ecosystems that must be managed responsibly . Trappers are recognized as “land custodians,” who are particularly interested in documenting changes in the distribution and harvesting of fur-bearing animals and the effects of habitat disturbances on forest operations and climate change . We sought to meet with experts, both Indigenous and non-Indigenous, who were the most recognized by their peers because of their experience in trapping and their knowledge of the forest in general, and the habitats of marten and fisher in particular. We have created four groups: i) marten trappers who were active on the same territory for several years (active trappers, AT); ii) trappers who were recognized as experts by their peers, but who are no longer able to carry out their activities on a full-time basis because of their age (recommended trappers, RT); iii) experts who were involved in the management of trapping areas or in fur sale (experts, Ex); iv) elders (Elders, E). Inclusion of elders has been justified, given their important role in the transmission of forest-related knowledge over the generations, and which has increased the temporal depth of information. We used the “snowball sampling method,” whereby people in the communities identified the most experienced trappers, who in turn were able to suggest other trappers, and so on [57, 58]. This identification of local experts by peers ensures the recruitment of the best-informed individuals [57, 59].
Data collection and analysis
We interviewed the participants in semi-directed individual interviews . This is a flexible survey technique that offers possibilities for acquiring additional information, within a familiar exchange framework . We conducted 41 interviews with Indigenous (n = 27) and non-Indigenous (n = 14) trappers. Indigenous trappers were members of the Anishnaabeg communities of Kebaowek (n = 5), Kitcisakik (n = 17), Timiskaming First Nation (n = 4) and Wolf Lake (n = 1). Most participants were men (n = 38) over the age of 40 (n = 37). Geographic areas were delineated a posteriori in order to group participants with consistent information: Zone 1 (n = 8), Zone 2 (n = 14), Zone 3 (n = 14) and Zone 4 (n = 4) (Fig. 1). The activities of one participant covered the entire study area. Interviews were conducted in French, English or Anishnaabemowin, depending upon the preference of each participant. Anishnaabemowin interviews were conducted in the presence of a contact person with whom the participants were familiar and who could provide translation. Codes that were used to identify participants corresponded to their status (AT, RT, Ex or E), followed by a number corresponding to the order in which they were encountered, and the area to which they could relate (Z1, Z2, Z3, Z4).
The interviews were intended to provide a better understanding of trappers’ perceptions of marten and fisher habitat use, and the interactions between the two species. The purpose of the questions that were asked was to document the perspectives of trappers on marten and fisher ecology within the study area and their perceptions regarding the effects imposed by forest management and changes in snow cover (Appendix). The main themes of the interviews were: (1) predator-prey relationships of marten and fisher; (2) the evolution of annual harvest success; (3) characteristics of locations that were utilized by each species, including hunting, cover and breeding sites; (4) the effects of forest management on habitats; and (5) changes in winter conditions. Interviews were conducted between August 2015 and March 2016. Participants were re-contacted following the analysis of the individual interviews to complete and validate the information . Thematic analysis of the interviews was conducted using QSR NVivo 10 software, which made it possible to divide the corpus of information into themes to define its meaning by successive destructuring-restructuring operations . Precise identification of species that were mentioned by the participants was not always possible. They are presented at the most precise taxonomic level possible, i.e., according to genus or family.
This project has responded to a request from Indigenous communities to investigate and better understand the reasons behind fluctuations in fisher and marten populations in their territories. We received a certificate from the Ethics Review Board at UQAT (the Université du Québec en Abitibi-Témiscamingue, # 2015–04). The project was also approved by the Band Councils of the participating communities: Kitcisakik, Timiskaming First Nation, Kebaowek and Wolf Lake. Each meeting began with a presentation of the context of the study and the rules of confidentiality. Participants were asked for their consent prior to the interview. Participants were involved in this research on a voluntary basis. Participants who wished received a summary of the main results of the research. Preliminary results were presented to the participating communities in advance of manuscript preparation and submission.
Marten prey species
[The marten, she eats a lot of mice. A year where you have a lot of mice – and this is a 3-year mouse cycle – the marten will raise four young, (…) but the following year you will have practically no babies. The squirrel is also a feast for the marten: when you have the marten, you do not hear squirrel calls.] [E1-Z2]
[People think that the marten catches hares, partridge, but it is mostly the mouse that it hunts. When there is too much snow, she switches to the air (in the trees) to catch squirrels, flying squirrels.] [AT12-Z2]
Fisher prey species
[(The fisher) even eats fish, it goes up to whitefish spawning grounds, where it often drags fish ashore, like the lynx. The marten she does not do that, she is not able to kill a fish in the water.] [Ex30-Z3]
[(The fisher) is the only animal that is going to eat porcupine, it is able to go and kill it, it flips it on its back and seizes the prey by the neck.] [AT2-Z1]
Relationship between the marten and fisher
[Clearly, it is the fisher that has the upper hand. It is faster on the ground, but the marten is faster when climbing trees. But the marten, sometimes, it jumps from tree to tree and misses its mark. The fisher waits on the ground beneath the tree. If the marten falls to the ground, it is done for, it is so fast! In the snow, the marten is going to walk under windthrow, but the fisher struggles more, it is too big. That is why the marten loves the windthrow, the overturned wood, the old roots. The fisher will go there too, but it lacks the facility of the marten.] [AT8-Z1].
[But fishers also eat martens. They kill martens. I saw that they chase them, from the tracks, the fishers run after the martens.] [RT38-Z1]
[The little ones (fishers) surely have predators, but not the adults.] [RT29-Z3]
[The wolf and coyote are able to attack (the fisher) quite easily because the wolf attacks pretty much everything that moves. When you have a lot of wolves on a territory, there is hardly anything else.] [AT4-Z2]
Evolution of captures
Participants have all found that marten captures have been declining for several years, but more markedly in the 2015–2016 season. The trappers were unanimous in stating that they have observed far fewer tracks recently compared to previous seasons. These responses point to several underlying causes. First, participants mentioned fluctuations in trapping effort, which intensify when the price of pelts from the previous season was high. Second, some trappers admitted to having captured a large number of martens in the 1980s, and observed mainly females in subsequent years, which can be interpreted as an indicator of over-exploitation. Third, several participants stressed the ease with which marten could be caught in traps, together with the increased likelihood of over-trapping them quickly when capture regulation was not yet implemented. Fourth, when prices for marten pelts were high, participants had noted an increase in competition by more occasional trappers. Since then, prices have dropped substantially and trapping has decreased. Several trappers suggested that fur price on the marketplace was the main factor regulating marten catches.
Several trappers have suspected severe winters (e.g., 2014 and 2015) as being potentially responsible for the decline in marten populations. Participants further attributed the general decline in marten populations to changes in their habitats and to direct mortality incurred by forest harvesting machinery. Participants underscored the fact that after logging, game can desert the territory due to the lack of protection, thereby reducing the prey base upon which marten relies. Further, they explained that marten avoids crossing large canopy openings, such as those created by harvesting operations; rather, it prefers to move along the edges of intact forest.
[A year where martens have no trouble finding food, it is going to be a year where people are going to catch less. When it has food, it will stay there, it will move less, is less in search. So it is going to have less opportunity to go through a trap. (…) A year like this year when the sampling was less good, I call it a year for nature. I'm happy with that.] [Ex9]
Participants in Zones 2 and 3 (see Fig. 1) indicated that fisher populations had decreased, particularly in the late 1980s as a result of increased trapping efforts that were driven by high fur prices. At that time, they indicated that the price of fisher pelts was higher than that of marten. In addition, Zone 3 participants attributed reduction in fisher abundance to the cutting of red and white pine that this species utilized as resting sites or used for raising young. Participants in Zones 2 and 3 found that as a result of the aforementioned period, fewer fishers travelled during the 1990s. Since the mid-1990s, participants reported that numbers of captured fishers remained relatively stable in Zone 1 (Fig. 1), while they have been increasing since 2000 in Zone 2, increasing since 2010 in Zone 3, and increasing since 2007 in Zone 4. According to Zone 4 participants, fisher captures commenced in 2000. They attributed this development to fisher recovery in places that are difficult to access with forestry machinery, viz., on steep slopes and near rivers. In contrast, participants from Zone 2 noted that increases in fisher captures coincided with the arrival of raccoon (Procyon lotor) to the area. Raccoons are found predominantly in Zones 1 and 2, and more recently, in Zone 3. Zone 2 trappers have also noted that raccoon populations have increased, especially since the development of cereal crops (especially corn) in the zone.
Peaks in populations that had been observed by participants likely included incidental captures that were made in traplines originally planned for marten or fox capture. Peaks were also the result of changes in the type, size and layout of traps that were designed specifically to capture fishers. For example, trappers employ larger traps, which are situated closer to the ground. They recognized the risk of the trapped animal being damaged by small mammals or by overheating when their bodies came in contact with the soil, but stressed greater capture efficiency. Other trappers have even installed snares that are specifically made to trap fishers for only a few years, similar to those they would deploy for foxes. Some participants mentioned that indicators of fisher presence, such as captures or snow tracks, had decreased throughout the study area over the past 5 years; in some areas of Zones 1 and 3, these declines occurred over the past 10 years. One explanation mentioned by the participants was based upon reductions in fisher populations due to a substantial harvest by trappers. Other explanations were related to general changes in habitat and the possibility that severe winters could affect the survival and, therefore, the state of fisher populations.
Most participants identified their best marten capture sites as being primarily located in conifer stands, especially spruce. Participants trapped martens in other conifer stands, which were dominated by fir, white cedar, pine, and hemlock, yet mixed forests were also suitable for marten capture. Trappers set up traps primarily in mature stands, viz., old forests where there are more branches, which they characterized as “dirty and dense forests.” While participants considered that martens used hardwood forests, these were more likely to be transient habitats. Indeed, trappers indicated that martens move with great difficulty through hardwood stands because of snow accumulation and, especially in winter, hardwood forests are too open to avoid predator attacks. According to the participants, good marten habitat is at the interface between coniferous and hardwood forests. Martens require cover to protect themselves from predators, but they also need to find food. Participants stressed the need for ground structures where small mammals can hide. Trappers further indicated that the presence of gaps or windthrows favors the presence of marten. This type of habitat structuring is mostly found in mature forests and on hillsides. Participants also explained that riparian areas were strategic locations for setting traps because martens often travel through these zones. Finally, participants emphasized the presence of old trees in which martens can make their dens, such as in woodpecker cavities or downed wood on the ground, and in old birch trees or snags.
Some participants attributed the same habitats to the fisher as to the marten, but several others emphasized the importance of large pine and white cedar utilization by the former species, particularly large hollow trees where fishers could take refuge. Participants also mentioned that fishers could travel greater distances than martens. Trappers likewise frequently set their traps along watercourses, which was part of the same strategy that was employed for capturing martens. Yet some trappers noted that more fishers could be caught in the hills, in contrast to results obtained for marten. Similarly, trappers found that they could catch more fishers than martens in deciduous forests. Unlike martens, fishers utilized cut-overs; indeed, fisher populations increased with the concomitant removal of forest canopies during logging. Trappers in Zone 2 reported successful fisher captures in a variety of habitats, ranging from mature forest to agroforestry landscapes, to edges of agricultural fields, and even in close proximity to human habitation rather than deep within forest stands. In the same area, trappers snared fishers in traplines that were intended for capturing foxes. Several trappers have indicated that fishers can use more sparse habitats than martens because they have less need for protective cover against predators. Experts have reported that trappers associate the presence of fishers with that of Canada lynx. They explained that the two predators share the same food resources, i.e., snowshoe hare and ruffed grouse.
Changes in forest structure and composition
[There is nothing in a plantation: no birds, no hares, it is a ghost forest.] [Ex16-Z2]
Effects on marten and fisher
[In cut forests, animals, if they have no shelter, they do not stay there.] [RT18-Z3]
[Because when it has been cut, the marten, you can forget about it. And, I’m going to tell you that right now, it is pitiful. It is the opposite for the fisher.] [AT11-Z2]
Orientation for development
Participants advocated that forest cover should be maintained not only to retain predator food sources, but also to protect the marten from "all predators that can run after it." They emphasized the importance of retaining pines and white cedars, in particular, as resting sites for marten and fisher. More generally, they stressed the need to conserve dead wood on site. They considered that protection strips (forest that is left untouched) around lakes and wetlands were not wide enough to act as appropriate buffers. Partial cuts were much more appreciated than clear-cuts by the trappers. Although they recognized that the forest industry currently maintains harvest retention patches, trappers did not consider that these were large enough to support game. Rather than leaving a plot of standing timber in the midst of a large clear-cut, participants suggested that smaller cuts surrounded by large-diameter trees promoting natural regeneration were preferable. They recommended a forest harvesting system, such as gaps or strip-cuts, which permit harvesting of forest patches, while retaining the forest matrix.
[There was not as much crust as that, before, the crust was just in springtime. Now it happens in winter, in December it has already happened. Before it was only March-April, when the sun starts to rise much higher above the horizon, it melts on top. Sometimes, it is too thin for us to walk on, but it does not bother the animals.] [AT22-Z2]
[I have always benefited from the crust, but it happens earlier now and it will last longer because we have had a lot of rain and it has permeated the snow from one side to the other. For a fisher, it must be paradise.] [AT4-Z2]
[If there is soft snow, the marten is going to have the advantage over the fisher that runs after him. On the hard (snow), I think the fisher would have the advantage.] [AT6-Z4]
[The best fur is when it is cold. Pelts are darker when taken later, and the same is true for all species. The price is better for dark fur.] [RT36-Z1]
Information that was derived from interviews with local trappers regarding the evolution of marten populations and pelt counts had exhibited the same trends as fur sales data that were compiled by the Government of Quebec (Ministry of Forests, Wildlife and Parks, MFFPQ) at the regional level (Fig. 2). Fisher abundance appears to have increased, especially since the 2000s at the northern limit of its range (Zones 2 and 4). Compared to Zone 3, Zone 2 is a region that contains more agricultural operations and more mixedwood stands than coniferous stands. However, trappers have noted a recent decline in fisher populations, which is particularly pronounced in Zone 3. The main cause of this decline is attributed by trappers to the decrease in large conifers that are used as resting and rearing sites. Marten populations are decreasing throughout the study area. However, trappers have acknowledged the discrepancy between sales of pelts that were recorded for each trapline and what was actually taken. One of the main reasons is the harvest on unstructured territories and exchanges between trappers to respect harvesting thresholds set by the government that would permit them to retain their rights to exploitation. Interviews were also used to identify changes in populations of other species for which the Quebec Ministry of Forests, Wildlife and Parks did not have data, such as unexploited (e.g., prey) species or those for which the fur sales data do not reflect these observed changes (lynx exploitation thresholds), or the particular nature of a species (e.g., wolves, which trappers are targeting for the challenge that its capture represents).
Trappers who were interviewed in this study were concerned about marten populations, a species that is particularly vulnerable to habitat alterations caused by logging operations. Concerns were expressed about the lack of protective cover, which has been incurred through the increase in hardwood species  and reductions in coarse woody debris (CWD) on the ground surface [65, 66]. The marten has long been perceived as being dependent upon mature and aging conifer stands [3, 67]. These stands generally provide greater quantities of CWD than do younger stands, forest plantations and intensively managed stands . CWD provides subnival spaces that can be used by marten . Subnival spaces are particularly important for prey accessibility and provide protection against predation, together with resting sites for thermoregulation [70–73]. Consequently, habitat use by marten is mainly dependent upon the internal structure of the forest [74, 75]. Fishers, in contrast, appear to be able to exploit a greater diversity of habitats, including more open forest environments, the edges of agricultural environments, and even urban areas [22, 76]. Fishers are not necessarily old-growth forest specialists, and are known to utilize young forests, mixedwood stands and ecotones . A study that was conducted in 2016 in New York State , however, showed that occupation of the territory by the fisher was positively influenced by proportions of coniferous and mixedwood forests, but negatively affected by the density and proportion of agricultural environments. Like marten, the fisher likely would be more dependent upon the structure of the forest than on the age or type of settlement [22, 73–75]. Participants also pointed out that mustelid habitats were especially consistent with those of their main prey: snowshoe hares, squirrels and other small mammals. These prey species and, therefore, fisher and marten, require coarse woody debris, vegetation cover, and structurally complex forests [72, 78]. This complex structure is encountered mainly in old-growth forests, but may also be present in younger stands that have suffered windfalls or insect outbreaks [79, 80].
Participants stressed the importance of the availability of resting and rearing sites, which they did not consider to be sufficiently protected by forest management. Fishers depend upon the availability of large moribund trees that often have rotting heartwood, such as white pine, white cedar and yellow birch, in which they can make their dens and raise their young [81, 82]. As noted by Bridger et al. in 2016 , managers need to consider the importance of den availability for martens and fishers. The scarcity of dead wood is a further ecological challenge to forest management [80, 83–85]. Protection measures for dead wood were previously mainly guided by FSC (Forest Stewardship Council) forest certification . With the introduction of ecosystem-based forest management, silvicultural practices have tended to create forest landscapes that contain all of the diversity of natural forests, including the composition and shape of stands and the presence of trees of different sizes, snags or woody debris [87–90]. Participants also encourage forest development that creates small openings, similar to gaps that naturally drive the development of sugar maple-yellow birch stands .
More generally, participants reported that the return of martens after logging was more rapid in mixedwood than in softwood stands. Most mixedwood harvest cuts are partial cuts, while softwood stands are cut more intensively. In 2005, Potvin et al.  determined that cut mixedwood stands had higher lateral cover and higher regeneration compared to cut conifer stands. Forest management influences populations of competitors and even predators of marten and fisher. Lynx, wolf and coyote probably benefited indirectly from forest management, which favoured their main prey, including snowshoe hare and moose [91–93]. Marten would thus be the victim of apparent competition . Whether through habitat alterations or its effects on prey or predator species, forest management appears to be detrimental to marten, while favouring the fisher.
The fisher is limited in its movements over snowpacks that do not fully support its weight and is dependent upon the coniferous cover that intercepts the snow . However, lower snow accumulation and ice crusting over a longer period of time result in greater load-bearing capacity of the snowpack, which seems to favour the fisher, thereby providing it with access to new habitats [8, 96]. The experience of trappers also has made it possible to document this snow load-bearing capacity, a characteristic for which no scientific follow-ups have been performed over long temporal and spatial scales.
Climate change and human activity have led to changes in abundances of other species, which in turn may influence the population dynamics of fisher and marten. Raccoon and coyote populations have increased in the northern part of their ranges [97, 98]. Populations of bald eagles and other raptor species have appeared to be recovering naturally throughout North America, since the use of DDT was discontinued [99, 100]. All of these changes appear to be detrimental to marten, which would increase the abundance of predators and competitors while leading to marten habitat degradation at the same time. The fisher would be less affected, having fewer predators than marten.
The fisher may exert competitive dominance, thereby excluding marten from areas that the latter occupies . Indeed, competition between the two species has been reported by the participants. Yet interviews with trappers indicated that the principal relationship between fishers and martens was predation by the former on the latter species. To our knowledge, no study has yet been able to evaluate effectively the extent of predation of fisher on marten. In 2010, McCann et al.  documented predation by fishers on martens in northern Wisconsin, which would occur only during the winter. Both fisher and marten eat squirrels, other small mammals and snowshoe hares, but in different proportions. They explained that their overlapping diets may lead to greater interactions in the winter when hunting by both predators decreases prey populations [103, 104]. Additional studies would be required to identify the importance of marten in the diet of fisher in areas where the species are sympatric. Assessment of predation by fisher on marten would be all the more relevant as the abundance of fisher increases north of its current range, resulting in greater interactions with marten.
In this study, it was difficult to distinguish between effects of natural and anthropogenic disturbances on the population dynamics of marten and fisher. Whether it is forest rejuvenation, increasing the proportion of deciduous species, intensifying agricultural activities, climate change, or the consequences of their effects on other animal species, all of these factors are cumulative and, according to the experiences of the trappers who were interviewed, appear to favour the fisher to the detriment of the marten.
Trappers‘experience has shown that martens and fishers are not exclusive to coniferous stands, although the marten is more closely associated with these forests than is the fisher. Trappers also identified the fisher as an important predator of martens. The fisher appears to benefit from open environments, including landscapes that have undergone extensive human alteration, such as forest cut-overs and agroforestry systems. For example, forest management frequently affects the marten, but has much less of an effect on the fisher. Climate change is likely to benefit the fisher by facilitating snow conditions that are favorable to its movement. Forest management and climate change therefore benefit the fisher, to the detriment of the marten, which is facing habitat declines, increases in predation, and competition from the fisher and other carnivores.
The research team would like to thank all of those individuals who took the time to share their experience and passion with us. Thanks to the collaborators who facilitated the contacts with interviewees: Pascal Bibeau, Danny Bisson, Simon Charest, Julie Delfour, Pierre Fournier, Claude Grenier, and Jimmy Papatie. WFJ Parsons translated the manuscript.
This research was funded by the Fonds de recherche du Québec: Nature et technologies (FRQNT). The funding body played no role in the design of the study, in the collection, analysis and interpretation of data, or in the writing of the manuscript.
Availability of data and materials
PS, HA and LI designed the research project. PS performed the data collection and analysis, with inputs from all coauthors. PS, HA and LI drafted the paper. MC and PD provided theoretical inputs and comments on the draft manuscript. All authors read and approved the final manuscript.
PS is a biologist. She conducted this research within the framework of her Ph.D. in environmental sciences. HA holds the Canada Research Chair in Aboriginal Forestry. He has been involved in participatory research with indigenous communities for more than 12 years. LI and PD specialize in wildlife management and sustainable forest management. MC is in charge of research on terrestrial wildlife management, with the Quebec Ministry of Forests, Wildlife and Parks (MFFPQ).
Ethics approval and consent to participate
This project has responded to a request from Indigenous communities to investigate and better understand the reasons behind fluctuations in fisher and marten populations in their territories. We received a certificate to conduct this research involving human subjects from the Ethics Review Board of Université du Québec en Abitibi-Témiscamingue (#2015–04). The project was also approved by the Band Councils of the participating communities: Kitcisakik, Timiskaming First Nation, Kebaowek, and Wolf Lake. Each interview began with a presentation of the study’s context and a recall of the confidentiality protection measures. Free, prior and informed consent was obtained from the participants before beginning the interviews. Participants were involved in this research on a voluntary basis.
Consent for publication
The authors declare that they have no competing interests.
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