The Distribution of Woodland Caribou (Rangifer tarandus caribou) and Moose (Alces alces) in the Fort St. James Region of Northern British Columbia, 1800-1950 Domenico Santomauro B.A., University of Bologna, Italy, 2003 Thesis Submitted In Partial Fulfillment Of The Requirements For The Degree Of Master in Natural Resources and Environmental Studies The University of Northern British Columbia September 2009 © Domenico Santomauro, 2009 1*1 Library and Archives Canada Bibliothgque et Archives Canada Published Heritage Branch Direction du Patrimoine de l'6dition 395 Wellington Street Ottawa ON K1A0N4 Canada 395, rue Wellington Ottawa ON K1A 0N4 Canada Your file Votre r6f£rence ISBN: 978-0-494-60853-1 Our file Notre reference ISBN: 978-0-494-60853-1 NOTICE: AVIS: The author has granted a nonexclusive license allowing Library and Archives Canada to reproduce, publish, archive, preserve, conserve, communicate to the public by telecommunication or on the Internet, loan, distribute and sell theses worldwide, for commercial or noncommercial purposes, in microform, paper, electronic and/or any other formats. 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Conformement a la loi canadienne sur la protection de la vie privee, quelques formulaires secondaires ont ete enleves de cette these. While these forms may be included in the document page count, their removal does not represent any loss of content from the thesis. Bien que ces formulaires aient inclus dans la pagination, il n'y aura aucun contenu manquant. M Canada ABSTRACT The Distribution of Woodland Caribou {Rangifer tarandus caribou) and Moose (Alces alces) in the Fort St. James Region of Northern British Columbia, 1800-1950 By Domenico Santomauro Throughout the 1800s and the 1900s, woodland caribou {Rangifer tarandus caribou) disappeared from the upper Nechako lowlands of the interior of British Columbia, and herds in the surrounding mountain ranges contracted. Conversely, moose {Alces alces) populations expanded during the 1900s and rapidly colonized former caribou habitat. Using historical-ecological methods of research and Geographic Information System (GIS) software, I documented caribou and moose historical distribution and abundance, and examined the causative mechanisms that led to caribou decline. I gathered historical information from four sources: 1) secondary literature; 2) semi-structured interviews with aboriginal and non-aboriginal elders; 3) journals of the Hudson's Bay Company of Fort St. James; 4) other written primary sources. The findings of this study provide evidence of greater historical distribution and abundance of caribou, and confirm the value of Traditional Ecological Knowledge of First Nations (TEK) and of long-term historical perspectives for the study of ecological changes over time. ii TABLE OF CONTENTS Abstract ii Table of Contents iv List of Tables vi List of Figures vii Acknowledgement vii i Chapter One Chapter Two Introduction Research Background Thesis Structure Woodland Caribou Ecology Distribution and Abundance Overview of Threats to Caribou as Gathered From Scientific Literature Predation Natural Disturbance Fire Climate Change Disease and Insect-harassment Habitat Loss Due to Anthropogenic Influence Hunting Moose Ecology Distribution and Abundance Historical Ecology Local and Traditional Ecological Knowledge Study Area Morphology History Research Methods Introduction Secondary Literature Interviews Participants Preparation Fieldwork Research Progression Interviewing and Transcribing 1 1 3 4 4 5 ^ 7 8 8 8 9 9 10 11 11 12 13 15 17 18 19 26 26 27 28 28 28 29 29 31 iii Chapter Three Chapter Four Content Analysis Hudson's Bay Company Archives Other Written Evidence Organization of Results Maps and Timelines Evaluation Theoretical Underpinnings Evaluation Criteria Results Secondary Literature Archaeological Literature The Pre-Contact Period: Archaeology of Caribou and Moose Artefacts Anthropological Literature Ecological Literature Evaluation of Results from Secondary Literature Summary Interviews Caribou Knowledge Moose Knowledge Evaluation of Results from Interviews Summary Fort St. James HBC Post Journals Evaluation of Results from the HBC Post Journals Summary Evaluation of Results from Primary Written Sources Summary Summary of Findings Evaluation: Summary of Results and Comparison of the Sources Discussion Introduction Trends Amongst the Data Caribou in the 1800s: Evidence for Greater Abundance and Wider Distribution Caribou in the 1800s: Competing Evidence for Scarcity Moose in the 1800s Moose in the 1900s Historical Distribution and Abundance: Conclusions Caribou Moose Hypotheses of Caribou Decline Hypothesis One: Habitat Change Hypothesis Two: Increased Predation 33 34 35 36 38 39 39 41 43 43 43 ^ 47 49 50 52 55 55 55 59 63 66 66 70 73 81 83 84 86 90 90 90 90 93 94 96 98 98 99 100 101 103 iv Hypothesis Three: Habitat Loss due to Anthropogenic Influence and Industrial Activities Hypothesis Four: Over-Hunting Conclusions Potential Biases of Historical-Ecological Information Suggestions for Further Research Literature Cited Appendix I Result Tables, Interviews 103 105 108 110 111 113 129 Appendix II Collateral Information on the Historical Landscapes of the Study Area Gathered from Interviews. 134 Appendix III Result Tables, HBC Journals 136 Appendix IV Result Tables, Other Written Sources 137 Appendix V Interview Guide 141 Appendix VI Interviewee Informed Consent Form 142 Appendix VII Band Consent 144 v LIST OF TABLES Table 2.1 Ethnic identity of persons selected as potential interviewees of the project. 30 Table 2.2 Distribution of completed interviews for Tl'azt'en, Nak'azdli and nonaboriginal participants. 31 Table 2.3 Example of statement gathered from the HBC journals organized in a result table (See Appendices I-IV for full tables). 37 Table 3.1 List of caribou and moose artefacts from the Athapascan Collection of the National Museum of Civilization (Gatineau, Quebec). 48 Table 3.9 Comparison of the individual qualities of the sources of data employed in this project, based on the four criteria of evaluation outlined in section 2.8 (Evaluation Criteria). 87 * vi LIST OF FIGURES Figure 1.1 Distribution of woodland caribou herds across British Columbia (2008), including boundary of historical distribution (BC Ministry of Environment). 23 Figure 1.2. Telemetry locations of present caribou populations within the study area of the Takla (Poole et al., 2000), Wolverine (Johnson et al., 2002) and Chase herds (Wood and Terry, 1999). 24 Figure 1.3 Study area and boundaries of the traditional territory (T.T.) of the Tl'azt'en and Nak'azdli First Nations. The borders of the study area approximately correspond to the geographic range of the information provided by the four sources of data. 25 Figure 3.2 Caribou scraper photographed in the house of interviewee #6 during the 48 interview session. Reproduced with permission of Interviewee #6 Figure 3.3 Timeline of caribou and moose historical observations gathered from the interviews with local aboriginal and non-aboriginal elders. 61 Figure 3.4 Caribou and moose historical observations gathered from the interviews plotted on a map of the study area using GIS software. 62 Figure 3.5 Timeline of caribou and moose historical observations gathered from the HBC journals of Fort St. James. 68 Figure 3.6 Caribou and moose historical observations gathered from the HBC journals of Fort St. James plotted on a map of the study area using GIS software. 69 Figure 3.7 Timeline of caribou and moose historical observations gathered from other written sources. 79 Figure 3.8 Caribou and moose historical observations gathered from other written sources plotted on a map of the study area using GIS software. 80 Figure 4.1 Master timeline of historical observations of caribou and moose 91 derived from semi-structured interviews with local aboriginal and nonaboriginal elders, HBC journals of Fort St. James, other written sources and secondary literature. Vll Acknowledgement Field Research was funded through the BC Real Estate Foundation Partnering Fund, a partnership generated by an endowment to the University of Northern British Columbia to assist faculty and students in obtaining and leveraging funding for research. UNBC and the Real Estate Foundation of BC share a mutual interest in advancing practices for the use and conservation of land that enhance the social, economic and environmental well-being of northern communities. My sincere thanks go to Gail Fondahl and Christopher Johnson, supervisors of this project, for their continuous support, encouragement and patience. I would also like to thank Ted Binnema, member of my Committee, for his ideas and support in the writing of the thesis. I am greatly indebted to the Tl'azt'en and the Nak'azdli First Nations for the great experiences and the help received during fieldwork, and in particular to Walter Joseph Jr., Ron Winser, Veronica Campbell, Kateri Haskel and Beverly Bird for having gone out of their way in assisting me with this research. In addition, I am grateful to the staff at the John Prince Research Forest for their logistic support at the Cinnabar Resort and as experts in this research, and the staff at the Fort St. James National Historic Site for their courtesy. I would also like to thank Annick Pereira of the UNBC International Exchange & Student Programs International Center, the UNBC graduate students and all friends attending the University of Northern B.C. for the welcoming environment and the friendship provided during the course of my studies. Finally, my heart and most sincere thanks go to my wife Claire for the exceptional support received and patience shown throughout the course of this long project. Without her help, this thesis would have not been completed. My love and gratitude also go to my parents, who always granted me their tremendous support and care, and to Claire's parents, who always remind me that everything in life is possible. viii 1. INTRODUCTION 1.1 Research Background Woodland caribou (Rangifer tarandus caribou) are an important part of the natural environment and the cultures of the indigenous peoples of northern Canada (Hare et al. 2004). In the status report produced by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC, 2002), caribou have been described as 'virtually endemic to Canada', and part of the cultural heritage of First Nations and of all Canadians. Today, the persistence of this species in many provinces is threatened by habitat loss, hunting, disturbance and increased predation (Cumming and Beange, 1993; Rettie and Messier, 1998; Schaeffer, 2003). Across British Columbia (BC), woodland caribou are classified into three ecotypes: mountain, northern, and boreal caribou (Heard and Vagt, 1998). Northern caribou historically populated the upper Nechako lowlands of the interior, the study area for this project. Over the course of the last two centuries, however, these populations disappeared from the lowlands, and contracted into the surrounding mountainous regions (Spalding, 2000). The historical dynamics and direct causes of this decline are unknown. Since prehistory, Athapascan First Nations, specifically the northern Carrier, occupied the upper plateau. Caribou still figure in their cosmology and Traditional Ecological Knowledge (TEK) as a powerful symbol and means of sustenance (Hall, 1992; Nak'azdli Elders Society, 2001). The year 1806 witnessed the arrival of European traders in the area, and the founding of the Fort St. James post of the Hudson's Bay Company (HBC) on the southern shores of Stuart Lake. In the early records of the Fort, caribou, though 'scarce', are described as present. 1 Additional primary evidence further confirms the occurrence of caribou in lowlands areas, and provides clues to their greater distribution and abundance over the course of the 1800s and the first half of the 1900s. The causes of woodland caribou decline in the study area and more generally in North America have been the subject of much debate in recent years (Bergerud, 1974; Bergerud, 1988; Seip, 1992; Cumming et al., 1996; Hatter et al., 2000; Schaefer, 2003; Wittmer et al„ 2005). As demonstrated by comprehensive studies on species' decline, a combination of factors, frequently too small to be recognized as independent agents of change, may act concurrently to influence persistence (LoGiudice, 2006). In the lowlands of the study area, survival of normally lowdensity populations likely was dictated by forage availability and the distribution of predators. Environmental change, either natural or anthropogenic, and other human influences rendered habitats unsuitable and increased the numbers of predators forcing caribou to move from once traditional areas (Spalding, 2000). In this project, I employed three local primary sources of historical evidence and interviews with First Nations to document the ecological history of the study area. In particular, I focused on the changes in distribution of woodland caribou and moose. Historical evidence and Traditional Ecological Knowledge offer insight into long-term ecological processes that cannot be obtained through other sources (Huntington, 1998; Saenz-Arroyo et al., 2006). Their use and application in ecology, however, involves a process of integration of non-scientific information into a scientific framework of research. The nature of historical-ecological data often requires the design of project specific analytical methods that are premised on in-depth knowledge of social science techniques (Huntington, 1998, 2000). Furthermore, historical information may not be available, or the sources may be too fragmented to be useful (Swetnam et al., 1999). Therefore, 2 the second objective of this study consisted of an evaluation of the sources of historical information that I reviewed. I developed a standard set of criteria that allowed a relative comparison of the spatial and temporal precision, richness of content, and barriers to application of Hudson's Bay Company journals, written historical evidence, secondary sources, and interviews with long-term knowledge holders. The time frame chosen for this project extends from 1800 to 1950. This period was critical in the life history of local caribou, as new European explorers entered the study area in 1806, followed by settlers later in the 1800s and industrial activities in the 1900s. The arrival of European explorers and the establishment of the HBC Fort on Stuart Lake provide the first written records on local environments and wildlife. The end point of the study recognizes the advent of modern techniques of scientific investigations, including aerial surveys. 1.2 Thesis Structure This thesis is organized into four chapters. The Introduction (Chapter One) provides a review of the essential background literature related to the ecology and known history of moose and caribou in the study area, the discipline of historical ecology, and the characteristics of Traditional Ecological Knowledge. In Chapter Two, Methods, I explain the processes, methods and criteria employed to collect and evaluate information from the four sources of data I employed. In Chapter Three I present the historical observations of caribou and moose in the study area, and I offer an evaluation of the information contained in each source. I organized the results to address the two primary research questions that underlie the thesis: 3 1) How did the distribution of caribou and moose change in the Fort St. James region between the years 1800-1950? 2) How do the sources of historical data vary in content and precision, and contribute to our understanding of the nature of these changes? What are the relative strengths and weaknesses of each source for describing the changing distribution of caribou and moose in the region? In Chapter Four, I explore and discuss the patterns and themes identified in the results. I highlight observations and records that improve our understanding of the long-term dynamics of caribou and moose in the study area. I conclude the thesis with suggestions for further research. 1.3 Woodland Caribou Ecology Caribou of BC are grouped into three categories based on distribution, habitat requirements and behaviour: northern, mountain and boreal ecotypes (Heard and Vagt, 1998; Spalding, 2000). The mountain ecotype inhabits the southern interior of the province and the mountain ranges of the southeastern central interior. The northern ecotype ranges across the northern boreal mountains and plains and the sub-boreal interior. The boreal ecotype is restricted to the forests of the northeast lowlands. My research is focused on the northern ecotype, classified as Threatened by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC, 2002) and Blue listed by the BC Conservation Data Centre (2008). Northern caribou migrate two times per year, in the fall to lower altitudes where they winter, and in the spring and summer to intermediate and higher altitudes, often in heavily 4 vegetated stands, where they birth their young (Hatter et al., 2000). Rutting season is between October-November, and calves are born in late spring. Each cow generally nurtures one calf per year. The ability to space away from predators and the availability of winter forage are critical factors influencing the annual distribution of woodland caribou (Schaefer et al., 2000; Johnson et al., 2001; Johnson et al., 2004). In the winter, caribou forage for terrestrial lichens in open patches of old forest at lower elevations or on alpine windswept slopes (Johnson et al., 2001). During snow-free months, caribou feed on a variety of species of grasses, shrubs, sedges, twigs, mushrooms, and on leaves of willow and dwarf birch at all elevations (BC Conservation Data Centre, 2008). Distribution and abundance During the past two centuries minor changes occurred in the distribution of caribou north of 55° N. In southern and central regions, however, caribou experienced significant range contractions (Heard and Vagt, 1998; Hatter, 2000; Hatter et al., 2004). Presently, the central interior of the province, from Quesnel to Fort St. James, has no caribou populations, though caribou are present in the bordering mountain ranges located east and north of the upper section of the plateau (Figure 1.1 and 1.2). A note of caution is necessary, however, in defining populated and unpopulated areas. Since home range is described as 'the sum of an animal's movement' (Hins et al., 2009) it is possible that remote areas defined as 'unpopulated' are, or were, in fact, periodically inhabited by caribou. Lack of data for remote areas also confounds estimates of caribou numbers, especially in a historical context. Estimates of the total number of caribou in BC for the early 1900s and pre-contact times vary considerably. Ritcey (1991) supposed there were approximately 30,000-40,000 caribou in 5 the province at the time of first European contact. MacDonald (1996) estimated that there could have been as many as 80,000 at the beginning of the 1900s. In recent times, Spalding (2000) suggested there were approximately 16,500 caribou in the late 1990s, while Heard and Vagt (1998) presented a higher figure of 18,000. Within or just outside the boundaries of my study area caribou are mainly concentrated in two herds, the Wolverine and the Takla; the Chase herd, composed of an estimated 400 to 1100 animals, inhabits the farther corners of the northern sections of the study area. The Wolverine caribou occupy the areas of Omineca Provincial Park (including the Wolverine Ranges) and parts of the Swannel ranges in the northern and northeastern portions of the study area. The Takla Lake herd, in reality a mosaic of fragmented sub-populations, inhabits the ranges surrounding Takla Lake (Hogem, Takla, and Mitchell ranges). The habitat ecology of the Takla population was studied by Poole et al. (2000). These authors observed that Takla caribou share characteristics typical of both mountain and northern caribou. They concluded that low elevations are avoided throughout the year, except in spring, while higher and medium elevations in forested and alpine areas are occupied during all seasons. A total of 102 caribou were counted in 1998, of which 39 were on the Takla range, 16 on the Mitchell range and 52 in the mountains surrounding Mt. Sidney Williams. The Wolverine herd was assessed by Terry and Wood (1999) and Wood and Terry (1999) and later by Johnson et al. (2001, 2002). These authors highlighted the importance of habitats composed of mature lodgepole pine forests interspaced with wetlands. This herd was estimated at between 260 to 560 caribou (Terry and Wood, 1999). 6 1.4 Overview of Threats to Caribou as Gathered from Ecological Literature Predation Predation is recognized as a primary factor limiting forest-dwelling caribou populations (Bergerud and Elliot, 1986; Bergerud, 1988; Messier, 2000; Wittmer, 2005). The main predators of caribou are humans, wolves (Canis lupus), grizzly bears (Ursus arctos) black bears (Ursus americanus) and cougars (Felis concolor) (Paquet, 2000). Though wolves are in most cases identified as the primary predator of caribou, research has shown that in certain instances the impact of bears on caribou can be slightly less and sometimes equal to that of wolves (Boutin, 1992). Cumming et al. (1996) hypothesized that predators limit populations of caribou and moose to a density of about 0.4/km2, well below nutritional carrying capacity. Following the removal of wolves in the Muskwa-Kechika area of BC, Bergerud and Elliot (1998) noted that densities of caribou and moose increased to 1/km2 and 1.5/km2, respectively. The link between caribou, moose and wolves is important for understanding the decline of woodland caribou (Seip, 1992; Seip and Chichowsky, 1996; Poole et al., 2000; James et al., 2004). As previously mentioned, the ability to space away from predators and the accessibility of winter forage are critical factors determining the distribution of woodland caribou (Schaefer et al., 2000; Johnson et al., 2001). Favourable caribou habitat includes old-growth forests at a range of elevations and windswept alpine slopes (Terry and Wood, 1999; Poole et al., 2000; Johnson et al., 2002). In contrast, moose choose locations closer to settlements, at moderate elevations, near wetlands and in areas characterized by recent fire (Loranger et al., 1991; Nielsen et al., 2004; Maier et al., 2005). In the 1900s, the northward expansion of industrial development and settlements created more moose habitat, particularly in valley bottoms and at the expense of old-growth forests and 7 caribou habitat. The resulting expansion of moose triggered a density-dependent response by wolves, increasing in numbers and switching to moose as primary prey (Wittmer et al., 2005). As a result, caribou suffered higher mortality from wolves in habitats that were adjacent to highdensity moose populations (James et al., 2000). Natural disturbance Fire Large wildfires have the potential to destroy caribou habitat and displace populations (Klein, 1982; Schaefer & Pruitt, 1991). At the same time, fire has been a natural agent of renewal of boreal and sub-boreal forests for thousands of years (Hawkes et al., 1997; Wong et al., 2003). Intermittent fire favours the long-term distribution and productivity of lichens. Historical fireregimes in BC have been analyzed by Bergerud (1974), who concluded that there is "no evidence that fires increased with early settlements" (Bergerud, 1974, p. 758). Nevertheless, the hypothesis that fires contributed in some degree to local caribou declines cannot be completely disqualified, as historically fire regimes have been highly-variable in frequency, size and severity (Wong et al., 2004). Climate change Grayson and Delpech (2001; 2005) using archaeological data for Pleistocene reindeer in southern France have assessed the potential effects of climate change on caribou. Their research has shown that periods of warming corresponded to decreases in caribou range, possibly caused by changing vegetation patterns and insect harassment. Further studies on present climate change have highlighted how alterations of atmospheric phenomena are more pronounced in the north, 8 and can influence the vegetation and life history strategies of affected animal species (Dormann and Wooding, 2002; Weladji et al., 2003). We can only speculate, however, how variation in climate patterns might have affected historical populations. In the 1850s, the study area seems to have been recovering from a 'little' ice age (Hudson, 1983; Thompkins, 2007). It is possible, therefore, albeit difficult to prove, that milder conditions affected general trends of persistence of caribou in the study area. Disease and insect-harassment Although there is little evidence, Spalding (2000) suggested that disturbance from parasitic insects and disease, though potentially deleterious (Weladji et al., 2003), had no affect on populations of caribou in the study area. Habitat loss due to anthropogenic influence Since the advent of settlers in North America, anthropogenic disturbance has played a primary role in the life history of woodland caribou. Today, caribou habitats are increasingly threatened across Canada by an intensification of human activities such as road-development, agriculture, logging, mining, oil and gas exploration and recreation (Schaefer et al., 2003; Vors et al., 2007). Human activities can directly influence caribou through loss of habitat, avoidance of human structures and corridors (Oberg, 2001; Vistnes and Nellemann, 2001; Dyer et al., 2002), and indirectly by facilitating the distribution of alternate prey and associated predators (see Predation). 9 Hunting Over-hunting and poaching can contribute to severe declines in caribou populations (Bergerud, 1974). The removal of caribou increases with the opening of roads and other access corridors used by hunters and possibly by predators (James, 1999). During the course of a review of caribou management practices in BC, Bergerud (1978) observed that the decline in the number of caribou across the province (-10,000) was approximately equal to the total harvest since 1970 (Bergerud, 1978, p. 98). He suggested that hunting might have been the cause of the decline. From Bergerud's (1974) perspective, caribou are easily hunted as they periodically migrate over the same areas and are susceptible to firearms. Blehr (1990) examined the belief held by zoologists, pre-historians and anthropologists that caribou are easily hunted. He is careful to differentiate traditional hunting as practiced by First Nations and modern hunting using firearms. Blehr (1990) stresses that despite the best abilities of bow-hunters, the range of these two weapons is not comparable. Secondly, the success of native efforts in communal drives of caribou, a practice often used in tundra environments, highlights the necessity of large numbers of people to secure caribou meat. Individual hunters, unless in the presence of massed herds at which to shoot directly, would have difficulties hunting and killing caribou. While the practice of communal drives was never adopted in the study area, Blehr (1990) underlines the difficulties of hunting caribou without the aid of modern weapons, thus emphasizing the deleterious effects that the introduction of firearms had on caribou. Sherry and Myers (2002) debate this point by arguing that little evidence supports contentions that primitive technology prevented First Nations from over-hunting; instead, harvest levels were controlled by community norms and rules (Sherry and Myers, 2002). The presence of rules controlling harvest levels and the belief that First Nations resource management was sustainable have been disputed 10 by several authors, who support the idea that native hunters played a much greater role in the limitation and control of species during pre-settlement times. Kay (1994, 1997) suggested that Native Americans not only limited species numbers in unregulated fashion, but also purposefully structured entire animal and plant communities. Martin and Szuter (1999) and Laliberte and Ripple (2003) used the Lewis and Clark journals to demonstrate how animals living in areas of higher native influence were less likely to persist. In conclusion, it is likely that aboriginal and non-aboriginal hunting alike played a role in the life history of caribou, although the importance of hunting during historical times for the study area is uncertain. 1.5 Moose Ecology Moose experienced rapid growth in population size and distribution during the 1900s in most ecoregions of Canada and Alaska (Ritcey, 1982; Spalding 1990). vegetation and snow in the north and by heat in the south. Their range is limited by Moose winter range occurs in secondary forests created by disturbance such as wildfire or logging (Nielsen et al., 2004; Maier et al., 2005). In the winter, the diet of moose consists primarily of willow (Salix alba), twigs and woody stems of various plants, while in the summer aquatic plants, serviceberry (Amelanchier alnifolia), maple (Acer campestre), birch {Betula pubescens), red osier (Cornus sericea) and aspen (Populus tremula) leaves are consumed. Rutting takes place between September and October and calves, typically one per female, are born between May and June (Blood, 2000). Moose predators are mainly wolves, black and grizzly bears, while wolves are generally recognized as the primary predator, bears can regulate moose populations in some areas (Boutin, 1992). 11 Distribution and abundance Currently, there are approximately 170,000 moose in the province of BC (Blood, 2000). The number of moose present in BC before the 1900s is, however, the subject of debate. Beginning in the 1900s, logging, industrial development, and wildfire opened the way to moose 'expansion' and 'colonization' of the interior ofBC: In many areas to the north of latitude 54, as well as in most localities to the south, it must be concluded therefore, that moose were absent, whereas in others the populations were small and did not increase until after the advent of settlers one hundred years later (Hatter, 1950; p. 56). A number of researchers have argued for the absence or rarity of moose in BC before the late 1800s and the 1900s (Racey, 1936; Hatter, 1950; Bergerud and Elliott, 1986; Kay, 1997). Racey (1936) reports that moose moved from the north and the east into the Chilcotins and that these animals were unknown to the local natives until the early 1900s. Hatter (1950) used historical evidence gathered from several areas of British Columbia to conclude that moose were either absent or very scarce in central and northern BC before the 20th century. Bergerud and Elliot (1986) maintain that moose were absent from the southern and central regions of BC before the 1900s. These conclusions are somewhat supported by more contemporary evidence of the expansion of moose into the coastal areas of BC following habitat modification (Darimont et al., 2005). Spalding (1990), however, rejects the hypothesis of a rapid colonization by moose; using historical evidence, he demonstrates that moose were already present in the province in the 1800s. Moose of the sub-boreal interior (including the study area) were, in his view, scarce at the time of Alexander Mackenzie, but "by the 1860s, moose had begun to increase; by the 1870s early accounts indicate moose were numerous, particularly in the eastern half of this eco-region" (Spalding, 1990, p. 5). 12 1.6 Historical Ecology A longer-term and more comprehensive understanding of caribou decline requires the thoughtful consideration of the role of nature and humans in a historical context. This is not a novel idea. In the early 19th century, the naturalist Henry David Thoreau came to recognize that much of what he sought to explain in nature was influenced by its history, which often included human activity (Foster, 2002). Today, environmental conditions have become a significant component in the narration of history, anthropology and other disciplines concerned with the study of past phenomena (Moran, 1990; Pointing, 1992; Rival, 2002). Within the environmental sciences and conservation, the drive from centralized to adaptive management, and from single to multidisciplinary approaches has further expanded historical-environmental applications into a wide range of scientific practices (Wimberly, 2002; Weber et al., 2001; Jannuzzi and Ludwig, 2005; Lawson et al., 2005). In ecology, the use of historical evidence and methods premised in the social sciences prompted the designation of a new sub-discipline, historical ecology. The latter may be defined as 'the use of historical knowledge in the management of ecosystems' (Swetnam et al., 1999), though such a definition limits this research approach to the use of historical data and offers no mentions of its objectives. A more detailed explanation is offered by Crumley (1994), who defines historical ecology as the study of natural and anthropogenic changes occurring over the landscape in time and space. For Crumley (1994, 2003), landscapes are the multidimensional bearers of all natural and cultural signs. Within them, humans are mechanisms of change integrated into natural dynamics (Balee, 1998). 13 This second definition is widely shared amongst current authors promoting historical ecology as a holistic approach to the study of natural and anthropogenic phenomena over long periods (Crumley, 1994, 2003; Rival, 2002, 2006; Balee, 1998, 2006). This is the description of historical ecology that I adopted for my project. I apply this concept neither as a technique nor as paradigm, rather as a philosophy of research that embraces a holistic, diachronic analysis of living ecological systems (Rival, 2006). The validity of historical-ecological research has been demonstrated in a number of studies with similar characteristics to this project. Blackstock and McAllister (2004) employed primary evidence and First Nations perspectives to reconstruct the past conditions of grasslands of the interior of BC. In fish management, Mackinson (2001) offers examples of integration between local and scientific knowledge, while Saenz-Arroyo et al. (2005; 2006) reconstructed old marine ecosystems of the Gulf of California for conservation purposes using accounts of early explorers, fishers' anecdotes and naturalists' observations. These studies highlight the benefits of research premised in the techniques and theory of historical ecology. Historical-ecological research attempts to defy the dualism between nature and humans characterizing traditional western worldviews (Goodison, 1990; Willems-Braun, 1997). Ecological and cultural phenomena are analyzed in their completeness without cultural prejudices, and using a wealth of different perspectives. These studies consistently employ historical evidence, Local Ecological Knowledge (LEK) or TEK of First Nations to gain holistic understanding of natural phenomena. The application of multiple knowledge sources can provide a much richer understanding of historical phenomena, from both a temporal, spatial, and thematic perspective. 14 1.7 Local and Traditional Ecological knowledge In this research, I employed TEK of First Nations and LEK of non-aboriginal contributors to gather information on the long-term dynamics of caribou and moose found across the study area. As previously mentioned, these alternative forms of knowledge are now consistently employed in several aspects of environmental and resource management. Despite their currency, however, there is a lack of specific definitions of TEK and LEK, and how they should be implemented (Usher, 2000). I provide a definition of these terms that is pertinent to this research, and then highlight some of their individual features. TEK can be defined as "a cumulative body of knowledge, practice, and belief, evolving by adaptive processes and handed down through generations by cultural transmission, about the relationship of living beings (including humans) with one another and with their environment" (Berkes, 1999). Usher (2000) distinguishes between four categories of TEK, of which two can be applied to all forms of LEK: factual knowledge about the environment and factual knowledge about past and current use of the environment. differentiate TEK and LEK. The remaining two categories, however, These categories are: cultural and societal rules about the environment, and the environmental worldviews from which cultural and societal rules originate and are based. TEK and LEK are differentiated by the cultural setting from which they originate, and by the time-depth of factual knowledge about the environment that characterizes them (Berkes et al., 2000). These differences are rooted in the concept of indigeinity. The term indigenous is applied in ecology to organisms native to a particular place or ecosystem. In this study, I choose to apply this definition to culture, and thus to associate TEK with Indigenous Knowledge (IK) and the native communities of the study area, and LEK to the knowledge of nonnatives, whose culture and practices are of European descent. Therefore, the separation between traditional and local forms of knowledge and western scientific ecological knowledge is based largely on different worldviews and practices, as "western science is a cultural entity itself, one of many subcultures of Euro-American society" (Carter, 2008, p. 18). The fishermen and their knowledge, described in the studies of Bergmann (2003) and Saenz-Arroyo et al. (2005), provide excellent examples of how different views of the natural world characterise different knowledge systems, even within the same culture. Local forms of knowledge and TEK have been extensively integrated in scientific studies, natural resource impact assessments and in wildlife monitoring (Yesner, 1988; Messier and Ferguson, 1997, 1998; Pierotti and Wildcat, 2000; Harris and Wasilewsky, 2004; Lyver and Lutsel Ke Dene First Nation, 2005). As both forms of knowledge are based on information and are constructed over many years, their application in science often offers much needed historical field observations. In ecology, LEK and TEK are valuable instruments of long-term monitoring. For example, techniques used by the Desenoline First Nations to monitor the movements of barren ground caribou (Rangifer tarandus groenlandicus) were employed by scientists to understand how bifurcation points created by mineral exploration affect the distribution of caribou (Parlee and Manseau, 2005). Other studies include community-based monitoring initiatives such as the Arctic Borderland Ecological Knowledge Co-op (Arctic Borderlands Coop, 2004). Despite the currency that TEK and LEK enjoy in contemporary research, their application in ecological studies is impeded by a number of obstacles. Sherry and Myers (2002) identify such issues as "myths" while Usher (2000) discusses how the lack of clear definitions and guidance hamper the wider application of TEK in management and conservation. TEK's format, the complicated process of data collection and the challenges involved in its integration in science 16 often tip the scale in favour of more established scientific practices of research (Pierotti and Wildcat, 2000). 1.8 Study Area Morphology My project focuses on the upper Nechako Plateau, located in the northern interior of BC, Canada. This area incorporates the Nechako lowlands, to which I will refer throughout this manuscript, though the latter definition is not representative of the variety of environments characterizing the study area. Fort St. James, the main settlement within the area, is approximately 100 km from Prince George. The Tl'azt'en and Nak'azdli Nations band offices are located respectively in Tache (approximately 45 km from Fort St. James, on the east shore of Stuart Lake) and adjacent to the town of Fort St. James (Necoslie). The boundaries of my study area are drawn according to the traditional territories and occupancy range of the First Nations on which this research is based, and the perceived sphere of influence of the HBC post of Fort St. James (see Figure 3). The borders include the northern side of the upper Nechako watershed east of Babine Lake, the mountainous regions surrounding Stuart and Takla Lakes and the areas immediately north of the Nation Lakes. In the south, the limit of the study area is the junction of the Stuart and Nechako Rivers; Carp Lake and Manson Lakes delimit the eastern boundary. The study area is characterized by a highly variable topography. The lowlands around Stuart, Beaver, and Carp Lakes feature a relatively flat post-glacial topography and numerous wetland areas. The uplands range from 750 to 2000m, and include the southern fringes of the Omineca and Skeena Mountain ranges and the Hogem, Swannel and Mitchell ranges. While the 17 uplands still host caribou, the lowland populations disappeared over the last 100 years (Spalding, 2000). Several hydrographical features mark the landscape, including the Stuart, Trembleur, Takla, Pinchi, Tezzeron, Inzana, Cunningham, Bear, Tsyata, Tchentlo, Chuchi, Witch, and Great Beaver lakes; and Stuart, Tache, Middle and Nation rivers draining into the Fraser River system. A number of small lakes and creeks drain into the Peace system. Trees mainly consist of white and black spruce (Picea glauccr, Picea mariana), fir {Abies lasiocarpd), lodgepole pine (Pinus contorta), trembling aspen {Populus tremuloides) and western white birch {Betula papyrifera). Large fauna include, but is not limited to: moose, caribou, elk {Cervus elaphus), mule deer {Odocoileus hemionus), mountain goat {Oreamnos americanus), coyote {Canis latrans), wolf {Canis lupus), black and brown bear {Ursus americanus', Ursus arctos). Being connected to the Fraser River system, most lakes and rivers contain abundant populations of salmonids and other species of fish. Cold and moist snowy winters and mild summers characterize the climate of the region, with variation between elevations and geographic position. The Nak'azdli Band and the Tl'azt'en Nation are considered to be part of the central Carrier linguistic group, and to belong to the northern Carrier. As the Carrier aboriginals of the interior refer to themselves as 'Dakelh', I will use this latter term in this manuscript. The terms Dakelh, as Carrier, refers to both people and their language, the Dakelh. Nak'azdli is translated in Dakelh as 'where the Stuart River begins to flow' (i.e. the southern shore of Stuart Lake), while Tl'azt'en is 'people at the edge of the bay' (i.e. the northeastern shore of Stuart Lake). Both First Nations are culturally distinct, though similar in cultural attributes, to the central and southern Dakelh to the south and the Sekani to the north. 18 History The native occupants of BC are thought to have populated the province using a land bridge that connected Siberia and Alaska in the late Pleistocene (15,000 to 20,000 years Before Present (BP)); though there are alternative hypotheses suggesting that North America was colonized by sea (coastal theory) or had been occupied well before then (Jablonsky, 2002). The northern expanses of American continent were heavily glaciated until 14,000 years BP, when the retreat of the continental ice sheets progressively began to open tracts of land. Between 12,000 to 10,000 years BP, warmer and drier conditions allowed a Paleo-Indian culture to spread across the areas free of ice (Wright, 1995). The subsistence of early people likely depended on large mammals such as caribou, elk, moose, deer and possibly buffalo in the south. People in small, mobile, nomadic groups hunted animals. Salmon was initially unavailable because of the residual effects of glaciations on rivers. In BC, the area of the interior spanning north along the Fraser River system is identified as the plateau. This vast region is characterized by a diverse topography, and has long supported a high degree of natural and cultural regionalism. Specifically, north-south movements of indigenous peoples characterized the interior of BC, with contact on the plains in the east and the coastal Paleo-Indians in the west (Borden, 1954; Kobrinsky, 1968). The continuous melding between cultures influenced subsistence and customs, and created common cultural features used by archaeologists to develop the definition of plateau culture. People occupying the plateau became semi-nomadic with the advent of salmon fishing between 10,000 to 4,500 years BP. The Drynock site near Kamloops dated 7,500 BP, shows that salmon fishing was beginning to play a larger role in the lives of the early people. By 4,500 BP, the interior began to develop what is described as the pit house tradition (Wright, 1995). Large 19 forests now covered most of the areas due to cooler and moister climate conditions, and subsistence focused on the salmon run in late summer and hunting and gathering throughout the rest of the year. The current inhabitants of the study area, the Dakelh, likely moved to their present location relatively recently. Donahue (1975) stresses the adaptability of Athapascan, including the Dakelh, to new cultures and environments. Some have hypothesized that their migration to the plateau was associated with the White River volcanic eruption and ash fall in the Yukon, which occurred around 1,500 years BP (Wright, 1995); although there is no definite proof of the timing of their arrival in the region. In pre-contact times, the Tl'azt'enne and the Nak'azdli lived as hunter-gatherers in a fashion similar to that of other First Nations of BC. During the summer months, villages near waterways and lakes were occupied for spring fishing and for the salmon run. In the winter, family groups scattered throughout the country for hunting and trapping (Bond and Russell, 1992). Trade was conducted to and from the coast with the neighbouring Tsimshian, with the Sekani, and with other Dakelh Nations. Historically, the primary source of subsistence for the northern Dakelh was fish. Salmon was collected in large quantities, usually in late August, dried in racks and used throughout the winter, while other freshwater species were taken in the fall and in the winter (Morton, 1988). After fish, small game was most important. Beaver (Castor canadensis), marmot (Marmota caligata), muskrats (Ondatra zibethicus) and other fur-bearers were gathered using traps and snares. Larger animals such as black bears and lynx (Felis lynx) were taken using pits and deadfalls (Hudson, 1983). Apart from caribou and moose, large herbivores used in traditional 20 subsistence also included mountain goats, white tailed deer (Odocoileus virginianus), and possibly elk (Cervus elaphus) (Hall, 1992). European explorers first entered the study area in the early 1800s. In the late 1700s, the competition between the HBC and the North West Company triggered a new wave of exploration of the territories west of the Rockies. In the fall of 1805, Simon Fraser, in company of John Stuart and James McDougall, retraced Mackenzie's route up the Peace River, taking his party to McLeod Lake (formerly known as Trout Lake). After receiving a positive reception from the Sekani inhabiting the region, Fraser established the McLeod Lake Fort. In 1806, McDougall examined the territory to the west, the land of the Dakelh. In May 14 of the same year, Fraser, at McLeod Lake, received the first report of Stuart Lake. Fish were described as "abundant in certain seasons of the year, fur animals are plenty, but large animals scarce" (Lamb, 1966, p. 1517). On July 26, 1806, Fraser descended the Fraser to the mouth of the Nechako River and thence arrived at Stuart Lake. The post of Fort St. James was established there shortly after. Several authors (Mardsen and Galois 1995; Harris 1997; Brown 2002; Morris and Fondahl, 2002) have described the dynamics involving the loss of aboriginal sovereignty over lands and natural resources following the establishment of the fur trade during the 1800s and the 1900s. In the first two decades of the 1900s, the decline of the fur-trade in Stuart Lake signalled the beginning of a new system of governance in the region, during which the provincial government further limited First Nations' use of local natural resources (Klippenstein, 1992). The expansion of industrial activities in the northern interior of BC in the first half of the 1900s brought railways, logging, mining, and progressively substituted hunting, trapping and fishing with wage-labour (Brown, 2002). In the 1960s, the larger forest companies of the Prince George 21 area switched modes of productions from selective logging to modern forestry practices, dramatically changing local landscapes and local First Nations' lives (Morris and Fondahl, 2002). 22 Legend B.C. Boundaries Caribou Distribution STATUS '^//z Extirpated HI [ Herd | Trace occurrences Figure 1.1. Distribution of woodland caribou herds across British Columbia (2008), including boundary of historical distribution (BC Ministry of Environment). 23 Legend Caribou Herd • Takla X Wolverine I Chase Protected areas • Water — Roads Figure 1.2. Telemetry locations of present caribou populations within the study area of the Takla (Poole et al., 2000), Wolverine (Johnson et al., 2002) and Chase herds (Wood and Terry, 1999). 24 r— Williston V ! H g g ^ t f N vi-, \ n , % Ranges i : I£ O- \ •N 'v; Swannel Ranges hc/a/ . [1 , Wl,.... V-" I Nation Lakes A/af/" 7. • I /y.y+kz: \ \ s- hs\V \f. ' % -< A a" V t •• ^ M ^ S S s ^ . -4, > v .. Dzitl'ainli Middle River Mt Sidney -1*—U • V* W k ! ^ . c - , N e c h a k o • *\ • ^ . - -f 'l Pa/ ta et eaa ii A /l -» • : Tache ,, ^ * V , . - -asir f : < C i n n a b a r Resort (UNBC) -x - ^ m r ^ C i i SttimSt, Babfoe ta/cev^inche L a k e ^ A F l J ^ i : * '--.u.' | ^^ ^ V ^ . J t Fort St. James ^ : - ^ x -V ^ Legend # ^ Necoslie , Study Area Research Locations Water Features Roads Tl'azt'en T.T. Protected Areas Contour Lines Nak'azdli T.T. Figure 1.3 . Study area and boundaries of the traditional territory (TT) of the Tl'azt'en and Nak'azdli First Nations. The borders of the study area approximately correspond to the geographic range of the information provided by the four sources of data. 1 Borders of the Tl'azt'en and Nak'azdli First Nations traditional territories have been created using the maps found in the Carrier Sekani Tribal Council website (CSTC 2008; http://www.cstc.bc.ca/cstc/l/cstc+homepage) and edited using Corel Draw™ Ver. 11. 25 2. METHODS 2.1 Introduction Primary written evidence and results from interviews were collected, analyzed and interpreted using a combination of qualitative and quantitative techniques founded on grounded theory. This methodological approach is defined as a theory emerging from the data, following a process in which "data collection, analysis, and eventual theory stand in close relationship to one another" (Strauss and Corbin, 1998, p. 12). As the name suggests, the shaping of the theory begins during the process of data collection and analysis. Initially, patterns and themes are identified from the data. These patterns are then combined to form the theoretical structure used by the researcher to understand the subject or phenomenon of study (Patton, 2002). Thus, grounded theory does not follow the traditional scientific flow of research starting with the formulation of hypotheses, testing, and development of subsequent theories. When adopting a grounded theory methodology, the researcher starts with a general question. designated sources. Data are then sampled from The collected information is analyzed to generate patterns and themes, referred to as 'concepts'. The examination of concepts may in turn underline the need for further sampling (Bryman, 2004). My project progressed according to five sequential steps substantiated by grounded theory: I. Methods development: literature review of secondary sources, creation of research questions, setting up of procedures, submission of research proposal. 26 II. Data gathering: conducting semi-structured interviews and performing content analysis of written material. III. Content analysis: coding and analysis of relevant themes from the data; define themes and trends in the data; mapping spatial information. IV. Reassessment: collecting further data where required to substantiate or reinforce findings. V. Evaluation of data sources: developing criteria and using critical questioning to assess the sources of information. 2.2 Secondary Literature The first stage of most research projects involves a review of the current knowledge of the topic of interest, including a description of what is known and what needs to be learned (Steward and Kamins, 1993). This task is generally accomplished by reviewing publications compiled by others who used primary sources. The secondary literature I reviewed focused on life sciences, history, anthropology, and archaeology as well as a range of literature on research methods. The review of secondary sources lasted throughout the entire course of the project, though its collection occurred in three somewhat distinct phases. During the first phase, I created a preliminary list of titles on caribou and moose with the help of research supervisors, fellow graduate students, and through searches of scholarly databases. During the second phase, I used other author's bibliographies to expand my literature search. The third phase involved the nonsystematic and opportunistic collection and review of additional sources. After the third phase my literature analysis was largely complete, but on occasion, I identified or was made aware of a previously unexplored source. 27 2.3 Interviews Participants I developed a number of criteria to identify and categorize potential participants for interview. Elders are defined as people of elderly age whose parents and/or themselves resided in the study area at the time of my research, and that are respected by their peers or communities as exceptionally knowledgeable about wildlife and associated environments. In the case of aboriginal participants, such people are also generally recognized as familiar with traditional Dakelh lifestyle and long-term history of the area. The differentiation between aboriginal and non-aboriginal elders is, in the process of analysis, purely a matter of method as the information from both participants is equally weighted in the results. The term Experts refers to persons, mostly of younger age, who live and operate in the study area and who are knowledgeable about its people, history and environments. Such persons are often involved in local institutions such as treaty offices, museums, as guides, or are recognized leaders in the community. Within the research process, experts are employed to identify knowledgeable elders during the process of participant selection. Preparation I prepared for the interview process in a number of ways. I reviewed pertinent training material (Sherry, 2003), relevant publications focused on conducting successful semi-structured interviews (Berg, 1998; Patton, 2002; Bryman, 2004), and I completed a course in qualitative methods at the University of Northern BC. My training was further enhanced by a daylong tutorial offered by the Tl'azt'en Treaty Office for employees and researchers conducting interviews with community members. 28 Fieldwork This project was approved by the UNBC Research Ethics Board (REB), the Tl'azt'en Band2, the band coordinator of the Nak'azdli Band, and conforms to the guidelines highlighted by TriCouncil Policy Statement: Ethical Conduct for Research Involving Humans (NCEHR, 2008). Following the approval of all aspects of my project, I began fieldwork in May 2006, and officially ended in December 2006. The main activities included excursions with staff of the Tl'azt'en Treaty Office and interviews with aboriginal elders. The Treaty Office Library in Tache contains a large collection of articles, books and media focused on Tl'azt'en Nation and the Dakelh natives in general. I examined these sources during my residency in the area. Residing and working in the community allowed me to develop trust and friendship with community members in preparation for the interviews, and to better understand the study area. Research Progression In May 2006, I presented a poster of my research plan at a community research open house in Tache to introduce the project to community members and to begin to attract potential experts and elders as participants. I had hoped to identify at least five names of Tl'azt'enne from this event, and to subsequently build a longer list using the reputational snowballing technique (Bryman, 2004). However, at the first meeting I gathered only two nominatives. I therefore adopted a reputational case selection strategy as described by Schensul and Le Compte (1999). Potential interview candidates were nominated through the advice of community experts. With the help of my supervisory committee, members of whom had been working with the Tl'azt'en Nation on joint research for over six years, and Tl'azt'en Natural Resource personnel, we identified 12 potential experts. Of those, only 11 responded: seven from the staff of the treaty office of the 2 See band consents in Appendixes. 29 Tl'azt'en First Nation in Tache, three from the John Prince Research Forest office in Fort St. James, and one from the Nak'azdli Band in Fort St. James. I asked the experts to nominate elders with knowledge of the historical distribution and abundance of caribou in the region before 1950. By the end of August 2007, I had received 72 nominations and 40 distinct names of candidates. Nak'azdli participants, originally not included in this study, were incorporated at a later stage through nominations made by their band coordinator. Table 2.1. Ethnic identity of persons selected as potential interviewees of the project. Received one nomination Received two or more nominations Total Tl'azt'en 15 12 Nak'azdli 6 3 Non-aboriginal 4 0 25 15 27 9 4 40 Total I chose to interview only those native elders who received more than one nomination. The exceptions are non-aboriginal participants. The latter, though nominated only once, were kept in the interview grid as fewer experts were used to identify non-aboriginal interviewees. This reputational selection technique resulted in 12 Tl'azt'enne, three Nak'azdli and four nonaboriginals identified for interviews in the first list. The almost even distribution of genders of participants (Table 2.2) suggests that women were actively involved in traditional hunting and trapping activities, and possessed extensive knowledge about the surrounding environments and its natural resources. 30 Table 2.2. Distribution of completed interviews for Tl'azt'en, Nak'azdli and non-aboriginal participants. Tl'azt'en Nak'azdli Non-Aboriginal Total Female 2 3 0 5 Male 5 0 1 6 Total 7 3 1 11 I worked with a community researcher, Kateri Haskel, to pre-test my interview questions and process. Subsequently, nominees were contacted by personal visits when possible or by phone to schedule the interview, and were asked to indicate a preferred place to hold the session: at home or at a community building. Interviewees were called a day in advance to remind them of the upcoming interview. Despite such efforts, the difficulty in holding the interviews soon became apparent. Interviews were frequently cancelled, or participants did not attend scheduled sessions. Contacting participants to reschedule interviews proved difficult. As such obstacles recurred, I asked employees of the Treaty Office to help me contact participants. At least three, and up to six attempts were made to re-schedule an interview. The equipment for the interviews consisted of a Samsung digital voice recorder, a video camera, consent forms as well as topographic maps (1:50,000 and 1:24,000 scales), pens and paper for use by the interviewee. Project assistants and members of the Tl'azt'en Treaty Office participated in several interviews as translators, facilitators and/or guides to the location of the interview. Interviewing and transcribing Interviews with Tl'azt'en, Nak'azdli and non-aboriginal elders took place between May and December 2006 in the town of Fort St. James and in the reserves of Necoslie, Pinchi, Tache and 31 Middle River. For all sessions, I employed a semi-structured approach. This format allows the interviewer to pursue sideline topics through additional questions, often leading to insights, and a departure from structured lists (Bryman, 2004). During the interview, I used a guide, in the form of a checklist, to ensure that all of the focal topics for the research were discussed with the interviewee (see Appendix V). Each interview started with a brief introduction of the topic and the signing of the consent forms (Appendix VI), and ended with the offering of an honorarium. Frequently, elders began to speak before the research questions were presented. Interviews ranged in length from 15 minutes to a maximum of almost two hours, with an average time of approximately 30 minutes. At the end of the interview, I asked participants to suggest names of other suitable candidates. Such questions allowed further validation of the list of participants selected using the experts' method, but did not change the interview roster. I transcribed the interview files using the free software Express Scribe™ and F4™. I applied minimal editing to improve grammar and fluidity. After the completion of the transcription and analysis phases in April 2007, I gave each participant a transcript package for verification, which included key excerpts of the interview, instructions on how to verify the transcript, and my contact details. When a Tl'azt'en research assistant or I was able to contact the elders in person, these instructions were also explained. As with scheduling interviews, I had considerable difficulty collecting and discussing verified transcripts with participants. I received no edited transcripts, and no elder expressed disapproval of the information recorded. 32 2.4 Content Analysis I used a structured analytical technique, content analysis, to identify key themes and ideas within the interview transcripts and the primary sources described in subsequent sections of this chapter. Content analysis is a form of examination of artefacts of social communication (Berg 1998). The latter might be words, sentences or entire paragraphs whose content is relevant to the research topics. The main function of this method is to reduce large volumes of written information into thematic units specific to the objectives of the research, defined as statements (Bryman, 2004). In this research, I employed content analysis to identify material that suggested changes in the distribution or abundance of caribou and moose as well as causal reasons for that change. Application of the content analysis method requires three main steps: sampling, counting, coding. Sampling requires the researcher to select the subset of documents or sources that are applicable to the focal topic. For instance, from the entirety of the HBC documents available for the Fort St. James post, I decided to sample the post journals. Counting involves finding and tabulating key words within the sampled document. Counting is performed by 'scanning' written text without necessarily reading it and by flagging each key word with an ID. Coding is the last stage of content analysis; here, key words found in the text are recorded as an alphanumeric code in a codebook. To provide context to the key word, the associated sentence or paragraph is also included in the codebook. Following completion of the coding process, all information is reviewed and arranged into thematic categories. Content analysis is a rigorous and repeatable method designed to identify and tabulate key words, statements, and themes. Working from Berg (1998), Bryman (2004) and Patton (2002), I defined key words as relevant thematic items identified in written documents. For this project, 33 key words are caribou, moose, deer and their semantic variations such as carribeaux, moose deer, etc. Key words are often associated with indicator words. The latter provide no direct information on caribou and moose, though their presence often offered clues to the nearby presence of key words and/or pointed to relevant collateral information. An example of an indicator is wolf. Because this predator is often associated with caribou, and since predation is an important factor in caribou decline, the reading of all the statements containing the word wolf can provide clues about the abundance of the predator and/or the presence of a statement containing information on caribou. Additional indicator words included hunt, fur, skin{s), return, mountains, antlers, moccasins, clothes, fires and their semantic variations. The product of sampling, counting and coding are statements. The latter provide context to the key word often in the form of the sentences or paragraphs in which key words are contained. Clusters of statements referring to a particular topic are grouped in themes, categories in which key words and statements are grouped. For additional detail, themes can be divided into sub-themes and arranged to suit research needs. 2.5 HBC Archives The HBC journals represent a significant source of primary evidence of Canadian history. The first catalogue of the HBC was compiled in 1796. After that date, systematic records were kept for many of the posts. In 1920, the HBC records became publicly accessible, while the archives, originally stored in London, were moved to Winnipeg in 1970 (Archives of Manitoba, 2007). The type of HBC written records available for Fort St. James include post journals, correspondence books, correspondence inward, account books, reports on districts, list of servants 34 and other miscellaneous items (Archives of Manitoba, 2007b). Post journals include daily entries of weather, activities, observations about the environment, occurrences of note, fur returns, arrivals and departures of visitors and expeditions in the hinterlands. I examined approximately 3,000 pages and four reels of the Fort St. James post, unevenly covering 42 years of history from 1820-1825 (1M128), 1824-1830 (1M129), 1827-1856 (1M130), and 1892-1898 (1M1022). The remaining years of records are unavailable. The information offered by the HBC journals is therefore fragmented for the second half of the 1800s and the 1900s. 2.6 Other Written Evidence For this thesis, written sources occurred as other written sources, primary written evidence or historical written sources. This broad range of sources revealed the varied typology of authors that inhabited the study area in historical times and the types of observation and documentation of the historical occurrence of caribou and moose. I divided these sources into three broad categories: 1) The written accounts of non-aboriginal explorers, travelers and early traders of Fort St. James who initially settled the study area (1806-1850). Examples of such documents are the diaries of Simon Fraser (Lamb, 1960) and the journals of Daniel Harmon (1904). 2) The written accounts of fur-traders, settlers and missionaries from 1850 onward; these documents record the experiences of longer-term residents with considerable knowledge of the study area. Of paramount importance in this period are the works of A.G. Morice (1892; 1897; 1906; 1907; 1909; 1910; 1930), oblate missionary in Fort St. James from 1885 to 1904 and active narrator of the history and culture of the area. Starting in the 1900s, a more modern format of 35 document appears. Examples of the latter are surveyor's works, and some anthropological literature (Jenness, 1932). 3) Recorded, transcribed, and sometimes published interviews of native accounts of life and recollections of the past. These include the interviews published by the Nak'azdli Elders Council (2001), or archived projects conducted by Tl'azt'en Nation, as well as the published account of Lizette Hall on Dakelh life (1992). Additional information includes a collection of interviews presented in a confidential documented collected by McKay (1998) on caribou distribution in the Valleau-Takla area. In the first phase of the search for written historical materials (beyond the HBC records) I first employed bibliographies of peer-reviewed literature (Hudson, 1983, Morton, 1988, Klippenstein, 1992 and Spalding, 1990, 2000). Subsequently, I identified additional titles by incorporating items found in the Tl'azt'en Treaty Office of Tache and by searching the Geoffrey R. Weller Library Collection at the University of Northern British Columbia. Most of the written sources were subjected to content analysis using the same technique and processes described in section 2.4. 2.7 Organization of Results Given the high volume of information gathered from primary sources, it became necessary during the process of analysis to organize the results in a consistent and reliable format. Using content analysis, I collected statements of interest from interview transcripts, HBC archives, and other written sources, and subsequently grouped them in tables divided by thematic categories, such as 'caribou distribution' and 'moose distribution' (See Appendixes I-V). The creation of tables 36 ultimately allows the qualitative assessment of individual statements and a quantitative analysis of patterns of frequency and other relations amongst the units of data. This process of data categorization occurred in three steps. First, each statement containing a key word was assigned a code, used to mark the statement in the transcripts. Second, I analyzed each of the statements to determine whether it provided temporal and spatial references to historical observations of caribou and moose. Third, I placed the statement under the appropriate theme. When statements lacked spatial or temporal references, I attempted to infer the information from the context of the statement or using collateral information derived from the other sources of information. Table 2.3. Example of statement gathered from the HBC journals organized in a result table (See Appendices I-IV for full tables). THEME Caribou distribution STATEMENT "The Marie des dent Biches Boy arrived & brought one Large Beaver & one small whole [sic], he is at present in the vicinity of Carriers Lake but complains of a scarcity of beaver - has killed no Rein Deer as yet." GEOGRAPHIC LOCATION Carrier Lake SOURCE HBC B.188/a/l, December 12, 1820, Collateral information is helpful in the determination of missing references, such as specific locations or dates, or helps provide context to historical events. The search for collateral data was conducted in the HBC journals using indicators or by finding excerpts of material used in anthropological secondary sources. Other collateral information was obtained by reading a primary source in its entirety, as opposed to the scanning employed during content analysis. At times, however, collateral information was unavailable. An instance is the statement shown in Table 2.3, for which I was able to gather only a very generic temporal location for the statement. 37 Maps and timelines Statements were often related to or were subsequently linked to a geographic location. These locations provided the content for the spatial analysis and the mapping of historical information using Geographic Information Systems (GIS). The process of linking information to ground coordinates was performed using the Atlas of Canada online mapping tool (Natural Resource Canada, 2007). These coordinates were subsequently imported into GIS software (ESRI Arc Map 9.2) and linked to a map (geocoding). Using Arc Map 9.2, I edited historical observations and created maps of the historical distribution of caribou and moose (See Chapter Three). Since the majority of statements did not provide specific locations, but references to morphological features (e.g. Mt. Sidney Williams), I centered locations in the mid-sections of the area that were consistent with known caribou distribution for that area (Poole et al., 2000; Johnson et al., 2002). The temporal information contained in maps is also provided in the form of timelines of events. As several statements lacked temporal specificity, in several occasions I was forced to estimate the part of the century to which it most probably belonged, or use collateral information to determine a date. In the case of statements obtained from interviews and other written sources, such dates were often derived from generic expressions such as 'in my father's time' or 'in my grandfather's time.' When not privy to additional data, I counted elders to be seventy years of age. Expressions such as 'my father's time' meant that an observation may have occurred between 60 to 100 years ago, and thus have happened in the early 1900s. In the case of 'my grandfather's time', the event was pushed one generation into the past, hence in the second half of the 1800s or in the early 1900s. 38 2.8 Evaluation Theoretical underpinnings I assumed that the sources of primary information employed in this project have both strengths and weaknesses relative to their ability to document long-term changes in the distribution of caribou and moose. However, few studies have performed a systematic evaluation of the spatial and temporal accuracy and precision or the information content of Hudson's Bay company journals, written historical evidence, secondary sources, and interviews with long-term knowledge holders. A formal evaluation of each source provides a context within which to consider the biases and limitations of the findings and conclusions presented in this study. In addition, such an evaluation could provide guidance to other researchers that might draw on these sources to answer similar questions. Qualitative research techniques and historical methods of assessment of primary documents are helpful in the evaluation of the quality of data collected and research process. Within qualitative frameworks, Marshall and Rossman (1985), Creswell (2003) and Bryman (2004) identify several strategies for evaluating findings. These strategies include: the use of triangulation between sources of data, of an appropriate form of narrative pertinent to the qualitative character of the events described; the use of verification from participants at the end of a research project to guarantee the correctness of the statements collected; employeeing peers and external auditors to enhance the quality of the information provided; and, finally, the portrayal of negative instances and biases to create a truthful and straightforward narrative (Creswell, 2003, p. 196). Conversely, historical methods of evaluation of primary sources are based on critical analyses of a source of information and historical documents. Such analyses are generally 39 premised on sets of questions, used as a checklist and 'asked' to a primary source or a document in order to verify its reliability. Examples of questions 'asked to a document' may concern the author, i.e. the historical context in which the author lived and from which the information was extrapolated, the degree of influence exercised by external conditions on the author, the motivations of the author for writing a particular statement, and so forth. Drawing from theory and techniques of evaluation of both qualitative and historical origin, I developed a set of criteria for evaluating the four sources utilized in this study (Crowley, 1988; Stewart and Kamins, 1993; Marius, 1999; Schensul et al., 1999; Creswell, 2003; Bryman, 2004). At a macro scale, these criteria are used to evaluate the general strengths and weaknesses of each source, with resulting recommendations for future studies. At a more detailed level, the criteria can be used to explore the information contained in individual documents. Each criterion of evaluation is further divided into a set of sub-criteria: precision, accuracy, and objectivity. I define precision as the measure of detail that a statement or source provides. For instance, a statement supplying a specific date of a historical observation is deemed precise, though it may not be accurate if the information that it provides is erroneous. Therefore, Accuracy is the degree to which the information reported is reliable, or error-free. The third subcriterion, objectivity, characterizes the degree of external bias of a statement. I used triangulation to evaluate each source according to the three sub-criteria. Triangulation is an analytical process in which the information contained in one statement is compared against other sources. Collateral information from alternative sources can assist with the triangulation process allowing the discovery of systematic or specific errors (Bryman, 2004). One must consider the limitations of the criteria and sub-criteria used for the evaluation. First, as most documents were not read and understood in a conventional sense but only scanned 40 using content analysis techniques, my appraisal of individual historical documents is limited to selected statements. Second, as much of the information contained in the statements relates to individual observations, it is difficult, if not impossible, to test the sub-criteria of individual historical information. Evaluation criteria #1: Source output and efficiency of data collection In this criterion, I evaluated the number of statements, or output, generated by each source. In a subsequent step, I explored the relationships between the total amount of information collected from each source, the overall quality of the information provided, and the effort required to collect and extract that information. I tabulated the quantity of statements by species and theme (e.g. caribou distribution, moose abundance and so forth) and assessed the efficiency of each source by comparing it with the others. #2: Temporal precision, accuracy and objectivity I used the number of statements providing information at the day, month, year, decade, or generic level to assess the relative precision of each source in providing the dates of observations. I then employed triangulation to conduct a qualitative appraisal of the potential factors affecting the accuracy and objectivity of the dates. #3: Spatial precision, accuracy and objectivity In this criterion, I analyzed the spatial dimension of the historical information extracted from each source. Across all sources, statements may be referenced to a specific, broad, or regional location, and precision of those locations may vary consistently across sources. A statement was deemed specific when it could be associated on a map to features such as mountains or small 41 lakes; broad when it was linked to a geographic feature on a larger scale (e.g. Stuart Lake area); and regional when it lacked reference to a feature, but nonetheless was located in the study area. As with the temporal criterion, the assessment of accuracy and objectivity was performed using triangulation. #4: Document animal abundance Spatial ecology, conservation biology, and wildlife management is concerned with not only population distribution, but also abundance (Nielsen et al. 2004). Thus, understanding the total number or density of caribou and moose can provide additional insight into how the presence of these two species across the study area has changed over time. In this criterion, I counted the number of times that each source provided a statement describing the abundance of caribou and moose. Statements that incorporated exact numbers of animals were specific. In cases of statements including qualitative or descriptive expressions of abundance, they were considered generic. 42 3. RESULTS In this chapter, I report the results of the content analysis of the secondary literature, interviews, HBC journals and other written sources. I used timelines and maps to summarise the temporal and spatial patterns of moose and caribou distribution across the study area (Figures 5-11). The original statements on which this chapter is based are provided in Appendices I - V. Using the criteria described in Section 2.8, I follow the analysis of the historical ecology of the two study species with an evaluation of the information content and specificity of each source. 3.1 Secondary Literature Archaeological literature With the exception of the pictographs of Stuart Lake, a review of the archaeological literature for the interior of BC revealed very few published studies. Additional unpublished literature developed by industry consultants and First Nations such as site-specific archaeological reviews or assessments preceding development may exist; however, I limited my research to relevant material found in the Tl'azt'en Band Office. The pre-contact period: archaeology of caribou and moose Over the centuries, Athapascan populations occupying present BC were well adapted to local environments and developed unique strategies of survival and resource use. The importance of caribou or moose in pre-contact subsistence is largely unknown. Caribou had a prominent role in the sustenance, oral traditions, and histories of First Nations populating the neighbouring southwestern Yukon (Hare et al., 2004), and in other areas of northern Canada (Dogrib Treaty 11 43 Council, 2001). In the millennia preceding the development of forests and the advent of salmon fishing, caribou and possibly moose likely were fundamental for the survival of nomadic Paleoaboriginals roaming the post-glacial landscapes of the interior of present BC. From the beginning of the pit house tradition 4,500 years BP until contact with EuroCanadians, subsistence in the interior changed from nomadic hunting of large game to a seminomadic lifestyle centered on a mainstay resource of fish, particularly salmon (Wright, 1995; 1999). Each spring and summer, prehistoric aboriginals used settlements near lakes and rivers to take advantage of the fish resource (Tobey, 1981). In winter, family units scattered for firewood and hunting (Hudson, 1983; Brown, 2002). Subsistence followed seasonal cycles, during which different species were harvested to overcome food shortages determined by failures in salmon runs and to obtain foodstuff for spring, winter and fall sustenance. Contact with neighbouring groups of the interior and the coast favoured the development of common cultural features and practices (Borden, 1954; Kobrinsky, 1981). As previously mentioned, the Dakelh might have migrated in the upper interior of BC in response to White River volcanic eruption and ash fall in the Yukon, which occurred around 1,500 years BP (Wright, 1995). Whereas the new occupants migrated recently or had been in the area for longer, the Dakelh adopted a semi-nomadic lifestyle patterns that is common to all First Nations of the interior, and which persisted until contact with European explorers, when new socio-economic conditions and industrial development in the 1900s supplemented traditional subsistence. The presence of forest-dwelling caribou in the lowlands and of herds in the nearby mountains might have played a significant role in the subsistence of these adaptable local populations. Given the presence of pre-contact Dakelh throughout the study area, it is likely that certain families and Keyohs (family land units) enjoyed a close relation with this ungulate, 44 specifically those groups whose traditional hunting grounds occupied the mountain ranges surrounding Stuart Lake. Numerous cultural and linguistic traces of the presence of caribou are found in Dakelh language, names of clans and places. It is hard, however, to pinpoint with exactness the overall role that caribou played in pre-contact times for these local First Nations. Archaeological excavations of prehistoric and proto-historic3 settlements yielded limited amounts of faunal remains attributable to large game. Wilmeth (1975) produced a report on the archaeological evidence for three sites south of Stuart Lake. The first site is located in the extinct native village of Chinlac, near the junction of Stuart and Nechako Rivers, between current Fort St. James and Vanderhoof. The village, historically inhabited by Dakelh, was destroyed by a raid of the Chilcotins in 1746 and was never rebuilt (Sewell, 1950). Amongst an array of findings, this location revealed very few bone artefacts or remains of consumed large game (Wilmeth, 1975). Further south, in the lower Blackwater river region (approximately 150km south of Fort St. James) the Punchaw site yielded faunal remains, predominantly mammalian, including caribou, deer, bear and other smaller fur bearers (Wilmeth, 1975). In another more southerly location near Anahim Lake (approximately 200km southwest of Fort St. James), faunal remains included caribou and a variety of furbearers and waterfowl (Wilmeth, 1975). None of the sites revealed the use of moose, although the incompleteness of the data does not allow the total exclusions of this species. Within the boundary of the study area, excavations at Carp Lake Provincial Park yielded only the remains of fish (May, 1977). The exact dating of the faunal remains discovered at these excavations is unclear. In the Anahim area, the Daniktco site was dated at 1300 BP. In the Chinlac site, the presence of European goods hints to a proto-historic occupation, though components of the remains might have been older. 3 The term proto-historic is employed by Wilmeth (1975) to define sites for which there is no documentation but that yielded European trade material. 45 Within the study area, several projects focused on the pictographs distributed along the shores of Stuart Lake (Corner, 1968; Richards, 1978; Mitchell, 2006) and on Takla Lake, about 200 km north of Fort St. James (McMurdo, 1971). On Takla Lake, McMurdo (1971) conducted an archaeological survey before the construction of the railway. McMurdo argued that the northern Dakelh and the Sekani people, whose traditional territory included the northern arm of the lake, peacefully shared Takla Lake. Though no excavations were conducted, the author noted that there was a high potential for further archaeological discoveries along the shores, and that the construction of the railway, lack of funds and periodic increases in the levels of the lake after abundant spring rains might have barred the discovery of other evidence. In his investigation, McMurdo (1971) analyzed six locations containing pictographs found on the shores of the Lake, two of which contained images of caribou. Mr. and Mrs. French, native elders of the Takla area, used their traditional knowledge to decipher the meaning of the pictographs. Based on their knowledge and interpretation, they concluded that the two sites depict caribou, as they stated moose did not frequent the area until 'quite recently'. However, the second pictograph, though interpreted as a caribou, is controversial as some argue that the shape represents a moose. McMurdo (1971) places the date of the pictographs between 100 to 150 years BP. The dating of the site is, nonetheless, also subject to interpretation. In McMurdo's (1971) view, the lack of reference of this site in local historical sources indicates that the pictographs are relatively recent. The sites on Stuart Lake have been reported in three studies: Corner (1968), Richards (1978) and most recently Mitchell (2006). For this research, I have decided to employ the more current postgraduate thesis of Mitchell (2006) on the Rock Art at Stuart Lake/Nak'al Bun. Mitchell (2006) analyzed fourteen pictograph sites located on the rocky shores of Stuart Lake. These locations were recorded, catalogued and interpreted using First Nation testimonies and 46 historical documents. Mitchell (2006) explained that in past interpretations the pictographs were alternatively described as either being 'message paintings' or 'divinating paintings'. In her opinion, however, the rock art of Stuart Lake was part of a more comprehensively shared native system of communication. This system, perpetuated through traditional practices, had been composed of culturally shared symbols and designs capable of communicating detailed messages. Specifically, the function of the pictographs around Stuart Lake was dependant on both content and location, and the painters and their contemporaries shared a collective understanding of the use of the landscape features as a means of communication. Most of the pictographs were focused on animal-related themes at multiple sites. In one of Morice's (1893) interpretations on the subject, caribou were described as 'on a mountain', while moose do not figure in any of the pictographs. The dating of the pictographs is unclear, though the sites were already present during the early 1800s. Mitchell (2006, p. 115) reported how Morice investigated the symbols, and how at that time the native peoples considered most of the pictographs of Stuart Lake to be 'very old'. Artefacts My attempts to find artefacts have been limited to a review of relevant items in the Athapascan ethnology collection of the Museum of Civilization (Gatineau, Quebec). The document containing the description of these objects was retrieved during fieldwork in May 2006 from the Tl'azt'en Treaty Office library in Tache (Table 3.1). 47 Table 3.1. List of caribou and moose artefacts from the Athapascan Collection of the National Museum of Civilization (Gatineau, Quebec). Object Material Powder pouch Tanned caribou skin Strap and European ropeties Club - used for both war and hunting Bark Scraper made of caribou antler Date Before 1925 Provenance Dakelh Native, Moricetown, BC Moose skin 1922 Dakelh Native, BC Moose leg bone 1924 Fort Fraser, BC Caribou bone 1925 Dakelh Native, Moricetown, BC An additional artefact was documented during the interview of participant #6. The elder placed a high sentimental value on the object, as she recollected that the scraper is over one hundred years old and had been previously used by her mother to treat raw skins while her father hunted. Figure 3.2. Caribou scraper photographed in the house of interviewee #6 during the interview session. Reproduced with permission of Interviewee #6. The presence of artefacts such as those described in Table 3.1 and Figure 3.2 provide evidence of caribou and moose use in the late 1800s and 1900s. Tools made from moose as early as 1922 indicates that by the 1920s this ungulate was well known to aboriginal peoples of the upper plateau, and was employed for a variety of uses and in traditional subsistence. 48 Anthropological literature The majority of the anthropological titles I reviewed were premised on the same sources of primary evidence (e.g., HBC Archives) on which this research is based. Therefore, this material did not supply new data on caribou and moose, though these works provide important collateral data and were essential for directing my research. This included guidance on the relative merits of primary documents and interpretation of events from which I based my narration of the historical ecology of the study area. The most relevant titles about the post-contact history of the study area are the works of Hudson (1981; 1983), Morton (1988), and Klippenstein (1992). Hudson (1981; 1983) provides a comprehensive ethnographic examination of the social, cultural and economic aspects of the Dakelh of Stuart Lake from pre-contact times through the fur trade and into recent times. Morton (1988) and Klippenstein (1992) focus instead on the years 1806-1915, the 'fur trade' period, and its implications for local First Nations. Other material focusing on the Stuart Lake area includes Duff (1951), Kobrinsky (1968), Tobey (1981), Bond and Russell (1992) and Furniss (1993). Overall, these authors concur on the scarcity of large game in the area. Klippenstein (1992; p. 47) states that in the district of New Caledonia there "was almost no large game besides some bear and, in the early years (e.g. early 19th century), some caribou" (italics added). Morton (1988) used a well-known statement by Simon Fraser (Lamb, 1960; p. 181) to describe the area: "fish abounds in the lake at certain seasons of the year, and animals of the fur kind are plenty, but large animals are scarce." Hudson (1983), as well as Morton (1988) and Klippenstein (1992) used evidence from the HBC journals to demonstrate the scarcity of large game. In particular, they report that caribou are not mentioned in sources of primary evidence for Fort St. James after 1851. Noteworthy, HBC records are unavailable after 1851. 49 One account, dated 1851, speaks of hunting caribou at a distance from Fort St. James: "all the Indians have now left here for their several hunting grounds - caribou are reported to be numerous in the mountains opposite Tache" (HBCA B.188/a/20. fo. 129, March 6, 1851; see also Hudson, 1983, p. 56). This statement and Tobey's work (1981) suggest the presence of more caribou in fur trade times than those observed today: The villages broke up, individual families dispersed... beaver, marmots, goats, and caribou were caught in snares, deadfalls, and surrounds. Hunting was done with spears, bows, and arrows. Meat was preserved by drying, and surplus caribou fat was melted and stored to provide food for the winter (Tobey, 1981, p. 425) Moose is not mentioned as being present in the area until the end of the 1800s. As for the causes of caribou decline in the area, Hudson (1983) is the only one to speculate on the reasons for changes in the distribution of caribou. He suggests that the disappearance of caribou from the Stuart Lake area might have been related to the end of a mini ice age from 1750 to 1850. Ecological literature To my knowledge, the only published ecological studies reporting specific information on the historical distribution of caribou and moose in the study area are those of Spalding (1990; 2000) and, in minor measure, that of Hatter (1950). Spalding (2000) conducted extensive historical research on caribou distribution in nine major areas, encompassing the whole of BC. My study area is included in what he defines as the sub-boreal interior eco-province (Spalding, 2000). Spalding (2000) states that there are no caribou in this area today, but that in historical times caribou, though scarce, were present. He does not offer, however, any explanation of the precise causes of their decline or of when caribou ceased to populate the lowlands. He reports that at the time of European arrival in the province the numbers of caribou were probably 30,000 to 40,000, twice what they are today. Over the course of the 1800s and the 1900s, the provincial populations 50 began to decline except, he states, in the areas north of 55°N. Hunting, in combination with ongoing predation, were deemed potential causes of early declines. Other contributing factors might have been habitat loss from wildfire, severe winter weather and changing land use. In their assessment of habitat use by caribou found near Takla Lake, Poole et al. (2000) report that caribou were extirpated from low-elevation valley bottoms. While moose expanded throughout central and southern BC in the early 1900s, their appearance in the Takla area encouraged larger wolf populations, which in turn significantly reduced caribou numbers. This resulted in highly fragmented caribou populations restricted to mountain habitats described as "island remnants in a sea of moose and wolves" (Poole et al. 2000; p. 1561). They suggest that in the 1800s and the 1900s, caribou "were apparently much more numerous," and that "huge numbers of caribou were reported migrating west across the north end of Takla Lake" (L. Erickson, quoted in Poole et al., 2000, p. 1561). Hatter (1950) observes that moose were absent from the regions comprising the study area until the first half of the 1900s. His views were supported by a body of literature documenting the 'colonization' of other parts of BC (see Brooks, 1928; McCabe and McCabe, 1928; Hall, 1964; Bergerud and Elliot, 1986). Spalding (1990), however, challenged the premises of these authors and thus the idea of recent colonization of the province by moose. Based on his interpretation of documented historical data, moose, though scarce, were already present at the time of Alexander Mackenzie's voyage through the region (early 1800s). He argues that their numbers began to increase in the 1860s, and that by 1870, moose were numerous, particularly in the eastern half of the sub-boreal eco-region (partly including the study area). Further analysis of the ecological literature does not offer conclusive evidence to support either the presence or the absence of moose in the study area for the 1800s, though other studies 51 have taken a more detailed look at the expansion of moose in other parts of BC (See Karns, 1998; Darimont et al., 2005). 3.2 Evaluation of Results from Secondary Literature The evaluation of secondary sources follows the same criteria of that used for other primary sources, though secondary sources by themselves do not constitute evidence, but only reinterpretations of other primary documents. Therefore, while these documents were useful in the identification of unknown or unpublished aspects of the historical distribution of caribou and moose across the study area (Stewart and Kamins, 1993), they did not offer original contributions to this research. Rather, they served as focal points that guided the development of questions that I investigated using primary sources. Exceptions within secondary literature are archaeological titles, which substantiate with primary data the occurrence of caribou in historic and pre-contact times in the upper plateau. The pictographs in particular provide further proof of the historic presence and use of caribou near Stuart Lake, while the remaining archaeological investigations offer sparse and inconclusive proofs in the form of animal remains. Anthropological literature, based on written historical sources, focuses on the socioeconomic and cultural change of people inhabiting the region throughout the 1800s. This material provides valuable interpretations of the influence that anthropogenic factors had on caribou and moose distribution. The statements collected from these titles support the hypothesis that caribou were present in scattered populations in the upper Nechako lowlands, and that moose were scarce to absent until the late 1800s or early 1900s. 52 The reliability and objectivity of secondary literature varies considerably across documents. Primary data collected by authors and included in this material is generally presented in academic format and created using modern standards of research. As such, its dependability is somewhat superior to that of grey literature. The recognition of biases in secondary sources, however, is a problematic subject as historical interpretations may ultimately differ. Differences in interpretation reflect the contrasting nature of many local documents, and the diverse processes of analysis employed by authors to substantiate claims of the presence and absence of caribou or moose. #1: Output and efficiency of data collection In total, 19 secondary titles refer to the historical distribution of caribou and moose in the study area. Of the latter, however, only 13 report non-redundant statements; the remaining six were therefore discarded. The majority of documents focused on archaeology (N=6), followed by ecology (N=4), and anthropology (N=3). Within the ecological category, two titles relate to caribou and two to moose. Amongst all sources secondary literature was, undoubtedly, the easiest to collect. In contrast to other primary sources it provided relatively large amounts of information on the research topics at little expense and effort, though insufficient amounts of data to justify its use as sole source of information. # 2: Temporal precision, accuracy and objectivity All secondary documents provide a very general dating of historical events. Archaeological sources are no exception, as faunal remains and pictographs are dated loosely, in almost all cases to the early 1800s and earlier. The vagueness of secondary sources is a result of these sources 53 focusing on anthropogenic themes rather than environmental history; thus, caribou and moose are mentioned as supplemental information in the context of traditional subsistence activities. Anthropological sources provide generic information on the history of caribou and moose in the region. An instance of the type of data collected from this source is the description found in Morton (1988) and Klippenstein (1992) of the trade of moose skins from the east. Based on this information, I inferred that moose products were present as a good of trade in the Stuart Lake area during the 1800s, but that moose themselves were unavailable for direct harvesting by aboriginal peoples. Such information was confirmed using the HBC archives. # 3: Spatial precision, accuracy and objectivity The geographic precision of secondary sources ranges from broad to generic to regional; exceptions are primary references cited in text. Overall, secondary literature lacks the necessary detail to link statements about caribou and moose to specific geographic locations. Archaeological titles are an exception, as the location of excavations and of the pictographs are accurately positioned. The pictographs of Stuart Lake offer ample evidence of native use of collectively understood symbols for hunting and gathering purposes (Mitchell, 2006). Mitchell (2006) reports that such symbols were not only present in the sites alongside Stuart Lake, but also in similar form in Carrier facial tattoos and in other signs of communication used by hunters in the forest. The presence of caribou in this variety of media employed by local native peoples provides a remarkable case for its presence and use in the immediate surroundings of Stuart Lake. Conversely, the absence of moose suggests this ungulate was unknown to local native peoples until the 1900s. 54 #4 Document animal abundance Secondary sources provide generic estimates of caribou abundance. I noted qualitative statements such as 'many', or 'scarce', but no direct measures or estimates of caribou or moose numbers. Generally, anthropological and ecological titles are reflective of primary information gathered from the HBC journals or other written evidence. As such, they describe caribou as not being significantly abundant in the Stuart Lake area. Summary Secondary literature provides little new information about the historical distribution of caribou and moose in the study area. The majority of the findings reported in these documents are derived from other primary documents, mostly HBC journals and other written sources. Exceptions are some archaeological and ecological titles such as the article of Poole et al. (2000) on the southern Takla herd. These documents generally supply limited primary data, characterized by poor temporal reference and high spatial accuracy. Most of the information contained in secondary literature is presented in peer-reviewed publications using academic standards. 3.3 Interviews Caribou knowledge Interviewee #2 was significantly informative of caribou and moose dynamics in the area. This elder stated that caribou were present in the Stuart Lake region during the 1800s, and "all around Stoney Creek, well down to Blackwater and Prince George area". In addition, he remembers 55 hearing from elders of his generation that a number of caribou were present on Mount Sidney Williams and vicinity, but that population was wiped out in a single occasion in 1890: Down this way, [...] (caribou) was plenty, and after they go around here and they crossed at Rainbow lodge, that is where they cross it, that's a crossing road for caribou. In the winter they would cross and go up to the other mountain, Mitchell and Takla range on that side, they crossed back and forth. [Caribou] were there prior to 1890, then there was starvation and they cleared out all the caribou. About 60-70 of it, they shot all over, they killed them till the last one, a white one [...] they shoot them all until the last one, and then they went to get everyone from down to Black water, Prince George, and Stoney Creek. [Interviewee #2, Tl'azt'en] Interviewee #2 believes that the caribou moved north, around "Bear Lake and that area". It is unclear whether this participant referred to Bear Lake located northwest of the study area4, or Bear Lake east5 of his traditional territory. The following statement related to moose suggests the interviewee referred to the more northerly location: "they used to go all the way up north like around Bear Lake and that area to hunt moose..." (italics added). This elder also recalled that the area was "full of elk," but that elk populations decreased over time. Interviewee #3 affirms that caribou were present before 1950 in the mountains, but that populations declined because of changes in forage availability: Many years ago [...] caribou had a special feed in the mountains [...] they don't feed around here in this kind of grass, they stay in the high mountain, they feed on different plants. So, since they moved out like in Sidney Williams all they feed on is gone, I don't know why. Years ago, I don't know what year; they were blasting up in Sidney Williams looking for gold. Some miners. That's when everything, everything, all those caribou moved out. [Interviewee #3, Tl'azt'en] 4 Bear Lake (56° 5' 6" N 126° 46' 38" W) is situated approximately 240 Km northwest of Fort St. James and Takla Lake, near the upper reaches of Driftwood river, in the Cassiar Land District of British Columbia. 5 This second location (54° 29' 44" N 122° 40' 10" W) is approximately 100 km southeast of Fort St. James, along the Highway 90 North towards Chetwying and Fort St. John, in the Cariboo Land District of British Columbia. 56 In another section of the interview the same elder mentions that caribou were seen in Shass Mountain in great numbers, but that all of a sudden they started "dying out," possibly killed by "lots of wolves." He also believes that moose took the caribou's place as the main prey, and that they are now suffering the same fate. In his opinion, however, caribou are not the only species declining; since the times of his father and grandfather, "all animals" are "moving out" of the area. The trapline of interviewee #3 is located near Whitefish Lake, approximately 40 km north of Fort St. James. The latter includes Shass Mountain, the place described by him and others as having been historically populated by caribou. Interviewee #5 is a non-aboriginal, long-time resident of the area who also worked as a guide in the late 1940s. His license allowed him to operate in selected areas from Fort St. James to Germansen Landing. He remembers never having seen caribou south of the Wolverine range, except in one instance. In 1980, while fishing on Tezzeron Lake, another fisherman reported that he had seen seven caribou crossing the Lake using the sand bar (a stretch of low waters crossing Tezzeron Lake approximately half-way). Interviewee #6 is a very knowledgeable elder of the Nak'azdli community, who contributed to a number of community projects involving TEK and the history of the area and its natives. She possesses extensive memories of the past, derived from the traditional lifestyle that she lived with her parents while inhabiting remote areas of their trapline. The latter is located in the Nation Lakes area, "in the mountains." She remembers her father hunting caribou during her youth. While he hunted, she and her mother treated the skins and furs of animals. The caribou bone scraper shown in Fig. 4 belongs to such a time. In her memories, they were "never out of food. We had a variety of fish, bear, goat, caribou meat, everything; not too much of this food wrap." 57 Interviewee #7 is a Nak'azdli elder whose trapline is nearby Salmon Lake, about 50 km east-northeast of Fort St. James. This elder used to spend much time hunting and trapping around that area and the Nation River. While sharing information with 'old-timers' of the area, he remembers the latter speaking about caribou being more abundant than in present times; specifically, caribou were found on Shass Mountain, Mt. Sidney Williams, and at a place called 'caribou flat', where old-timers use to see caribou all the time, "even in the summer". Using his descriptions, I concluded that this site corresponds to the presently named Butchers flats, approximately 45 km north of Fort St. James along the North Road. Interviewee #8, being a sibling of interviewee #6, related similar information of caribou distribution and abundance. Interviewee #9 is an esteemed elder of the Tl'azt'en community whose traditional knowledge was sought for a number of projects focusing on the area. Her trapline, located near Whitefish Lake, is approximately 45 km northwest of Fort St. James, at the northern base of Shass Mountain. She remembers her father talking about a number of caribou crossing around Whitefish Lake and being permanently present on Shass Mountain. She also states, "caribou were not there when I was growing up. That's when he was young." Interviewees #10 and #11 belong to two consecutive generations living in the Dzitl'ainli community, also known as Middle River. Interviewee #10 remembers many stories told about past caribou abundance, but he recalls having seen no caribou in the valleys and lowlands during his life. Interviewee #11, however, recollects seeing his first caribou in 1932, and states, "there were lots then." He remembered the following about caribou: "that's what my grandfather's fathers hunted, and they were all over." 58 Moose knowledge Interviewee #1 is a Tl'azt'en elder who recalls elders speaking about the first time hunters saw moose tracks: "They followed it for two days, catch it, and then invited all the people. After that, the moose came, little by little: "I don't even know [when], I wasn't even born when these things happened." Her statements are somewhat corroborated by interviewee #2. His grandfather and others "had followed it [a moose], and, after few days, had killed it." Between that date and the 1920s - 1930s, this elder maintains that moose were not found in the area in any number. Interviewee #3 narrated that someone his father and friends used to talk about shot the first moose around Trembleur Lake; he, however, has forgotten the name. He also stated that people used to go hunt moose, sometimes for entire seasons, "up Bear Lake and that area." Both statements are similar in content to those provided by interviewee #4. The latter remembers that in 1898 his uncle killed the first moose. He also says "there weren't much [moose] at the time, that's when they started." Interviewee #5, the non-aboriginal guide recalls 'old-timer natives' talking about eating beaver, and that moose was "a new delicacy" when it finally moved into the area. He also suggested that moose migrated from Alaska. Interviewee #6 mentions again a 'first time' when a moose was killed. The recurrent theme of a 'moose first kill' implies that at the time, the event created quite a sensation in the community: "I was a child [...] my mother was looking for somebody to baby-sit us [...] they had heard that somebody had killed a moose thirty miles from Fort St. James". Interviewee #7 described a similar event occurring in 1911. He recollects his uncle saying "they followed a moose that crossed Nation River for seven days, at which point they killed it." Interviewee #8 recalls that while her father was freighting a cargo for the HBC from Prince 59 George to Fort St. James, he saw a moose for the first time. They "just stared at it, it was so awesome; they couldn't believe it was so large." Shortly after that occasion, "moose started to come. No matter how far you'd go, you would kill a moose." In her opinion, however, the Dakelh knew about moose before that first happening. Native traders from her community used to go in "Cree country" bringing with them dried black bear and "other Indian food," and they used to trade such foodstuff for moose hide. The location of 'Cree country' cannot be determined with certainty. Based on information obtained in personal communications and during the interview with #8, I deduced that "Cree country" is located in the east. Given the geography of the interior, it is possible that aboriginal trails connected the Peace region and thus the Cree, Beaver and other First Nations of the plains with the Dakelh. The last interviewee #11, states that the first moose tracks were seen in the area in 1918. 60 :rviewees. 2J, 6. n.d) t'e used caribou for foodstuff, blankets, hones as scrapcrs. sinew,( I n t e r v i e w e e fib. early 1900s) stomach as container for animal'Ifat. ihink they started to c o m e when handles, andfor many oilier things' I was a child (...] M y m u m was • (Interviewee #2. 1890) Caribou numerous on Mt. Sidney Williams and Mt. Tsitsutl: following widespread starvation 60-70 caribou are killed. After that episode, only few caribou remained. f ( I n t e r v i e w e e 47. 1911) First m o o s e . (Interviewee #11, 1918) 1 ( I n t e r v i e w e e # 3 . 1800s) ' M v g r a n d f a t h e r u s e d lo talk about n o m o o s e in this area; they used to g o u p n o r t h a r o u n d Bear lake a n d that area. And then m o o s e started to c o m e ; s o m e o n e I forgot his n a m e w e n t u p in T r e m b l e u r a n d killed t h e first m o o s e ' (Inteniewce f,4. IHOOs) They {caribou] used to he everywhere. Shass mountain, hundreds of them, and deer, hut no moose at all' (Interviewee #2. 1896) , ' F i r s t m o o s e . T h e n , in t h e 2 0 - 3 0 m a n y started to c o m e ' (Interviewee #4. 1898) - First m o o s e tracks. looking for a babysitter because s o m e b o d y had killed a m o o s e ( I n t e r v i e w e e #5. early 1900s) 'I d o r e m e m b e r talking to long timer indians. m e n in their 70s at thai time. T h e y remember moose was a n e w d e l i c a c y w h e n they tlnallv m o v e d into the a r e a ' (Interviewee #3 & U7. >1940) There used to be Caribou on Mi. Shass, Ml. Sidney Wimmiums and Mi. Tsitsutl, bin moved out #5. I9S0) «S 9 early WHO) H'ofverine ran^e the (interviewee till, 1932) 'Use lo hunl closest I heard ofcaribou: 1932. that 's when I caribou. many saw first caribou. except in 19X0, when a There used in the motttuains fishermen told me 1 caribou to be lots then ' around Nations crossed the Tezzeron Lake' Lakes. There were (Intervieweeti7,1950s) some a! the hollow l know in one place when: \e hum there is a hunch ofpeople dial of the valley. kill toomy m caribou, and »vc noticed a decline. If'c used caribou You go in one place one year and you for many things' find them. Nest year, nothing' (Interviewee Late 1800s) ' M y f a t h e r u s e d to work for the H u d s o n ' s Hay. T h e y went t o Prince G e o r g e and t h a t ' s w h e n they s a w the m o o s e first. T h e y couldn't b e l i e v e it w a s s o l a r g e ' 'First moose* Figure 3.3. Timeline of caribou and moose historical observations gathered from interviews with local aboriginal and non-aboriginal elders. 61 % • A « WiHiston N •I 1 - , V ^ • w- Early 1900 Migrations - » Hogem * 0 - , Early 1900s Nation Lakes• Migrations <1950 in the 1800s t 5 across Middle_ r ^ . ' Q Moose Hist. Observ. 0 Research Locations Water Features Protected Areas t?arp ^ Lake 1800s * ^-Av^.v Caribou Hist. Observ. .Samon., <1940: - Early ^ « P "" 0 " ^ N . • V C> Lafce , J-Wce ^ ^ T a c h e Q l a S ^ i ; YT Legend - -X •Dzitl'ainli ' (Middle River)1 -» .1890 < 1 8 9 0 ^ \Babine ' • 'l911.12 ' V t, ( \ WillmmiZA932 -fcT .; • 6""" v. . behleenMitcheiiand TaK.a Ranges. JffSU LBkjBt s- V Swannel Ranges . i' . Bu ,2VV 1 9 0 0 < . ^ * • .> a n Late 1800s , U f c a r l y 1900s '1800sjt<1940 1 » r. • ^ * " ' £, . ^ ^ f c F t . St. J a m ^ s , / C j v - ^ - ' r ; T N e c o s l i e ^ ^ ; Sfc*- ; . V . < S a m ^ Stuart Rivers> •. Provincial \ Park . o HiU I H t M flu I'jiW <:,/ :n tllihll >1 ill iit\ tttitiruliit'in Orlohi-r I'i. /VSJ hunt al i iinl-nii li/,l;utt\ kill, ,1 ti these t/ihiruri \ JWC.I II /.vs a i>J i iiiihuu ii r/ic IIW I « MV . : nHave tilting iht f-iliHtun IS. /.WJ Ikwiih, i- iv. lidf ' In iialiiin •>hut < iifv'',>if hunting in utrtifailt* hi iifttti th. immuuiiu < ,-il/tlT / li/< ' I ij HBCAfl/ V. c/ /' .i/urWi /'), ' If? .ni/iu'I lilu J ///« i II /.w.i; /humeri; thills t(*!hi /"vw", ,il,(Km ,(/ Curtii.r I I UK A HISS 17 MukII 2V. IS 32 1 LXvluinvai l>a> killed ;i KiiRlCv'r" TI SEJ , l/IU I H !\< u ' \hiahf> / V/ ///« i /< /,v.v „\ C illihill tin- nptlfh'J U../. H « / sv. Hiinwii-u* ill illi' Uuui .A i * v \f,, t, r-'th-.tl Mli|W/iMl> lu-iilf; (.ilhif aniwhl \ctn\lic tipjkmlv I'm fie ^Vars covrrcil In Ihr tllit A (lost journal?) i'urf SI. Juint-s Figure 3.5. Timeline of caribou and moose historical observations gathered from the HBC journals of Fort St. James. * j - j & t ' P " Laj*?s \ 852 ' i Hogem s\ '"VS^X ", • ^ • V . . \ . „ ^ -Salmon. v VDzitl'ainli > ' "-..f ^ 0 ^1896 \Rabine • * ^ •Lake, . s , \ ' V ' • ivA. •S ^ - Q l 8 3 2 Tache * ^ V > - . . 1842-, y^'."' o r1851 Legend ® Caribou Hist. Observ. Q Moose Hist. Observ. 9 Research Locations ' . ^Binchey ^1852 .v '. . Ft. St. Jam&3^- Necoslie' Protected Areas . •> 5 " ,.VI » Stuart RiverzS - . Provincial ^ Water Features • ** v ' " v .ake - C f^ «' h-" - V - v , - ^ 'a. Par* • Okm 10 20 40*i i i i i i i i i ^ - Figure 3.6. Caribou and moose historical observations gathered from the HBC journals of Fort St. James plotted on a map of the study area using GIS software. 69 3.6 Evaluation of Results from the HBC Post Journals The HBC post journals of Fort St. James have been employed in almost all publications concerned with the history of the study area (Hudson, 1982; Morton, 1988; Klippenstein, 1992; Spalding, 1990; 2000). A literature review of similar projects has highlighted the importance of this source to historical research across Canada (see Catchpole and Moodie, 1978; Catchpole et al., 1981). The reasons for the widespread use of the HBC journals are several, and worthy of discussion. The journals provide data such as daily observations on weather and fur returns in a systematic manner that fits within most standards of scientific research. Biases, though present, are easily recognized in the process of analysis and can be reported. In addition, the journals are available for a variety of geographic locations, and are consistently reported in the same format. The main disadvantages of the journals are difficulties with interpretation and missing records for some of the posts (including Fort St. James). Information from the journals of Fort St. James is only available for the first half of the 1800s and from 1892 to 1898, and their complexity and sheer length makes content analysis challenging. The periodicity of this source, undoubtedly advantageous in certain instances, could also be interpreted a source of bias. Crowley (1988) describes how several issues affect the quality of the evidence provided by a periodical source such as newspaper. Haste of composition and immediacy obscure the long-term context of events. Furthermore, the author 'perforce depends on observation, handouts and interviews, with only rarely the opportunity to look back and reflect' (Crowley, 1988, p. 35). Other potential biases in the statements gathered from the HBC journals include the limited knowledge of the surrounding environment held by the company employees, their 70 prejudiced view of the natives, and, at the same time, their reliance on the latter for subsistence, at least in the first decades of the Fort (Klippenstein, 1992). Such dependency was seen by the HBC as dangerous for trade relations, and several schemes were tried by the traders to increase their self-sufficiency. It is likely, therefore, though only a conjecture on my part, that local Dakelh maintained some level of secrecy about the natural resources that were needed by personnel at the Fort in order to maintain an upper hand during trade negotiations. Such information would have benefited local aboriginal groups in trade negotiations, and provided them some degree of control over Euro-Canadian settlers. If this assumption is accurate, the location of caribou or knowledge of migration routes would have almost certainly not been disclosed in the journals. #1: Output and efficiency of data collection From the estimated 3,000 pages of written records contained in the journals, I obtained 10 statements. Of this number, eight were related to caribou, one to moose and one to 'deer'. While several references to the key word 'moose' are present in the journals, I reported the latter word only when related to an actual observation, and not when mentioned in relation to trade from the east. Further research into the trade of moose skins from east to west (e.g. McLeod post journals) may offer additional clues on the historical occurrence of this animal in the eastern sections of the study area and the interior of BC. The limited number of statements makes of this source the least efficient in terms of the number of results obtainable relative to the volume of information analyzed. The process of gathering and scanning the HBC journals lasted roughly one month. As mentioned, content analysis was fraught by difficult handwriting, missing pages, and, overall, influenced by discontinuity in the years of records available. 71 #2: Temporal precision, accuracy and objectivity The temporal precision of the HBC journals is the highest amongst the sources. The journals were written on a daily bases; therefore, all statements specified a day of observation. Most of the information concerning caribou or moose reported to the fort consists of third party observations such as "Dechanyai killed a reindeer." Consequently, there might be a gap between the time of actual observation and that reported in the journal, which could influence to a small degree the accuracy of the records. #3: Spatial precision, accuracy and objectivity Statements taken from the journals have precise spatial references: five out of 10 statements are specific, while the remaining are regional. As previously mentioned, observations are mostly second-hand information such as: "All the Indians have now left here for their several hunting grounds - caribou are reported to be numerous in the mountains opposite Tache" (HBCA B.188/a/20, March 6, 1851); and: "Prince and Brother also arrived from an excursion. They I believe have made a good hunt of carriboux and a few furs" (HBCA B188/a/20 March 17, 1852); [italics added]. The precision of the information contained in the journals is, thus, dependent on the source of the statement, rather than the author of the journal. In addition, as most of the information reported for areas outside the fort was derived from native hunters and trappers, the considerations previously expressed on what was told to the traders and what was not might further affect the accuracy of the information provided. #4: Document animal abundance Because of the commercial nature of the HBC, and perhaps because of the scarcity of provisions for the fort, the statements of the HBC journals provide detailed descriptions of animal 72 abundance. Out of 10 statements, five report exact numbers, while the remaining five are more generic. Consider for instance the following statement: "Indians shot 3 carriboux beyond Carrier Lake" (HBCA B.188/a/19 February 12, 1842). Summary The infrequent mention of caribou and moose in the HBC journals suggests that these species were not common in the study area. However, the few statements found do not offer conclusive evidence of their scarcity. Caribou are documented in the journals with great spatial and temporal accuracy, as well as detail. The major flaw for this source is the incomplete chronology of records. 3.7 Other written sources Other written sources are primary documents mostly authored before 1950 that directly document the historical ecology of the study area. From the establishment of Fort St. James in 1806 to 1950, the inhabitants of the local area produced a variety of written works. These include EuroCanadian accounts of local life and travels, survey reports, historical-anthropological works such as the studies of the Dakelh conducted by Morice, and stories and legends of the Dakelh collected from the Treaty Office of the Tl'azt'en Nation. Within this category, I also include the results of more contemporary interview projects. One of the earliest sources of information concerning caribou and moose in the study area are the accounts of Harmon (1904). During his travels in the region, he provides mentions of caribou: 73 Their principal food consists of salmon, white fish, and trout; and they, at times, kill a beaver, or a caribou. The country around the Lake is hilly (Harmon, 1904, p. 179) The lack of supplies dictated by the cyclical nature of the salmon run is in the early decades a recurring theme in the accounts of early explorers and traders (Harmon, 1904; Lamb, 1960). We must assume that in the first decades of colonization the traders of New Caledonia were faced with considerable hardships in finding enough provisions. Simon Fraser (in Lamb, 1960) wrote in 1806 from the vicinity of Stuart Lake: We propose to continue our route as soon as we can collect a few provisions, but then we have nothing to expect but dry salmon, which is bad stuff; there are no large animals except the Carruban [caribou] which is to sly for us (Lamb, 1960, p. 326) In 1815, J. Stuart (in Morice, 1897, p. 5) reflects on the scarcity of large game in the area: "We have no buffalo or deer, except the caribou ... and not many even of those." Such statements seem to confirm that caribou or any other ungulates in the area were uncommon, a theme that is recurrent in all titles derived from European accounts. In contrast to these descriptions of low ungulate densities, native accounts suggest that caribou and elk were common: As I mentioned earlier there were no moose, but there were plenty of caribou, elk and some deer. The smoked hides of these animals were used at potlatches (Hall, 1992, p. 36) The presence of moose in the area seems to be confirmed for the second half of the 1800s by Anderson (1872): "moose killed near the junction of Stuart and Nechako rivers" and by Turner-Turner (1888): "moose... killed within 18 miles of Fort St. James." Furthermore, Morice (1910, p. 139) observes how caribou and moose flesh can be "procured at a distance from beaten tracks, or near the mountains, whereon the hunters roam for weeks at a time". 74 Other sources, including the interviewees of McKay (1998) and Nak'azdli Elders Society (2001) suggest that caribou numbers in pre-contact and early 1800s were much greater than they are today, particularly in the mountains: As I have been told, the caribou gathered in a herd of hundred or more. They fed in the lowlands. They were everywhere, and people killed these animals with bow and arrows. The Indians killed only what they needed. The meat of the caribou was dried. From the tanned hides, the women made coats, pants, mitts and moccasins. The bones were made into knives and hide scrapers. (William Julian, 1917; in Nak'azdli Elders Society, 2001, p. 54) Other written sources provided contrasting information in describing the distribution of caribou and moose in the area. While Euro-Canadian accounts seem to converge on the scarcity of caribou and the presence of moose as early as 1870, in native accounts caribou seemingly appear more numerous, particularly in pre-contact times and in the mountains. Alternatively, moose are not reported until the end of the 1800s. In the collection of 'Elders Stories and Legends' of the Tl'azt'en archives6 I found several references to both caribou and moose. In the traditional subsistence section of the Band Office records, one interviewee states "moose came in 1913." Another elder, speaking of times of starvation, comments on a hunting expedition for caribou in the mountains. On a tape dated 1987, a Tl'azt'en elder recounts a legend named "Been married to caribou". Overall, however, the transcribed tapes found in the Tl'azt'en archives did not provide crucial information on past distribution and abundance of ungulates. The unpublished and confidential set of interviews of first Nation elders conducted by McKay (1998) provides useful information on past distribution and abundance of caribou, in the Valleau Creek and the Takla Lake areas, located northeast and northwest of Stuart Lake, 6 Retrieved in July 2006 from the Tl'azt'en Band Office, Tache. 75 respectively. Because of their remoteness, these regions are not mentioned in detail by any other source I reviewed. Information based on the knowledge of two respected elders of the Takla Lake First Nation prompted McKay (1998) to suggest a remarkable theory for the historical distribution of caribou populations in the area. The author named the latter the 'grand herd theory'. The elders explained how in the 1800s caribou migrated in great numbers across the north end of Takla Lake to reach the Bulkley Valley. The latter was deemed, in historic times, optimal caribou habitat, before settlers "burned and tilled the land" (McKay, 1998; p. 4). The same elders also mentioned a herd composed of approximately 200 caribou, seasonally inhabiting Murray-Ridge and Pope Mountain, near present Fort St. James. The large migrations no longer occurred after the 1930s for several reasons. The elders suggesting the grand herd theory maintained that in the past winters were much colder, and the tree line lower. The advent of a warmer climate brought to the region increased forest fires, which in turn opened favourable habitat for moose, the first of which was seen in the area in 1914. The presence of moose also increased wolf numbers, previously solely reliant on periodic migrations of caribou. The mining boom of the 1930s and settlements further limited caribou movements, until only a few animals kept moving and the urge to migrate was lost. The second interviewee of McKay (1998) confirmed parts of the grand herd theory, though she did not have any personal recollection of large migratory events. She stated that caribou were beginning to disappear from many areas during the 1940s, and the main causes of their decline were increased predation and railway tracks. The third interviewee of this project lived close to the Omineca River, in the northern sections of the study area. This elder suggested that moose inhabited the Takla area in pre- 76 contact times. He remembered how his great grandfather told him of a moose-like animal around Takla Lake, now gone for over 300 years. The same elder also stated that caribou used to winter in the lower end of Takla Lake, but not anymore. He blamed predation and warmer climate for the disappearance of caribou. The fourth elder interviewed by McKay (1998) recollected that herds in the past were "much bigger than today". In his memory, the first sighting of moose in the Takla area occurred in 1920. Other interviewees spoke of the importance of Baldy and Gillis Mountain (Manson Creek area) for caribou populations. A local guide operating in the Fort St. James region from 1940 to 1970, reiterated the importance of Baldy and Gillis Mountain, but stated that caribou populations were 'never abundant', in his experience, in any of the areas. Two additional interviewees mention unregulated hunting of caribou by natives as the main cause of caribou decline in the 1900s. McKay (1998), drawing from the comments of his interviewees and his own knowledge, concluded that caribou populations were much larger than today. Proof of larger herds, migrations and extended range were not only found in TEK gathered from elders, but also from old game trails, where hooves from ungulates resulted in paths cut 'twelve inches deep' in the forest floor. According to McKay (1998), migrating herds composed of several hundred if not thousand individuals ranged across the entire study area. These northern herds migrated the entire length of the Rocky mountain trench, "perhaps as far as the Kechika and Rabbit River Areas" and the Ospika, Akie and Peace Rivers. From the east, the herds crossed the Finlay and Parsnip rivers and arrived as far south as present Fort St. James. McKay (1998) hypothesizes how such migration ceased because of man-made obstacles, over-hunting, strong increases in the 77 number of moose and wolf populations, industrial activities (including the creation of Williston Lake) and changes in natural patterns (i.e. weather, vegetation, fire patterns, etc.). 78 (Hull. Tobey. Nak 'azdli elders speak. McKay: Pre-cuntact limes/early ISOOs) herds composed of hundreds of caribou (W. Julian. Nak'uzdli elders speak). Caribou hunted with bow and arrows in piv-contact times and par! of traditional subsistence througout the study area in the ISOOs. Possible large migrations acniss nearby mountainous regions, including Mt. Pope, Alt. Shass. southern Takla, Mitchell and Hogem ranges. Moose, mentioned as entering the area only in the late ISOOs and early 1900s. (Fraser. 1806) In Stuart Lake There anno large animals cxce.pt the caribou which is too sly for us' (Morice, 1860-1900) ' M o o s e and caribou, w h o s e h a b i l a l is m o s t l y in i h e n o r t h . C a n b e p r o c u r e d o n l y at d i s t a n c e from beaten tracks' —sis O n (Harmon. IS! 1) Harmon reaches settlements near Trembleur Lake. Describing the local natives, he mentions thai 'at times they kill a caribou'. He then continues his trip north, during which he sees caribou. (J. Stuart. /,V/5> hew caribou in the. studv area. • (Harmon, 1811) No moose found on western side of Rockies, except f e w struggling ones. In McLcod Lake he mentions ihe presence of few moose and occasionally caribou. (Anderson, 1867) Moose killed near junction 4 Necbako-Stuart rivers I — s | (Nak'azdli elders speak, late 1800s to early 1900s). 'Heard from the Beaver Indians (Peace region?) That large animals with horns were all coming soon' (Turner-Turner, 1866,1880) ' M o o s e killed within 18 miles of Fort St. J a m e s ' Figure 3.7. Timeline of historical observations of caribou and moose gathered from other written sources f i. P 2 1859-1910' 1810-1815 1877 1950 - ' 4 ^-t t • « , ' 01800s-1900s • i" Vs. 1880s v- Swannel 'Rarrfjes -•park N 'A ®1800s 1800s k WiHisfon .v ' ,.-» , • , • * "b \ • ' ' r* • — .Tv. ' ? Hogem * NS' 1811 ^^ T'- . v. . ,, * V-Dzitl'ainli Dzitl'ainli * » "(Middle River)- V ' < T T - • ... Salmon ytLake A A , 1800s : . 1800-1830'-» iqnno - . V f i ' V - * " * sa 1888 Binche ® Caribou Hist. Observ. Moose Hist. Observ. 9 Research Locations • ^ Pe ( " 3 Late 1800s U P . - early 1900s mt&ope^ .. ^ . v f * F t . St. James, 1 ' Legend Q 7> . 1800s 1900s 1866 - « u a ».' Lake y -Lake . t , \\ ? % • Si' ^ J * ' Pre-contact, Water Features Protected Areas 1860s : i .a Ss^ Figure 3.8. Caribou and moose historical observations gathered from other written sources plotted on a map of the study area using GIS software. 80 3.8 Evaluation of Results from Primary Written Sources I divided primary written evidence into several categories: early Euro-Canadian accounts of local life and travels, historical-anthropological studies, surveys and reports, stories and legends of the Dakelh collected from the Treaty Office of the Tl'azt'en Nation and other interview projects conducted in the area. These works can be further subdivided into three broad groups based on the perspective and experiences of the author. The first group consists of works by early colonialists, including explorers and fur-traders such as Simon Fraser. Documents created by this cluster of authors often reflect observations and ideas distinctive of the new frontier: minimal knowledge about the surrounding region, search for suitable places to settle and trade, and meticulous descriptions of the environment traversed during travels. The second category is composed of Euro-Canadian settlers of Fort St. James, including missionaries, who settled in the study area from the second half of the 1800s to the early 1900s. These authors differ from the first group by a superior knowledge of local people and environments. The third type of other written sources is derived from interview projects conducted in the area, mostly among First Nations. Given the extremely variegated character and background of the authors of historical written sources, the evaluation of these sources requires generalizations. Overall, the advantages of historical written sources include accessibility, a high number of statements, and a range of perspectives across the variety of titles. Disadvantages include the need for individual interpretations and evaluation, and lack of information about the origin of the data contained in some of the works. 81 #1: Output and efficiency of data collection The primary written sources provided 25 statements, of which 17 related to caribou and eight to moose. Of this total output, descriptive works of missionaries and early explorers account for the largest amount of data. Overall, primary written sources proved a very efficient source of data. Their accessibility is second only to secondary literature, as most works are obtainable from universities and specialized private and governmental archives. My collection of primary written sources lasted approximately five months of discontinuous work. The process was facilitated by access to materials collected by the Tl'azt'en Nation and contained in their Band archives. #2: Temporal precision, accuracy and objectivity Of 25 statements, nine provided the year of observations, seven are less specific and nine are generic. For caribou, six statements supply a year, seven offered less specific descriptions (e.g. related to statements such as 'my father's time') and four others were generic. For moose, three statements provided a year, two were less specific and three were generic. Diaries and accounts of early explorers figure amongst the most precise and accurate sources of information, as they present a structure similar to that of the HBC journals. The information of late settlers and missionaries of the second half of the 1800s, though also precise, have a lower accuracy; triangulation with other sources suggested that the statements contained in some of these works might be redundant with earlier observations. Lastly, interview projects, notably McKay (1998), have the same temporal precision, accuracy, and objectivity as projectspecific interviews. #3: Spatial precision, accuracy and objectivity Five caribou statements supply specific geographic references, while the remaining 14 are regional. The ratio is more favourable for moose: of eight statements, five provided specific 82 information, and three were regional. Overall, the primary written sources I consulted have shown moderate spatial accuracy, though each title differs considerably. Interview projects contained spatially accurate information, while the remaining material, with few exceptions, tended to describe geographic locations in general terms. #4: Document animal abundance The overall ability of primary written sources to document the historical abundance of caribou and moose is poor. Of 17 caribou observations, 15 are generic and only two provide specific numbers. The ratio is slightly higher for moose, though still below the average of other sources: two specific and six generic. The sources vary in their description of abundance. For instance, the diaries of Harmon (1904) offer accurate descriptions of single observations, but lack the spatial and temporal breadth of observations from native sources. Summary Primary written sources offer the second largest contribution in terms of quantity of information. The works of early explorers and fur-traders operating in the early decades of the 1800s form the bulk of this material, though the quality of the information provided by this group of authors is less informative than other interview projects such as that of McKay (1998). These titles share comparable attributes to HBC records in terms of spatial and temporal accuracy. The documents created by later settlers and missionaries in the area vary in both temporal and spatial precision. Within this category, the publications of Morice (e.g. 1897) offer a significant amount of ethnographic information and descriptions of the study area. Interviews conducted with local First Nations, and specifically that of McKay (1998), offer the same quality 83 of information of project-specific interviews, such as I completed. As such, they present moderate temporal precision and higher spatial precision. 3.9 Summary of Findings Secondary literature, semi-structured interviews, HBC journals of Fort St. James, and historical written evidence each offer different interpretations of the history of caribou and moose in the study area. Secondary literature, and specifically archaeological material, has provided evidence of caribou presence and use by First Nations during pre-contact times and during the 1800s. On the contrary, moose does not figure in excavations and pictographs, and artefacts constructed from moose materials are only available from 1920. Anthropological works generally uphold the idea of scattered populations of caribou around Stuart Lake and in the lowlands, though some authors do not exclude the possibility of more numerous herds in pre-contact times (Tobey, 1981; Hudson, 1983). These sources also reveal that moose were scarce to absent until the late 1800s to the early 1900s. Ecological studies do not concur on historical abundances of caribou and moose populations in the upper plateau of BC, though Spalding (1990, 2000) maintains that caribou were present in the lowlands of the study area in scattered, low-density populations and that moose, although even more scattered, might have always been present in the sub-boreal interior. Results from the interviews conjure hypotheses of much larger populations of caribou in pre-contact and early historic times than those observed today. Interviewees suggested that caribou were common in the lowlands east of present Fort St. James, around Fort St. James and in the immediate vicinity of Mt Pope, Murray Ridge, Mt. Shass, Mt. Sidney Williams, Mt. Tsitsutl and the Hogem-Mitchell (Takla) and Swannell ranges (south Omineca). These populations began 84 to decline from the late 1800s up to the 1950s, and in the view of some interviewees never recovered to previous levels of abundance. Most participants reported that moose entered the study area at the end of the 1800s and were scarce until 1920-1930, at which point populations increased dramatically. HBC journals hint at the presence of moderate caribou densities around Fort St. James, specifically near Carrier Lake, Mt. Pope-Murray-Ridge and Mt. Shass. One of these statements also suggests that moose may have been present in the area as early as 1832. The discontinuity of the journals prevents documentation of the history of caribou and moose in the area after 1850. Other written sources provide conflicting evidence depending on the cultural origin of the author or interviewee. The documents of early settlers and explorers residing in the area uphold the idea that caribou populations in the lowlands were scarce, or at least not abundant enough to play a significant role in their sustenance. Moose were noted by non-aboriginals as being either absent from the area or present in very scattered populations throughout the second half of the 1800s, with a marked increase in the 1900s. Conversely, aboriginal accounts hint to the presence of much greater caribou populations than those observed today, specifically in the lowlands and mountainous regions of the study area. Caribou were deemed particularly abundant in pre- contact and early historic times, when large migrations were reported. The decline of caribou began in the late 1800s and in the early 1900s, and in the opinion of many participants never recovered to match their historic distribution or levels of abundance. Moose reportedly entered the study area only in the 1900s, and increased in numbers rapidly after the 1920s. In summary, results from the sources I reviewed confirmed that the distribution of caribou was greater than it is today, and that it incorporated the lowlands of the study area. In the second half of the 1800s, caribou disappeared from the vicinity of Stuart Lake, and became available to 85 hunters only in the mountains and 'outside beaten tracks' (Morice, 1910). The descriptions of past caribou abundance varies depending on the source considered, though in general the four sources suggest the existence of larger historical populations of caribou, particularly in the early 1800s, compared to today. Considering moose, HBC journals and non-native accounts point to their early occurrence in the study area (as early as 1832), while First Nations participants of this project and most of McKay's (1998) interviewees maintain that moose did not enter the region until the late 1800s or the early 1900s. All sources concur, however, on a dramatic increase in moose populations beginning sometime between 1880 and 1920. 3.10 Evaluation: Summary of Results and Comparison of the Sources In this section, I provide a summary of the strengths of each source using the criteria and sub-criteria discussed in Section 2.8. I specify the total number of statements, the numbers per category and some general features of each source. I ranked each source on the evaluation criteria using a 5-point qualitative scale (0= very poor 1= poor 2=medium 3=high 4=very high). The sum of these values provides a quantitative value of the general performance of each source. The sources with the highest ranking in output of information and efficiency of data collection (evaluation criterion #1) are other written sources and interviews. Primary written sources are accessible in university libraries and specialized archives, provide large amounts of data, and can be effectively employed as stand-alone material. In contrast, HBC journals and interviews were more difficult to obtain or analyse, while secondary literature supplied insufficient amounts of information despite its accessibility. 86 Literature Other Written Evidence HBC Journals Interviews Secondary Literature (Summary) Scientific Anthropological Literature A rchaeological Literature Medium Very Poor Poor Poor Poor Medium Very High: all statements specify a day of observation High: 5 specific statements and 5 broad. Often include descriptions of places where hunters found or observed ungulates Medium: 4 specific High: 10 specific statements. High: 5 statements specify statements (year/decade), 24 16 broad, 2 regional. numbers, 23 gcneric. gcneric. Participants retained Participants provided excellent memories of generic but meaningful wildlife locations descriptions of historical animal abundance Poor Very Poor Poor Medium: 5 specific statements. 5 broad. Generally provide detailed descriptions of animals taken or encountered, but not of populations. 25 statements, 17 caribou, 8 Medium: 9 specific High: 8 specific statements, Medium: 4 specific moose. High: high output and statements (year), 7 specify 17 broad/regional. The type statements, 21 generic. Generally provide ease of access despite the dates with ±50 ys, 9 generic. of source considered different formats of written Precision, accuracy and determines spatial accuracy information on wildlife at the regional scale, but some evidence objectivity arc dependent on titles retain greater accuracy the type of source considered in describing historical animal abundance 10 statements, 8 caribou, 1 moose, 1 n.a. Very Poor: in over 3,000 pages of records scanncd only 10 rccords found Very Poor Very High Poor 6 titles. High: poor output but easily accessible using academic resources and specialized archives 3 titles. Medium: poor output but easily accessible using academic resources and specialized archives 4 titles. Medium: poor output but easily accessible using academic resources and specialized archives 13 titles, Medium: poor output but easily accessible using academic resources and specialized archives 52 statements, 18 caribou, 8 moose. 26 miscellaneous. Medium: good output but difficult process of data collection #4: Document animal abundance #3: Spatial precision, accuracy and objectivity #1: Output and efficiency of #2: Temporal precision, data collection accuracy and objectivity 10 10 Summary £ » >*> c a o _. SS S3 ss na C v; w 3 -a £L o »an C63 « <» O o a 3 st N> » be n an a o o s < £> » S3 S ». 89 ao s o s » E sr n n s » aS mm o £ a © B l. 1 sr l—J »1 MB. 89 S 2 S 'S « » S w V nn vo rtcr n » vn oas a *a O 3 Interviews offered the highest volume of data, though they required a lengthy process for data collection. In view of the accuracy and the number of statements supplied by participants, I considered this source as efficient as other written sources. Triangulation with other sources based on aboriginal accounts demonstrated a high degree of correspondence between historical observations and historical-ecological events. A lengthy process of data collection and limited results exemplified the HBC journals of Fort St. James. In addition, the analysis of this source was fraught by several difficulties of interpretation during content analysis, which likely influenced the accuracy of this method. The lack of utility of the HBC journals for this research is, however, entirely dependent on the focus on caribou and moose. As I noted for the Fort St. James journals, and as demonstrated in other historical-ecological studies, other species are reported more frequently and in detail. For instance, Viljugrein at al. (2001) and Erb et al. (2000) analyzed spatial-temporal patterns of mink and muskrats in Canada using the HBC archives. Their assessment demonstrates how species central to the fur trade enjoy ample coverage in the archives. In the analysis of temporal precision, accuracy and objectivity (criterion #2), interviews and other written sources are similarly characterized by a lack of temporal specificity. These sources, however, afforded more holistic descriptions of events for longer spans of time. As previously mentioned, the information originating from all sources of aboriginal informants was consistent in describing caribou and moose and their population changes through time and space. In contrast, HBC journals and some of the other written sources offered precise observations, but provided little information on general trends and dynamics. In terms of spatial precision, accuracy and objectivity (criterion #3), the descriptions of places and events offered by aboriginal and non-aboriginal interviewees across all sources were 88 frequently detailed enough to provide specific geographic locations. The HBC journals and other written sources supplied equally valid geographic accounts, while secondary literature provided mostly regional descriptions. The sources that most effectively documented the historical abundance of caribou and moose (criterion #4) are, again, aboriginal accounts. These statements lack the level of detail provided by the HBC journals and some other written sources, but provide a general description of past abundance and change through time. 89 4. DISCUSSION 4.1 Introduction The analysis of the various sources, including interviews, HBC post journals, other written sources and scientific literature has revealed two broad patterns. The majority of native accounts, derived from either interviews or other written sources, suggest that caribou previously inhabited the study area in greater abundance and distribution than those reported today. Conversely, the statements made by Euro-Canadian traders hint to a wider distribution of caribou in the 19th century but nevertheless to a scarcity of this species, and to the presence, albeit rare, of moose in the 1800s. These patterns are depicted in Figure 4.1, a synopsis of caribou and moose observations from 1800 to 1950. 4.1 Trends Amongst the Data Caribou in the 1800s: evidence for greater abundance and wider distribution Most of the evidence collected in this study suggests that caribou were more widely distributed, abundant, and more extensively used by First Nations in pre-contact times and throughout the 1800s than they were after the 1900s. The primary sources supporting this hypothesis are the interviewees of this project, the participants interviewed by McKay (1998), archaeological titles, as well as aboriginal accounts from other written sources (Hall, 1992; Nak'azdli Elders Speak, 2001). 90 P r e - c o n t a c t a n d 1 8 0 0 s - C a r i b o u p r e s e n t i n g r e a t e r n u m b e r s in s t u d y a r e a and part of First Nations traditional subsistence. M o o s e in w e s t e r n s e c t i o n s o f t h e s t u d y a r e a (Interviewee tf2: Interviewee $4: hue.rvie.weeTf7; Interviewee 09; Interviewee ftlll; HHCA. March 16. 1851: HHCA. March 17. 1852: II,ill 1992. Tnhe.v 1981. X'ak 'aidli elders speak. 200/: McKay. 1998: Jennets. 1977: Fraser. 1806). Caribou present in greater densities in lowlands and numerous in mountainous regions, including Mt. Shass. Pope-Murray Ridge, southern Ttikht, and foothills of Swutmel Ranges and South Omineca. I.urge migrations of caribou involving gran numbers of animals in mountainous region.':. Caribou playx greater pari in traditional subsistence at local First Nations. Declines of caribou siari in lale 1800s and t:t infinite throughout the first half of the 1900s. /Fraser, 1806) In Shtari Lake 'There arc no large animals except the caribou which is Ion sly for us' (Harmon. 1811) Harnwn reaches settlements near Trembleur Lake. Describing the local natives, he mentions that 'at limes they kilt a caribou'. He then continues his trip north, during which he sees carihou. (J. Sltiari. 1X15) Few caribou in the study area. {Interviewee £1. late 1800s -early 1900s) - First M o o s e (Inter vie wee U3. lale 1800s -early 1900s) • Fin. I M o o s e (Interviewee PH, late ISOOs -early 1900s) - First M o o s e (Interviewee n2, 1896) - Kirsr M o o s e (Interviewee #4, 1898) - First M o o s e (Interviewee #7. 1 9 1 1 ) - First M o o s e ( l n i c r v i e w c e f l l I. 1918) - First M o o s e 1800s • C a r i b o u scarce a r o u n d the Fort. (Morice, 1897. 1920: ./. Stuart. 1X15: Harmon. 1904: HHCA, Jan. 11. 1X29; huerviewce U5. Inlen-iewee H8). Canhou scarce around the Fori, hut present in mountains and 'awayjivai beaten trucks'. HBC A March 6, H B C A B.188/U/I7 M a r c h 16, 1 9 3 2 A n indian h a s killed t w o m o o s e deers' " M o o s e in M e L e o d and eastern sections of t h e s t u d y a r e a in e a r l y ISOOs" B.IS8/a/20 Ml 'Caribou are reported numerous in the mountains opposite Tache' (Harmon, l g M ) N o mu()sc f,lliml o n w c s t c m 5jac „f (Interviewee #3) R « « k i e s . « < * p t lew " M v grandfather used snuggling ones, to talk about 1.0 moose I" Mcl eod Lake in (his urea, they used h e mentions the [O BO up north around Presence of few Bear Lake and moose and that area, occasionally caribou. (Interviewee. H2) 'Following widespret id famine, all southern Takle caribou are hunted. Populations never recoveredafter the episode. " M o u s e i n t h e i n t e r i o r in t h e s e c o n d half of the 1800s" ( N a k ' a z d l i elders speak, late 1800s to early I900s>. ' H e a i d from the B e a v e r Indians (Peace region?) Thar large animals with horns were all coming soon' (Andcrs„n> |g,>7) M o o s e killed near junction N e c h a k o - S t u a n rivers (Turner-Turner, 1866/1880) ' M o o s e killed within 18 miles of Fort St. J a m e s ' Figure 4.1. Master timeline of historical observations of caribou and moose derived from semi-structured interviews with local aboriginal and non-aboriginal elders, HBC journals of Fort St. James, other written sources and secondary literature. 91 In addition, two HBC references (Fort St. James Journals, March 16, 1851; March 17, 1852) and further statements from miscellaneous authors contained in written sources offer additional evidence. Interviewee #2 spoke of "enough caribou to live on all around" (italics added). His observation is confirmed by interviewee #4, who mentions "lots of caribou" in the vicinity of Fort St. James, while interviewee #7 provides a very fitting description of higher populations: "...before moose arrived caribou were not just in alpine country. They were (italics added). everywhere..." Other sources, and particularly the interviews collected by McKay (1998), seemingly confirm the presence of numerous caribou in lowlands and greater populations on Mt. Pope and Murray Ridge, Mt. Shass, the foothills of the Swannel and Hogem Ranges northnorthwest of Tezzeron Lake and Mt. Sidney Williams-Tsitsutl (southern Takla). Large-scale historical migrations were reported in southern Takla by interviewees #1 and #2, and by the elders interviewed by McKay (1998). As McKay (1998) explains, such migrations involved hundreds of animals from herds of the Wolverine and Omineca mountains and from the Takla Lake area itself. Caribou seemingly played a prominent role in the culture and subsistence of aboriginal communities found across the study area. The information provided by the pictographs of Fort St. James and their interpretation by Mitchell (2006) highlights the importance of this ungulate for pre-contact and historic aboriginals of the study area. Caribou are depicted at multiple sites; in addition, Mitchell (2006) reports how the caribou symbol was used in other traditional media of communication. Interviewees #2, #4, and #6 recall caribou use for foodstuff, blankets, scrapers, sinew and the stomach as fat container. Morice (1906, p. 66) describes how the Carrier traditionally found beaver by "sounding the ice in different directions with caribou horns..." Hall 92 (1992) wrote that "...clothing and moccasins were made from the hides of caribou and the beaver, for clothing the latter being the warmer..." and that "...sinews of the caribou, and elk, were used as thread for piercing together clothing, moccasins, and blankets." Caribou in the 1800s: competing evidence for scarcity The historical information gathered from early explorers of the area such as D. Harmon (1904), S. Fraser (in Lamb, 1960), J. Stuart (in Morice, 1897), entries in the Fort St. James HBC journals, and also interviewees #5 and #8 point to scarcer caribou populations in the study area than those reported by native sources. J. Stuart, one of the founders of Fort St. James wrote in 1815: "we have no buffalo or deer, except the caribou, and not even many of those" (quoted in Morice, 1897, p. 95). The lack of statements in the Fort St. James HBC journals could be interpreted as compelling evidence of caribou scarceness. If caribou had been present in significant populations around Stuart Lake, the traders of Fort St. James would have mentioned this food source more frequently in their accounts. Such a hypothesis seems particularly correct in light of the scarcity of food that characterized life in New Caledonia (Klippenstein, 1992). Consider, for instance, that statement of G. Simpson in 1828 regarding the provisioning of Fort St. James: The establishment is maintained on fish, of which there is a variety, say carp at the opening of navigation, a small species of salmon about the size of herrings in summer; a larger kind [...] (but spent or in a dieting state being out of season) in the fall [...] a few white fish in the winter which with the occasional treat of berry cake prepared by the Natives, and a Dog Feast on high days and holy days constitute the living of nearly all posts of New Caledonia. (Morton, 1988, p. 167). In order to alleviate the dependency from fish and native supplies, within the first years of the establishment of Fort St. James the traders of the North West Company began planting 93 gardens and importing livestock (Hudson, 1983). Whenever fisheries failed, however, the traders of Stuart Lake were forced to consume their livestock or import provisions from other posts. Morton (1988, p. 222) reports the occurrence of such an episode in 1861, when over 70 horse loads of foodstuff were sent to New Caledonia because of the failure of the salmon run the previous fall. Unfortunately, as the Fort St James HBC records are missing for the years 1856-1892, it is not possible to acquire information on the role of caribou for subsistence purposes during the second half of the 1800s. Towards the end of the 1800s and in the 1900s moose, and possibly other species, might have begun to appear in the study area. For example, in a statement from the HBC post journal dated March 5, 1895, the writer reports that: "many deer are now being killed by the Indians of this side of Necoslie" [italics added], I conclude that in the 1800s, apart from the occasional kills near the Fort, the fur traders did not observe large numbers of caribou in the area, or were not able to hunt caribou as successfully as natives were. Moose in the 1800s While the lack of mention of large prey species and the provision problems of early traders suggest that moose were rare across the Plateau, several statements contained in the primary sources hint to their presence in the proximity of the study area during the 1800s. This evidence is consistent with the work of Spalding (1990), who concluded that moose of the sub-boreal interior (including the study area) were scarce at the time of Alexander Mackenzie (1763) but "by the 1860s, moose had begun to increase; by the 1870s early accounts indicate moose were numerous, particularly in the eastern half of this eco-region" (Spalding 1990, p. 5). 94 Reports of moose on the western side of the Rockies begin in the early 1800s with a statement from Harmon: Sicannies" [Sekani] ...they remain on this side of the mountain where they find buffaloes, moose and deer. On the other side [i.e. the western], none of these animals except a few struggling ones are to be found. (Harmon 1904, p. 156). In March 16, 1832, the Fort St. James journals record the following: "an Indian [...] has killed two Moose Deers." This statement is, by itself, one of the earliest mentions of moose in the study area. C. M. Turner-Turner (1888) mentions the occurrence of moose near Fort St. James in 1887, while Anderson (1872) wrote about moose being killed at the junction of the Stuart/Nechako Rivers. A.G. Morice, oblate missionary in Fort St. James from 1885 to 1904, comments on the availability of large ungulates in the study area: We have mentioned venison. By this we mean the flesh not only of caribou and of moose, which could be procured only at a distance from beaten tracks, on or near the mountains, whereon the hunters roamed for weeks at a time ... (Morice, 1930, p.66-67) Statements from interviews with First Nations individuals carried out by myself and those reported in McKay (1998), speak of 'first sightings' of moose in the last decade of the 1800s and in the 1900s in regions flanking the study area. Interviewee #3 talked about moose around 'Bear Lake', northwest of the study area. Interviewee #9 describes how 'before' moose arrived, "they used to go from Fort St. James to Cree country where they traded dried black bear and other goods for moose hides; they "never saw a moose but they did buy moose hides from them". 'Cree country' was almost certainly referring to regions east of the Rockies. During the 1800s, moose were abundant in the Peace region, and sporadically sighted on the ranges east of the Nechako plateau (Spalding, 1990). In 1813, Harmon observed plentiful populations around present Fort St. John (Spalding, 1990, p. 3), where moose were hunted to supply dried meat and 95 hides for the posts of the interior of BC. West of the Rockies, additional evidence collected by Spalding (1990) points to the presence of moose in the Parsnip and Finlay Rivers, Arctic Lakes, McGregor Ranges, near present Prince George, McLeod Lake, the upper Peace River (Williston reach), the Omineca region and the Lower Kechika River. Perhaps because of their more frequent travels along eastern supply routes, Euro-Canadian settlers and explorers seemingly met moose where natives did not. It is also possible, though only a conjecture on my part, that when referring to moose most Euro-Canadian accounts indicate regions outside my study area. If such an assumption is plausible, non-aboriginal statements would be supported by those native accounts describing the presence of moose north and east of the study area, 'Bear Lake area' and 'Cree country'. This possibility, however, does not take into account other statements made in the second half of the 1800s specifically mentioning moose within the study area (Anderson, 1972; Turner-Turner, 1988; Morice, 1930). In summary, EuroCanadian accounts suggest that moose albeit scarce was present in the study area during the second half of the 1800s. Moose in the 1900s While all sources concur on increasing numbers of moose in the 1900s, the majority of information collected from the interviewees of this project, some of McKay's interviewees (1998), and primary written evidence such as Hall (1992), suggest that until the late 1800s and the early 1900s moose were absent from the study area, and that this animal was unknown by sight to most native inhabitants of the area. Historical 'first sightings' are documented from 1880 to 1930, with two statements focusing on the years 1896 and 1898 and another in the 1910s. This cluster of data seemingly corroborates the hypothesis of moose absence from the interior 96 expressed in several ecological studies (Racey, 1936; Hatter, 1950; Bergerud and Elliott, 1986; see also Spalding, 1990) The first moose in Tl'azt'en and Nak'azdli traditional territories created a sensation. Interviewee #1 mentions that after the hunters followed a moose for two days, they 'caught it' and then "...invited all the people..." to share of its discovery, though the interviewee does not provide a specific date for that event. Participant #1 also reveals, however, that after that episode "they started to see moose a little, and after some time moose came." Interviewee #2 states that the first moose was killed in 1896, while Interviewee #4 claimed the first kill to have happened in 1898 near Trembleur Lake after a four-day chase. Interviewee #5, a non-aboriginal guide, remembered talking with natives of the area "...men that were already in their seventies at that time and started hunting when they were kids [...] they remember eating beaver, and that moose was a new delicacy when they finally moved into the area." Interviewee #6 recollects the first moose when she was a child: I was a child and my mother was looking for a baby-sitter for us, someone that had to look after us because they heard somebody had killed a moose, thirty miles from here, Fort St. James, and a bunch of them were going to get it, and my mum was going with them. Everybody was surprised somebody caught a moose. That's why; they didn't even know what it looked like at the time. Interviewee #9 remembers her father working for the HBC ferrying goods to and from Prince George. Encountering moose on the way surprised the ferrying party: ".. .That's where they've seen that moose for the first time, they said it came out of the blue just to stare at. That moose was so awesome for them; they could not believe it was so large. That is the first time in the 19th hundreds. That's when, yeah, the 19th hundreds, that's when they first saw moose..." Estimates based on the interviewee age suggest that this encounter most likely happened either in the late 1800s or in the 1900s. In the collection of interviews in Nak'azdli Elders Speak 97 (Nak'azdli Elders Society, 2001) another elder recalls how different people followed the first moose for several days, and how a few years later they started to enter the area. The reaction that the appearance of moose created in the native communities and the almost unanimous opinions concerning their absence in the 1800s within native sources cannot be disqualified as purely coincidental. Whereas some Tl'azt'en and Nak'azdli might have recognized moose as being present in the east, we must conclude that their appearance in the study area was not noted before the late 1800s or the early 1900s. 4.2 Historical Distribution and Abundance: Conclusions Caribou Relative to present-day range occupancy (Poole et al., 2000), the majority of the historical information suggests that caribou had a greater distribution across the Nechako lowlands during the 1800s, and specifically, inhabited the areas surrounding Stuart Lake. The preferred habitats of these historical populations were mainly medium and high elevation, though compared to current habitat use caribou probably ranged across a wider variety of environments. The sources do not concur on caribou abundance in the historical and pre-contact period. It is important to highlight, however, that what seemed abundant to aboriginal peoples might have seemed scarce for non-aboriginals, and vice versa. Since there is no historical standard or context by which to standardise these relative quantitative terms, we cannot directly compare such measures among sources. Consider, for instance, the entry in the Fort St. James HBC journals made December 12, 1820, stating that: "The Marie des dent Biches Boy arrived & brought one Large Beaver & one small whole [sic], he is at present in the vicinity of Carriers Lake but complains of a scarcity of beaver - has killed no Rein Deer as yet" (Fort St. James HBC Journals, 98 B. 188/a/l) [italics added]. A direct interpretation of this statement suggests that the author of the journal expected the hunter to find reindeer (caribou) near Carrier Lake, but this is impossible to confirm. On another occasion, a journal entry hints at plentiful caribou in the vicinity: "all the Indians have now left here for their several hunting grounds - caribou are reported to be numerous in the mountains opposite Tache... March 6, 18510) [italics added]. " (Fort St. James HBC Journals, B.188/a/20, As there is no reference point for 'numerous', we cannot translate this statement into an absolute or even relative measure of abundance. In summary, I believe the data offers evidence of higher caribou abundance in the precontact period and in the early 1800s. While historical herds were certainly more numerous, it is unclear, however, just how much higher those numbers were in comparison to present abundance. Native peoples' accounts, the analysis of the pictographs conducted by Mitchell (2006), and other ethnographic material scattered amongst the sources provides evidence of substantially greater populations in both lowlands and mountains. In addition, such data suggests that this ungulate played a much greater role in the culture and traditional subsistence of First Nations of the study area than what was previously assumed in other anthropological research (Hudson, 1983; Morton, 1988; Klippenstein, 1992). On the other hand, Euro-Canadian historical records hint to the presence of low-density populations, though as argued, the reinterpretation of their statements can also suggest evidence of higher abundance. Possibly, seasonal caribou migrations influenced the perception that aboriginal and non-aboriginal people had of caribou. Moose No source mentions moose in pre-contact times, while native and Euro-Canadian accounts do not concur on their presence in the study area throughout the 1800s. Historical written sources offer 99 very few clues concerning this difference, while the statements provided by native sources lack sufficient temporal accuracy to determine with exactness when the first moose appeared in the area. The majority of the data supports, however, the hypothesis that moose were either absent or extremely rare in the upper plateau until the 1900s, at which time they began to increase in Tl'azt'en and Nak'azdli traditional territories. Early sightings might be attributable to isolated animals wandering in the region from neighbouring areas that housed established populations. No evidence supports the presence of moose in the western sections of the study area in the first half of the 1800s. 4.4 Hypotheses of Caribou Decline With the passing of time, caribou populations gradually abandoned the lowlands of the upper plateau of the interior of BC. In the late 1800s and 1900s caribou were reported as being available only in the mountains or, as Morice recollects, "at distance from beaten tracks" (1930, p. 66-67). Across the four sources of historical ecological information, numerous authors and interviewees have proposed mechanisms or reasons for the contraction in the distribution of caribou. Although these reasons vary amongst the sources and are not supported by compelling evidence, they can serve as premises for further investigation. I organised the various mechanisms as four broad hypotheses focused on 1) habitat change, 2) increased predation, 3) loss of habitat for caribou, and 4) over-hunting. 100 Hypothesis one: habitat change One of McKay's (1998) interviewees, whose informants had been two respected Takla elders, deemed the large-scale caribou migrations 'over by 1930s'. What is left was, in their opinion, the remnant of larger herds. Furthermore, winters were in their view much longer, the tree line lower, and this allowed for 'better caribou country.' Similarly, a statement found in Nak'azdli Elders Speak (2001) highlights how caribou were getting scarcer in the study area at the time moose arrived: At this time the Lht 'at 'en people (Sekani) told the people here that it was heard from the Beaver Indians, that large animals with horns were all coming soon. Now at this time the caribou moved from the lowlands to the mountain country. The people had to hunt upon the mountains for the caribou. It was a long way to go to the mountains, as the caribou were getting scarce. So my dad told me this. He was just a young man then, when he first saw the tracks of what looked like two animals. One was big, the other was small. On the ground, there were three or four inches of fresh snow and he was able to track the animals. The animals kept traveled on, eating ends of willows. My father got close to Benoit Ah'uille's trapline and turned around, leaving the tracks. It was late at night when he got back to the cabin at Eagle Lake [...] so the story goes on that Benoit Ah'uille followed the tracks as far as Beaver Lake and he too, turned around leaving the tracks. The next one to follow the animals was Leon (Cho) Prince. His trapline was on Stuart River. He followed the animals for a long distance and gave up and turned around. Then it was told that around Christmas time, the Stoney Creek people told their stories about the tracks. They said it must be what the Lht'at'en people meant, when they said that large animals with horns would be coming in the future. They called it Huda in their language. We call it Duni, but the white people called it moose. In a year or two, they became frequent in numbers. My father told to me this story. (Nak'azdli Elders Society, 2001, p. 55; italics added) Interviewee #4 supported this statement: "I think [that caribou declined] when the moose arrived..." The idea that with the passing of time wolves increased, that winters were more severe, and that the combination of both factors may have contributed to the decline of caribou was a common theme expressed by several interviewees. Participant #4 remembered: "There were lots 101 of caribou. Then all of a sudden they started to die out." Interviewee #2 recalled colder climates, the presence of more wildlife, and that in 1930s wolves increased: There used to be hundreds of them. They (wolves) lived on the ice yelling and yelling, we could hear them. It was very wise to kill them; we tried with traps and everything but we couldn't. Sometimes we got them with snares. Yeah, whenever they were getting too many. In the thirties, I think. As for other types of natural disturbance with the potential to affect caribou, interviewee #3 remembered a large forest fire, presumably at the end of the 1800s or at the start of the 1900s: Oh yeah, one year, that's before my time a fire went right across BC. Where did it start? Somewhere around this area. It went right across this area and then between the Fort and Vanderhoof. You see all that small pine? Lots of it, right through that, right to down to Prince George, Quesnel, and all that area. Went right across, big fire, that's before my time. My dad used to talk about it. The statements above provide some substantiation for the hypothesis of habitat change and, consequently, an increase in the availability of habitats preferred by moose. Given the limited amount of data available, however, the timing of the arrival of moose and their impact on caribou is unclear. Furthermore, there seemingly is a temporal gap of a decade or more between the years of an established moose presence in the region (the 1910s -1920s), and the decline of caribou in the areas surrounding Fort St. James in the late 1800s. This gap suggests that factors other than moose influenced the decrease of caribou, though the latter might still have played a secondary role during this transition period. Grayson and Delpech (2001; 2005) propose that periods of warming correspond to decreases in caribou range, possibly triggered by changing vegetation patterns and insect harassment. Changing snow depth is also known to have a deleterious effect on site selection and feeding habits of northern caribou (Johnson et al., 2004). Snowfall during gestation has the potential to affect birth weight, with the growth of herds stopping during higher-than average years of snowfall (Adams, 2005). In the anthropological sources Hudson (1983, p. 45, 65) dated 102 the end of a 'little ice age' in the area to 1850. In Hudson's opinion, this climatic shift was directly linked to the decline of caribou in the region. I was unable to find additional resources detailing the little ice age and its effects on local flora and fauna. Nonetheless, I cannot rule out that changes in climate, weather and fire patterns might have had a significant role in changing caribou habitats, or increasing the availability of early successional habitat for other ungulates such as moose. The effects of climate change are, nonetheless, difficult to pinpoint with precision, especially at the small scale. Hypothesis two: increased predation As my research objectives did not include a comparative analysis of the historical abundance of wolves or that of other predators, I am unable to define with certainty the occurrence and effects of increased predation on ungulate populations. Interviewee #2 and several of McKay's participants recollected the presence of 'too many wolves' (1998, p.4, 5, 6, 10). In contemporary ecological literature, increases in the number of wolves are recognized as a primary factor limiting forest-dwelling caribou populations (Bergerud and Elliot, 1986; Bergerud, 1988; Messier, 2000; Wittmer, 2005). Increased predation by wolves on caribou might have been triggered by the alteration of natural habitats through climate change and habitat modification (hypotheses one and three) and by the subsequent surge of alternate prey in the study area. The latter might not be limited to moose but incorporate other species. Hypothesis three: habitat loss due to anthropogenic influence and industrial activities Laliberte and Ripple (2004) describe how species richness in North America declined following Euro-American settlement during the course of the last two centuries. Industrial activities (e.g. 103 mining, logging, and recreational) and land clearing for settlements are recognised as primary causes of caribou decline (Oberg, 2001; Dyer et al., 2002; Schaefer et al., 2003; Vors, 2007). The importance of anthropogenic modifications of the environment in my study area is, nonetheless, difficult to substantiate. Several gold rushes in BC (1858, 1862, 1866, and 1869-73) brought increasing numbers of fortune seekers to the central and northern parts of BC. Although some of the miners passed through the study area, their numbers and the impact they might have had on local wildlife is unknown. Interviewee #3 states that during his grandfather's time, mining had been a principle cause of the decline of caribou found near Mt. Sidney Williams and Tsitsutl (southern Takla): Yeah there were blasts for mines; they were looking for gold up in Sidney Williams. I don't know when, it was not in my time; my grandfather was talking about it. That's why he said there were lots of caribou before there, but when they went there to hunt again caribou, they found none. They found the site where they have been blasting. I don't know how they got up there but they were blasting around that area so all the caribou moved out of there. They don't go there anymore, they went in Tsitsutl the next mountain to look for caribou and there's nothing there either. So, up, around Bear Lake that area, Johansson, lots of caribou there... The early 1900s were also characterized by an increase in settlements throughout the Nechako Plateau and Bulkley Valley. In 1889 and 1893, extensive surveys of the region were conducted to locate potential agricultural areas and map future settlements (Hudson, 1983, p.128). After the 1900s, more settlers moved into the region and began clearing tracts of lands for agricultural purposes. In 1914, the building of the railway from Edmonton to Prince Rupert on the Pacific coast triggered a wave of exploration and land pre-empting in the northern interior (Hudson, 1983). New legislation limiting Native's rights to resources access, the decrease in profits from the fur trade, epidemics decimating the native population, and failures in salmon runs, critical for 104 subsistence resulted in the northern Dakelh shifting from subsistence hunter-gatherers and trappers towards labourers, especially in the forestry sector (Hudson, 1983; Klippenstein, 1994; Brown, 2002). Naturally, such a change occurred gradually. Nonetheless, by the 1950s the Dakelh had been substantially integrated into modern socio-economic processes (Hudson, 1983). The effects that such socio-economic alterations had on wildlife are likely complex. The disruption of traditional native systems of resource stewardship caused by these events and the restriction of native's resource base (Brown, 2002) may have increased unregulated hunting and provoked the adoption of a more competitive hunting ethic, with large numbers of native and fur trader's alike thinking about their survival and profit rather than the sustainable use of edible species. Similarly, increases in the population of Fort St. James during the 1900s added pressure on ecological systems already strained by almost a century of fur trade. Despite such changes, however, it was not until 1940 that the study area saw significant growth in logging and mining (Morris and Fondahl, 2002). It is also possible that other developments outside the study area (e.g. settlements in the Bulkley Valley, the Omineca gold rush) had regional repercussions for ecosystems in the study area. Despite the lack of direct evidence, anthropogenic disturbances must be considered further when attempting to understand the reasons for the change in the distribution of caribou and moose in the region. Hypothesis four: over-hunting Hunting has the potential to severely effect caribou populations (Bergerud, 1974, 1978; James, 1999). Some of the statements from this research imply that over-hunting during periods of food scarcity might have played a considerable role in the eradication of local caribou. Interviewee #2 talks about a famine occurring in 1890, after which the entire herd of southern Takla (Mt. Sidney 105 Williams and Tsitsutl) was killed ("60-70 of it") to satisfy the needs of people in the region. This elder also mentions that after this episode periodic migrations across Middle River ceased until the 1950s, when a "...few caribou started to cross back [in the 1950s], two or three [animals] only, but they would never remain permanently as before." Hudson (1983) documented how in 1888 starvation among the natives, scarcity of fur-bearers, rabbits and other food animals, the failure of salmon fisheries, and unprecedented mildness of the winter of 1887-1888 underpinned profound socio-economic ad cultural transformation for the Trazt'enne. In addition, he documented how Tl'azt'en oral traditions recall movements of Babine people to Stuart Lake because of starvation. Interviewee #6 provided further supporting evidence for a starvation episode in the 1880s. Her father warned her about the dangers of famine: "he was born in 1873 but he heard a lot about starvation." In her opinion, the famine was around the 1870-1880, and her "dad used to talk about it a lot..." According to a number of interviewees, the rate at which caribou were harvested was quite high. Interviewees #6 (Nak'azdli) recollected going into the mountains when she was five or six years old, where her father "one time killed about 10 of them." Interviewee #8, related to #6, remembers how "my dad used to kill lots of caribou, about 10 to 50 and they skinned it all and my mother dried all the meat and she worked on the skins" (emphasis added). Interviewee #4 states that in early times ".. .they killed lots of caribou ..." (emphasis added). The statements presented above suggest that hunting of caribou in critical times might have played a key role in the decline of certain populations of the study area. The idea that aboriginal hunting in particular exceeded sustainable levels of harvest was common in the statements made by non-aboriginal guides interviewed by McKay (1998) and myself (interviewee #5). Examples of such statements are: "the [...] Indians are worse than the wolves for killing 106 game" and "...the Indians are hard on caribou." Interviewee #5, a non-aboriginal guide who operated in the late 1940s northeast of Fort St. James describes the following: I know, in one place where we hunt, there is a bunch of people that kill too many caribou, and we noticed a decline. You go next year and there is nothing there. We only hunt just enough for ourselves, you know my niece, nephews and uncles. But there are too many hunters out there. Interviewee #5 explained that the statement referred to native hunters who, in his opinion, killed large numbers of caribou in the country around Nation Lakes and Germansen Landing. Aboriginal over-harvesting has also been discussed in a historical context by Kay, (1994, 1997), Martin and Szuter (1999) and Laliberte and Ripple (2003). Kay (1997) suggests that moose biogeography in the interior of BC had been controlled by native hunters, who kept this species in check through systematic harvesting. In Kay's (1997) opinion, the subsequent abundance of moose was determined by the decline of native populations, following Europeanintroduced diseases. Martin and Szuter (1999) and Laliberte and Ripple (2003) employed the Meriwether Lewis and William Clark journals to demonstrate how species living in areas of higher native influence were less likely to persist. In the view of these authors, Native Americans were directly responsible for drastic ecological changes, including the over-harvesting of certain species used for sustenance. Conversely, other species were maintained by a prolonged native hunting pressure at low-densities, or well below the limits imposed on them by environmental constrictions. I did not find significant evidence supporting Kay's (1997) hypothesis of aboriginal over-harvesting of moose for the study area, though over-hunting episodes might have played a part in caribou decline. 107 4.5 Conclusions Secondary literature, interviews, HBC journals and primary written evidence portray a picture of drastic environmental and socioeconomic changes through the 1800s and the early 1900s for the study area. These changes acted concurrently and influenced the historical distribution of caribou and moose in the area. During the last decades of the 1800s, woodland caribou had abandoned the areas surrounding Fort St. James. Alternatively, moose, previously absent or rare, became more common, until in the first half of the 1900s it superseded caribou in several sections of the study area. The transition between caribou and moose during the last decade of the 1800s and the early 1900s is unclear, though at some stage the increase of the latter might have played by itself a significant role in the decline of caribou. While moose and caribou populations shifted, various statements suggest that humans were exercising an increasing influence on local environments. Trapping increased as new settlers populated the study area; caribou, one of the only big game species during the 1800s, was taken when encountered. Cultural and economical changes affecting traditional native societies during the same period might have contributed significantly to changes in the distribution of local fauna. For the Tl'azt'en and the Nak'azdli, access to resources in the Keyoh (the families' hunting-gathering grounds) was regulated through the clan system and the bahlats (potlatches) (Hudson, 1983; Morris and Fondahl, 2002). However, a number of factors - the disempowerment of traditional systems of governance, coupled with new legislation constraining native access and rights to resources, several epidemics decimating aboriginal populations, and the creation of reserves - changed long-standing patterns of human occupancy and traditional resource use (Hudson, 1983; Brown, 2002). Such changes could manifest as an increase in unregulated 108 hunting and/or habitat modification with a subsequent decline in caribou. The antagonism triggered by the arrival of white trappers and the fur trade in the area might have exacerbated episodes of over-hunting, while increasing the overall pressure on the local fauna. Hudson (1983) and Klippenstein (1992) argue how in the late 1800s the depletion of furbearers caused by intense trapping, coupled with periodic starvation episodes, contributed to deep social and economical changes of the Dakelh. In addition, it is unclear how miners participating in the gold rushes of 1858 and 1882 affected local environments. Wildfires may have accompanied mining activities; this would result in a reduction in the availability of caribou habitat and an increase in habitat for moose. My interpretation of historical evidence suggests that humans played a primary role in determining the contemporary distribution of caribou and moose. This pattern is consistent with other observations of historical species decline across North America (Bergerud, 1974; Ceballos and Ehrlich, 2002; Laliberte and Ripple, 2004). Hunting and human-induced modifications of the environment caused a direct increase in mortality of caribou and indirectly increased the number of moose, wolves, and predation on caribou (see Poole et al., 2000). Whether the changes in caribou and moose distribution started within the region, or were a product of events that occurred outside the boundaries of the study area is uncertain. However, these interacting effects highlight how extinctions of species and range retraction often result from a combination of seemingly unrelated factors (LoGiudice, 2001). 109 4.6 Potential Biases of Historical Ecological Information The evaluation of the four sources of data presented in Chapter Three has highlighted some potential biases. One of the key issues for historical data is that they are often available in discontinuous time-series (Swetnam et al., 1999). The lack of continuity characterizing the HBC journals is an excellent example of the challenges involved in the use of historical information. Temporal fragmentation increases the potential for bias and a reduction in the precision and accuracy of historical events. This may be reflected in the dating of historical observations, the distortion of events, or the loss of important information through time. For instance, much of the data related to moose observations in native sources is not temporally specific. Thus, it is not possible to provide any confirmation of the role of moose in caribou decline. For caribou, the lack of specificity of statements and written historical evidence prevented a precise description of the timing of decline. In terms of spatial accuracy, aboriginal sources tended to offer reliable geographic descriptions, particularly for the early 1800s. Aboriginal peoples undoubtedly held better knowledge than settlers and explorers of the environments of the study area because of their longterm occupancy in the region, traditional land-based lifestyles, and their activities as trappers and hunters in the first decades of the fur trade in Fort St. James. As a result, their statements tend be spatially accurate and more holistic in nature, while Euro-Canadian historical observations, while precise in time and space, does not offer the same long-term knowledge. Findings are also influenced by the methods adopted for the research. In this research, the approach I have taken likely shaped the overall quality and accuracy of the information collected. In retrospect, the interview process could have been improved to collect higher accuracy 110 information. Greater temporal accuracy might have been achieved using timetables to which the interviewees could have referred to or pinpointed observations. The spatial accuracy of statements might have increased by referring to maps more consistently. The use of certain words instead of others, and language barriers might also played a part in the shaping of the results, though I strived to maintain an objective and non-directional perspective. 4.7 Suggestions for Further Research As with all research, more data is always welcome. Possibilities for further information include additional interviews with Nak'azdli and non-aboriginal elders, as well as interviews with the Takla First Nations and perhaps with other Dakelh bands residing at Babine. In addition, my research revealed numerous related topics that deserve additional study. Additional examination of the historical patterns of resource use by Tl'azt'en and Nak'azdli could improve our understanding of the dynamics of caribou and moose and their relations to human activities. Particularly relevant would be research on the impact that social change and the fur trade had on ecosystems and on caribou and moose. This study could also benefit from supplementary documentation of the progression of historical settlements in the study area during the 1900s, and on the role of miners in the gold rushes of the 1800s. The collection of such material would require research in government archives and further interviews and has the potential to offer a better picture of the changes in caribou distribution during a dynamic historical period. The hypothesis of over-hunting discussed by several authors deserves further attention. Supplementary research could focus on the documentation of starvation episodes due to failure in 111 salmon runs, and on the effects of epidemics on aboriginal resource use. A further review of the archaeological literature would complement such investigations. The pictographs of Stuart Lake in particular deserve further attention. In retrospect, supplementary questions about the pictographs and other cultural artefacts concerning caribou would have, perhaps, further clarified the degree of historic and pre-historic presence and use of this ungulate around Stuart Lake. Probably the most fruitful direction for further research is investigation of HBC journals from the neighbouring posts. The documentation of the historical presence of caribou and moose in the northern interior of BC would be improved by a comparison of records from different locations. Such information could greatly increase our understanding of caribou and moose dynamics in the study area (Spalding, 1990; 2000). Finally, the study of environmental changes, and most notably historical climate and fire regimes of the region could assist with our understanding of the potential impact of these changing dynamics for caribou, moose and their habitat. Such data might be available in the HBC journals of Fort St. James, although the missing journals from 1856-1892 present a notable gap. Information from other nearby HBC posts and additional primary evidence, including dendrochronological evidence, soil profiles and further interviews could contribute significantly to a better understanding of natural disturbance processes that occurred historically across the region. 112 LITERATURE CITED Adams, L.G. (2005). Effects of maternal characteristics and climatic variation on birth masses of Alaskan caribou. Journal of Mammalogy, 86, 506-513. Alfred, P., Mitchell, R. & Michell, B. (1978). More stories of the Moricetown Carrier indians of northwestern BC. Moricetown Indian Band Council, BC: Young Canada Works Project. Allee, W.C., Emerson, A.E., Park, O., Park, T. & Schmidt, K.P. (1949). Principles of animal ecology. Philadelphia, PA: WB Saunders Company. Anderson, A.C. (1872). The dominion of the west: a brief description of the province of British Columbia, its climate and resources: the government prize essay [microfilm]. Victoria, BC: R. Wolfenden. Retrieved June 2006 from Geoffrey R. Weller Library, University of Northern British Columbia. Ames, K. & Maschner, H. (1999). Peoples of the northwest coast. prehistory. New York, NY: Thames and Hudson. Their archaeology and Areas Consulting Archaeologists Ltd. (1995). Archaeological overview of the Fort St. James land and resource management planning sub-region. Victoria, BC: Archaeology Branch. Archives of Manitoba (2007). Microfilm catalogue - types ofpost records. Retrieved September 2007 from http://www.gov.mb.ca/chc/archives/hbca/resource/post_rec/types.html#a. Arctic Borderlands Ecological Knowledge Co-op (2004). Retrieved October 2005 from http://www.taiga.net/coop/. Community reports 2003-2004. Balee, W. (1998). Advances in historical ecology. New York, NY: Columbia University Press. Ball, C.A.F (n.d.). Wildlife management of the Indians and the HBC. Retrieved June 2006 from the Tl'azt'en Treaty Office, Tache Native Reserve, BC. Ball, T.F. (1983). Preliminary analysis of early instrumental temperature records from York Factory and Churchill Factory. Syllogeus, 49, 203-219. Barr, W. (1995). The role of independent traders in the near-extermination of muskoxen on the mainland tundra of Canada, 1892-1915. Polar Record, 31, 425-426. Berg, B.L. (1998). Qualitative research methods for the social sciences. Needham Heights, MA: Allyn & Bacon. Bergerund, A.T. (1974). Decline of caribou in North America following settlement. Journal of Wildlife Management, 38, 757-770. Bergerud, A.T. (1988). Caribou, wolves, and man. Trends in Ecological Evolution, 3, 68-72. 113 Bergerud, A.T. (1978). The status and management of caribou in British Columbia. BC: Fish and Wildlife Branch Report. Victoria, Bergerud, A.T. & Elliot, J. (1986). Dynamics of caribou and wolves in northern British Columbia. Canadian Journal of Zoology, 64, 1515-1528. Berkes, F. (1993). Traditional ecological knowledge in perspective: concepts and cases. Ottawa, ON: Canadian Museum of Nature. Berkes, F. (1999). Sacred ecology: traditional ecological knowledge and resource management. Ann Arbor, MI: Taylor and Francis. Berkes, F., Colding, J. & Folke, C. (2000). Rediscovery of traditional ecological knowledge as adaptive management. Ecological Applications, 10, 1251-1262. Bishop, C.A. (1983). Limiting access to limited goods: the origins of stratification in interior British Columbia. In Proceedings of the American Ethnological Society, Native North America, 1979. New York, NY: Tooker, Elizabeth. Blackstock, M.D. & McAllister, R. (2004). First Nations perspectives on the grasslands of the interior of British Columbia. Journal of Ecological Anthropology, 8, 24-46. Blehr, O. (1990). Communal hunting as a prerequisite for caribou (wild reindeer) as a human resource. In Hunters of the Recent Past (300-326). London, UK: Unwin Hyman. Blood, D. (2000). Moose in British Columbia: ecology, conservation, and management. Victoria, BC: Ministry of Environment Publication, Lands and Parks, Wildlife Branch. Bond, L. & Russell, S. (1992). The Carrier of long ago. Prince George, BC: School District No. 57. Borden, C. (1954). Some aspects of prehistoric coastal interior relationship in the Pacific. Anthropology in BC, 4, 26-32. Boutin, S. (1992). Predation and moose population dynamics: A critique. Journal of Wildlife Management, 56, 116-127. British Columbia Conservation Data Centre (2008). List of Endangered Species and Ecosystems - woodland caribou. Retrieved November 2008 from http://www.env.gov.bc.ca/cdc/. Brooks, A.C. (1928). Invasion of moose. Murrelet, 11, 43-44. Brown, D. (2002). Carrier-Sekani self-government in context: land and resources. Geography, 12, 21-67. Western 114 Bryman, A. (2004). Social research methods, second edition. Oxford, UK: University Press. Carlson, R. & Dalla Bona, L. (1996). Early human occupation of British Columbia. Vancouver, BC: BC Press. Carlson, A. & Mitchell, L. (1997). Cultural heritage of a portion of the Fort St. James forest. Vanderhoof, BC: Traces Archaeological Research and Consulting Ltd. Carrier-Sekani Tribal Council (n.d.). Carrier tribe: culture and history. Prince George, BC: Carrier Sekani Tribal Council. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Carter, L. (2008). Recovering traditional ecological knowledge (TEK): Is it always what it seems? Transnational Curriculum Inquiry, 5. Retrieved October 2008 from http://nitinat.library.ubc.ca/ojs/index.php/tci. Catchpole, A.J.W., Ball, T.F. & Harrington, C. R. (1981). Analysis of historical evidence of climatic change in western and northern Canada. Syllogeus, 33, 48-96. Catchpole, A.J.W. & Halpin, J. (1987). Measuring summer sea ice severity in eastern Hudson Bay, 1751-1870. The Canadian Geographer, 31, 233-244. Catchpole, A. J. W. & Harrington, C.R. (1992). River ice and sea ice in the Hudson Bay region during the second decade of the nineteenth century. In The year without a summer? World climate in 1816, (232-243). Retrieved October 2008 from Arctic & Antarctic Regions database. Catchpole, A.J.W. & Moodie, D.W. (1978). Archiviaria, 6. Ceballos, G., & Ehrlich, P.R. (2002). Science, 296, 904-907. Archives and the environmental scientist. Mammal population losses and the extinction crisis. Corner, J. (1968). Pictographs in the Interior of British Columbia. Vernon, BC: Wayside Press. COSEWIC, Committee on the Status of Endangered (2002). COSEWIC assessment and update status report on the woodland caribou (Rangifer tarandus caribou) in Canada. Ottawa, ON: Committee on the Status of Endangered Wildlife in Canada. COSEWIC, Committee on the Status of Endangered Wildlife (2007). Specie at Risk - woodland caribou (Report). Retrieved October 2008 from http://www.cosewic.gc.ca. Creswell, J. W. (2003). Qualitative, quantitative, and mixed methods approaches, second edition. Thousand Oaks, CA: Sage Publications. Crowley, T. (1988). Clio's craft: a primer of historical methods. Pittman Ltd. Toronto, ON: Copp. Clark 115 Crumley, C.L. (1994). Historical ecology: cultural knowledge and changing landscapes. Santa Fe, NM: School of American Research Press. Crumley, C.L. (2003). Historical ecology: new paths towards collaboration. In Proceedings of the Conference on Urban Landscapes and Dynamics, Session 5, Cognitive Landscapes: Multi-Scalar Perspectives Urban Landscape Dynamics and Resource Use, August 28-31, Uppsala, Sweden. Retrieved October 2008 from http://scholar.google.ca/scholar?hl=en&q=crumley+2003+and+historical+ecology Cumming, H.G. & Beange, D.B. (1993). Survival of woodland caribou in commercial forests of northern Ontario. Forestry Chronicle, 69, 579-588. Cumming, H.G., Beange, D.B. & Lavoie, G. (1996). Habitat partitioning between woodland caribou and moose in Ontario: the potential role of shared predation risk. Rangifer, Special Issue 9, 81-94. Darimont, C.T., Paquet, P.C., Reimchen, T.E., & Crichton, V. (2005). Range expansion by moose into coastal temperate rainforests of British Columbia, Canada. Diversity and Distribution, 11, 235-239. Dogrib Treaty 11 Council (2001). Caribou migration and the state of their habitat: final report. Yellowknife, NT: West Kitikmeot Slave Study Society. Donahue, P. (1975). Concerning Athapascan prehistory in British Columbia. Wayside Press Ltd. Vernon, BC: Dormann, C.F. & Woodin, S.J. (2002). Climate change in the arctic: using plant types in a metaanalysis of field experiments. Functional Ecology, 16, 4-17. Duff, W. (1951). Notes on Carrier social organization. Anthropology in BC, 2, 28-34. Dyer, S.J, O'Neill, J.P., Wasel, S.M. & Boutin, S. (2002). Quantifying barrier effects of roads and seismic lines on movements of female woodland caribou in northeastern Alberta. Canadian Journal of Zoology, 80, 839-845. Edward, R.J. (1958). Landforms and caribou distribution in British Columbia. Mammalogy, 39, 408-412. Journal of Erb, J., Stenseth, N. C., & Boyce, M. S. (2000). Geographic variation in population cycles of Canadian muskrats (Ondatra zibethicus). Canadian Journal of Zoology, 78, 1009-1016. Foster, D.R. (2002). Insights from historical geography to ecology and conservation: lessons from the New England landscape. Journal of Biogeography, 29, 1269-1275. 116 Foster, D. R., Orwig, D. A. & McLachlan (1996). Ecological and conservation insights from reconstructive studies of temperate old-growth forests. Trends in Ecology and Evolution, 11, 419-425. Furniss, E. (1993). Dakelh Keyoh: the southern Carrier in earlier times. Quesnel, BC: Kluskus, Nazko, Red Bluff and Ulkatcho Indian Bands. Goodison, L. (1990). Moving heaven and earth: Sexuality, spirituality and social change. Hammersmith London, UK: Pandora Press. Grayson, D.K., Delpech, F., Rigaud, J.P. & Simek, J.F. (2001). Explaining the development of dietary dominance by a single ungulate taxon at Grotte XVI, Dordogne, France. Journal of Archaeological Science, 28, 115-125. Grayson, D.K., Delpech F. & Rigaud, J.P. (2005). Pleistocene reindeer and global warming. Conservation Biology, 19, 557-562. Hall, L. (1992). The Carrier, my people. Abbotsford, BC: CMY Prepress. Haney, A. & Power, R.L. (1996). Adaptive management for sound ecosystem management. Environmental Management, 20, 879-886. Hare, P.G, Greer, S., Gotthardt, R., Farnell, R., Bowyer, V., Schweger, C. & Strand, D. (2004). Ethnographic and archaeological investigations of alpine ice patches in southwest Yukon, Canada. Arctic, 57, 260- 272. Harmon, D. (1904). A journal of voyages and travels in the interior of North America, between the 47th and 58 th degree of N. lat., extending from Montreal nearly to the Pacific, a distance of about 5,000 miles: including an account of the principal occurrences during a residence of nineteen years in different parts of the country / by Daniel Williams Harmon; [microform], Toronto, ON: George N. Morang & Co. Retrieved September 2007 from Geoffrey R. Weller Library, University of Northern British Columbia. Harmon, D. (1957). Sixteen years in the indian country: the journal of Daniel William Harmon, 1800-1816 / edited with an introduction of W. Kaye Lamb / maps by C. C. J. Bond [Microfilm], Toronto. ON: MacMillian Co. of Canada Ltd. Retrieved September 2007 from Geoffrey R. Weller Library, University of Northern British Columbia. Harris, C. (1997). Native lands and livelihoods in British Columbia. Historical Geography, 30, 15-32. Harris, D. & Ingram, G. (1972). New Caledonia and the fur trade: a status report. The Western Canadian Journal of Anthropology, 3, 179-195. Harris, L.D. & Wasilewski, J. (2004). Indigeneity, an alternative worldview: four R's (relationship, responsibility, reciprocity, redistribution) vs. two P's (power and profit). 117 Sharing the Journey towards conscious evolution. Systems Research and Science, 21. Retrieved August 2006 from ABI/INFORM Global. Hatter, J. (1950). The moose of central British Columbia. Pullman. Behavioural State College of Washington, WA: Hatter, I., Harcombe, G., Stanlake, L., & Bethune, A. (2000). Caribou in British Columbia: ecology, conservation and management. Victoria, BC: Ministry of Environments, lands and Parks. Hatter, I.W., Quayle, J. & Ramsay, L.R. (2004). A Conservation status assessment of the mountain caribou ecotype based on IUCN red list criteria. In T.D. Hooper, Species at Risk 2004 Pathways to Recovery, Conf. March 2-6, 2004. Victoria, BC: Species at Risk 2004 Pathways to Recovery Conference Organizing Committee, Victoria, BC. Hawkes, BC, Vasbinder, W., Opio, C. & DeLong, C. (1997). Retrospective fire study: interim report. Fire in the SBS & ESSF biogeoclimatic zones of British Columbia - a literature review. In Interim report prepared for the McGregor Model Forest Association. Prince George, BC: McGregor Model Forest Association. Heard, D.C. & Vagt, K.L. (1998). Caribou in British Columbia: a 1996 status report. Special Issue 12. Helm, J. & Leacock, E. (1971). The hunting tribes of sub-arctic Canada. Indians in historical perspective. New York, NY: Random House. Rangifer, North American Hill-Tout, C. (1907). British North America: the far northwest, the home of the Salish and the Dene. Toronto, ON: Copp. Clark Company. Hins, C., Ouellet, J.P., Dussault, C. & St-Laurent, M.H. (2009). Habitat selection by forestdwelling caribou in managed boreal forest of eastern Canada: evidence of a landscape configuration effect. Forest Ecology and Management, 257, 636-643. Hudson, D. (1981). A cultural history of the band (Report prepared at Fraser Valley College). Retrieved June 20 2006, from the Tl'azt'en Treaty Office Library, Tache Native Reserve, BC. Hudson, D. (1983). The interior or plateau Indians of British Columbia: the Carrier. (Doctoral dissertation, Dept. of Anthropology and Sociology, Fraser University). Retrieved November 2006 from Geoffrey R. Weller Library, University of Northern British Columbia. Huntington, H.P. (1998). Observations on the utility of the semi-directive interview for documenting traditional ecological knowledge. Arctic, 3, 237-242. Huntington, H.P. (2000). Using traditional ecological knowledge in science: methods and applications. Ecological Applications, 10, 1270-1274. 118 Jablonsky, N.G. (2002). The first Americans. Berkeley, CA: University of California Press. James, A.R.C. & Stuart-Smith, A.K. (2000). Distribution of caribou and wolves in relation to linear corridors. Journal of Wildlife Management, 64, 154-159. James, A.R.C., Boutin, S., Hebert, D.M. & Rippin, A.B. (2004). Spatial separation of caribou from moose and its relation to predation by wolves. Journal of Wildlife Management 68, 99809. Jannuzzi, T.J. & Ludwig, D.F. (2005). An interdisciplinary investigation of ecological history and environmental restoration objectives in an urban landscape. Ecological Restoration, 3, 157-166. Jenness, D. (1934). Myths of the Carrier Indians of BC. Journal of American Folklore, 47, 99257. Johnson, C.J., Parker, K.L. & Heard, D.C. (2001). Foraging across a variable landscape: behavioural decisions made by woodland caribou at multiple spatial scale. Oecologia, 127, 590-602. Johnson, C.J., Boyce, M.S., Case, R.L., Cluff, H.D., Gau, R.J., Gunn, A. & Mulders, R. (2005). Cumulative effects of human developments on arctic wildlife. Wildlife Monographs, 160, 136. Johnson, C.J., Parker, K.L., Heard, D.C. & Gillingham, M.P. (2002). A multiscale behavioural approach to understanding the movements of woodland caribou. Ecological Applications, 12, 1840-1860. Johnson, C.J., Parker, K.L., Heard, D.C. & Seip, D.R. (2004). Movements, foraging habits, and habitat use strategies of northern woodland caribou during winter: implications for forest practices in British Columbia. BC Journal of Ecosystem and Management, 5, 22-35. Kay, C.E. (1994). The role of Native Americans in structuring western ecosystems. Nature, 5, 1045-6767. Human Kay, C.E. (1997). Aboriginal overkill and the biogeography of moose in western North America. Alces, 33, 141-164. Kay, C.E., Patton B. & White C.A (2000). Historical wildlife observation in the Canadian Rockies: Implications for ecological integrity. Canadian Field-Naturalist, 114, 561-583. Karns, P.D. (1998). The ecology and management of the North American moose. Washington DC: Smithsonian Institution Press. Klein, D.R. (1982). Fire, lichens and caribou. Journal of Range Management, 3, 300-395. 119 Klippenstein, F.E. (1992). The role of the Carrier Indians in the fur trade at Fort St. James, 1806- 1912. Ottawa, ON: Historical Services, Canadian Park Service, Western Regional Office. Kobrinsky, V.H. (1968). Ethno history and ceremonial representation of Carrier social structure. (Doctoral dissertation, University of British Columbia). Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Kobrisky, V.H. (1981). On thinking about eating animals. Dialectics of Carrier social identity symbols. Calgary, AB: University of Calgary. Krech, S. (1978). Disease, starvation, and northern Athapascan social organization. Ethnologist, 5, 710-732. Lamb, W.K. (1937). Ogden's notes on western Caledonia. Columbia Editions. American Victoria, BC: Archives of British Lamb, W.K. (1960). Letters and journals of Simon Fraser, 1806-08 [Microfilm], Toronto, ON: McMillan Company of Canada. Retrieved November 2006 from Geoffrey R. Weller Library, University of Northern British Columbia. Lamb, W.K. (1970). The journals and letters of Sir Alexander Mackenzie [Microfilm]. Toronto, ON: Published for the Hakluyt Society, University Press. Retrieved November 2006 from Geoffrey R. Weller Library, University of Northern British Columbia. Laliberte, A. S. R. & Ripple, W.J. (2003). Wildlife encounters by Lewis and Clark: a spatial analysis of interactions between Native Americans and wildlife. Bioscience, 53, 994-1003. Laliberte, A. S. R. & Ripple, W.J. (2004). Range contractions of North American carnivores and ungulates. Bioscience, 54, 132-138. Lawson, I., Church, M., McGovern, T., Simun, A., Woollet, J., Edwards, K., Gathorne-Hardy, F., Dugmore, A., Cook, G., Mairs, K.A., Thompson, A. & Sveinbjarnardotti, G. (2005). Historical ecology on Sandoy, Faroe Islands: paleo-environmental and archeological perspectives. Human Ecology, 5, 651 -684. LoGiudice, K. (2006). Towards a synthetic view of extinction: a history lesson from a North American Rodent. Bioscience, 56,687-793. Loranger, A.J., Bailey, T.N. & Larned, W.W. (1991). Effects of forest succession after fire in moose wintering habitats on the Kenai Peninsula, Alaska. Alces, 9, 100-109. Lunt, I.D. & Spooner, P.G. (2005). Using historical ecology to understand patterns of biodiversity in fragmented agricultural landscapes. Journal of Biogeography, 32, 1859-1873. 120 Liitolf, M., Kienast, F. & Guisan, A. (2006). The ghost of past species occurrence: improving species distribution models for presence-only data. Journal of Applied Ecology, 43, 802-815. Lyver, P.B. & Lutsel Ke Dene First Nation (2005). Monitoring barren ground caribou body condition with Desenoline traditional knowledge. Arctic, 58, 44-56. Marshall, C. & Rossman, G.B. (1989). Designing qualitative research. Thousand Oaks, CA: Sage Publications. Martin P.S. & Szuter C.R. (1999). War zones and game sinks in Lewis and Clark's west. Conservation Biology, 13, 36-45. Mackinson, S. (2001). Integrating local and scientific knowledge: an example in fisheries science. Environmental Management, 27, 533-545. Maier, J.A.K., Ver Hoef, J.M., McGuire, A.D., Bowyer, R.T., Saperstein, L. & Maier, H.A. (2005). Distribution and density of moose in relation to landscape characteristics: effects of scale. Canadian Journal of Forest Research, 35, 2233-2243. Marius, R. (1999). A short guide to writing about history. New York, NY: Longman. Marsden, S. & Galois, R.G. (1995). The Tsimshian, the Hudson's Bay Company, and the geopolitics of the northwest coast fur trade. The Canadian Geographer, 39, 169-183. Matson, R.G. & Magne, M.P.R. (2007). Athapascan migrations: the archaeology of Eagle Lake, British Columbia. Tucson, AZ: University of Arizona Press. May, J. (1977). Archaeological reconnaissance of Carp Lake Provincial Park, 1977. Interior Archaeology. Victoria, BC: Heritage Conservation Branch. Central McCabe, T.T. and McCabe, E.B. (1928). The Bowron Lake moose: their history and status. Murrelet, 11, 1-9. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. McDonald, G.A. (1996). Caribou and human agency in the Columbia mountains. Calgary, AB: Parks Canada, Historical Services. McKay, B. (1998). Local knowledge of caribou in the Valleau area. (Unpublished Report for Industrial Forest Service Ltd). Retrieved September 2006, Courtesy of Dr. Chris Johnson, University of Northern British Columbia. McMurdo, J. (1971). A report on archaeological investigations in the Takla Lake. Victoria, BC: Heritage Conservation Branch. Meidinger, D. & Pojar, J. (1991). Ecosystems of British Columbia. Special Report Series No. 6. Victoria, BC: Research Branch, BC Ministry of Forests. 121 Messier, F. & Joly, D.O. (2000). Comment: Regulation of moose populations by wolf predation. Canadian Journal of Zoology. 78, 506-510. Messier, F. &. Ferguson, M.A.D. (1997). Collection and analysis of traditional ecological knowledge about a population of arctic tundra caribou. Arctic 50, 17-28. Ministry of Environment (2004). Provincial database of blue listed species - woodland caribou, northern population (Report). Retrieved June 2008 from http://www.env.gov.bc.ca/atrisk/toolintro.html. Mitchell, S. (2006). Minding the gap: an exploration into the social landscapes of rock art at Stuart Lake/Nak'al'Bun, British Columbia. (MA Thesis, University of Northern British Columbia). Retrieved August 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Moodie, D.W. (1977). The Hudson's Bay Company's archives: geography. Canadian Geographer, 21, 268-74. a resource for historical Moller, H., Berkes, F., Lyver, P.O., & Kislalioglu, M. (2004). Combining science and traditional ecological knowledge: monitoring populations for co-management. Ecology and Society, 9, 44-59. Morice, A.G. (1892). Are the Carrier sociology and mythology indigenous or exotic? [Electronic resource]. Scanned from a CIHM microfiche of the original publication held by the National Library of Canada. Ottawa, ON: Canadian Institute for Historical Microreproductions, 1999. Printed Copy Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1897). In the land of the black bear. Translated by Dwight Dodge, 1997. Toronto, ON: William Briggs. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1905). The history of the northern interior of British Columbia: formerly New Caledonia: 1660 to 1880. Toronto, ON: William Briggs. Morice, A.G. (1906). The Great Dene Race. Anthropos I, 1, 2, 229-253, 254-278. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1906). Notes - archaeological, industrial, and sociological on the western Denes. In Native People Living in New Caledonia. (Booklet prepared by Julie Lane for the Fort St. James Historic Site, BC). Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1907). The great Dene race. Anthropos II, 6, 8, 1-34, 181-186. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. 122 Morice, A.G. (1909). The great Dene race. Anthropos IV, 9, 10, 582-594, 595-606. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1910) The great Dene race. Anthropos V, 11, 12, 13, 14, 113-131, 132-142, 419428. Retrieved June 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Morice, A.G. (1930). Fifty years in western Canada. Toronto, ON: Ryerson Press. Morris, P. A. & Fondahl., G. (2002). Negotiating the production of space in Tl'azt'en territory, Northern British Columbia. The Canadian Geographer, 46, 108-125. Morton, J. (1988). Fort St. James 1806-1914: a century of fur trade on Stuart Lake [Microfilm], Ottawa, ON: Environment Canada Parks Service. Printed Copy Retrieved June 2006, Courtesy of Canadian Park Service, Fort St. James, BC. Munro, J.B. (n.d.). Language, legends and lore of the Carrier Indians. (Doctoral dissertation, University of Ottawa). Retrieved July 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Nadasdy, P. (2003). Hunters and bureocrats: power, knowledge, and aboriginal-state relations in the southwestern Yukon. Vancouver, BC: UBC Press. Nak'azdli Elders Society (2001). Nak'azdli elders speak (Nak'azdli t'enneyuhulduk). BC: Theytus Books Ltd. Penticton, National Council on Ethics in Human Research [NCEHR] (2007). Canadian Research Ethic Board - University of Northern British Columbia. Retrieved August 2008 from http://ncehrcnerh. org/forms/searchKeyword.php. Natural Resource Canada (2007). Atlas of Canada - topographic maps. Retrieved October 2007 from: http://atlas.nrcan.gc.ca/site/english/maps/topo/map. Neuman, L.W. (2003). Social research methods: qualitative and quantitative approaches. York, NY: Pearson Education, Inc. New Nielsen, S.E., Johnson, C.J., Heard, D.C., & Boyce, M.S. (2004). Modelling species occurrence and abundance: does probability of occurrence reflect population density? Ecography, 28, 197-208. Oberg, P.R. (2001). Responses of mountain caribou to linear features in a west-central Alberta landscape. (Postgraduate thesis, University of Alberta). Retrieved November 2006 from Geoffrey R. Weller Library, University of Northern British Columbia. Paquet, M. (2000). Caribou in British Columbia. Victoria, BC: BC Ministry of Environment, Lands and Parks, Wildlife Branch. 123 Parlee, B. & Manseau, M. (2005). Using traditional knowledge to adapt to ecological change: Denesoleine monitoring of caribou movements. Arctic, 58, 26-37. Paterson, B. (2006). Ethics for wildlife conservation: overcoming the human-nature dualism. Bioscience, 2, 144-150. Patton, M.Q. (2002). Qualitative research and evaluation methods. Thousand Oaks, CA: Sage Publications. Pierotti R. & Wildcat D. (2000). Traditional ecological knowledge: the third alternative. Ecological Applications, 10, 1333-1340. Pointing, C. (1992). A green history of the world: the environment and the collapse of great civilizations. New York, NY: St. Martin Press. Poole, K.G.H. & Mowat, D.C. (2000). Habitat use by woodland caribou near Takla Lake in central British Columbia. Canadian Journal of Zoology 78, 1552. Racey, K. (1936). Notes on some mammals of the Chilcotin, British Columbia. Canadian Field Naturalist, 1, 15-21. Raleigh, V.Y. (1994). Recording oral history: a practical guide for social scientists. Oaks, CA: Sage Publications. Rettie, J., Rock, T. & Messier, F. (1996). Rangifer, 10, 105-109. Thousand Status of woodland caribou in Saskatchewan. Rettie, W.J., & Messier, F. (1998). Dynamics of woodland caribou populations at the southern limit of their range in Saskatchewan. Canadian Journal of Zoology, 76, 251-259. Richards, T.H. (1978). A pictograph survey of southeast Stuart Lake/nak'al Bun, British Columbia. In Annual Research Report of the British Columbia Heritage Conservation Branch. Victoria, BC: B. C. H. C. Branch. Ritcey, R. (1982). Conservation. Moose in British Columbia. Victoria, BC: Ministry of Recreation and Ritcey, R. (1991). Caribou statement for British Columbia, April 1991. Victoria, BC: Ministry of Environment, Land and Parks. Rival, L.M. (2002). Trekking through history. New York, NY: Columbia University Press. Rival, L. (2006). Amazonian historical ecologies. Institute, 12, 79-94. Journal of the Royal Anthropological 124 Saenz-Arroyo, A., Roberts, C.M., Torre, J. & Carino-Olvera, M. (2005). Using fishers' anecdotes, naturalists' observations and grey literature to reassess marine species at risk: the case of the Gulf grouper in the Gulf of California, Mexico. Fish and Fisheries, 2, 121-133. Saenz-Arroyo, A., Roberts, C.M., Torre, J., Carino-Olvera M. & Hawkins, J.P. (2006). The value of evidence about past abundance: marine fauna of the Gulf of California through the eyes of 16th to 19th century travelers. Fish and Fisheries, 2, 128-146. Schaefer, J.A., and Pruitt, W.O. (1991). Fire and woodland caribou in southeastern Manitoba. Wildlife Monographs, 116, 1-39. Schaefer, J.A., Veitch, A.M., Harrington, F.H., Brown, W.K., Theberge, J.B. & Luttich, S.N. (2001). Fuzzy structure and spatial dynamics of a declining woodland caribou population. Ecologies, 126, 507-514. Schaefer, J.A. (2003). Long-term range recession and the persistence of caribou in the taiga. Conservation Biology, 17, 1435-1439. Schensul, J.J., Le Compte, M.D., Nastasi, B.K. & Borgatti, S. (1999). Advanced ethnographic methods. Walnut Creek, CA: Altamira Press. Seip, D.R. (1991). Predation and caribou populations. Rangifer, 7,46-52. Seip, D.R. (1992). Factors limiting woodland caribou populations and their interrelationships with wolves and moose in southern British Columbia. Canadian Journal of Zoology. 70, 1494-1503. Seip, D. R. & Cichowski, D.B. (1996). Population ecology of caribou in British Columbia. Rangifer, Special Issue No. 9, 73-80. Sewell, J.H. (1950). Archaeological remains in central British Columbia. Anthropology in BC, 1, 28-32. Sherry, E. & Myers, H. (2002). Traditional environmental knowledge in practice. Society & Natural Resources, 15, 345-358. Sherry, E. (2003). Criteria of joint forest management: learning to be a good interviewer. In Researcher Training Program, NLUI, UNBC. Retrieved October 2005 from Geoffrey R. Weller Library, University of Northern British Columbia. Sherry, E., Halseth, R., Fondahl, G., Karjala, M. & Leon, B. (2005). Local level criteria and indicators: an aboriginal perspective on sustainable forest management, Forestry, 78, 513539. Somerset, H.S. (1895). The land of the Muskeg. London, ON: William Heinemann. 125 Spalding, D.J. (1990). The early history of moose (Alces alces): distribution and relative abundance in British Columbia. Victoria, BC: Royal British Columbia Museum. Spalding, D.J. (2000). The early history of woodland caribou {Rangifer tarandus caribou) in British Columbia. Wildlife Bulletin, B-100. Stevenson, S. & Hatler, D. (1985). Woodland caribou and their habitat in southern and central British Columbia (Report No. 23). Victoria, BC: Ministry of Forest and Land Management. Steward, J.H. (1955). Variation in ecological adaptations: the Carrier Indians. culture change. Urbana, IL: University of Illinois Press. In theory of Steward, J.H. (1977). Evolution and ecology: essays on social transformation. University of Illinois Press. Chicago, IL: Stewart, D.W. & Kamins, M.A. (1993). Basics of qualitative research: techniques and procedures for developing grounded theory. Thousand Oaks, CA: Sage Publications. Strauss, A.L. & Corbin, J. (1998). Basics of qualitative research: techniques and procedures for developing grounded theory. Thousand Oaks, CA: Sage Publications. Swetnam, T.W., Allen, C.D. & Betancourt, J.L. (1999). Applied historical ecology: using the past to manage for the future. Ecological Applications, 9, 1189-1206. Taylor, S.J. & Bogdan, R. (1998). Introduction to qualitative research methods, a guidebook and resource. New York, NY: John Wiley & Sons, Inc. Terry, E. L. & Wood, M. D. (1999). Seasonal movements and habitat selection by woodland caribou in the Wolverine Herd, north-central British Columbia, Phase 2: 1994-1997 (Report No. 204). Prince George, BC: Peace/Williston Fish and Wildlife Compensation Program. Tl'azt'en Nation (n.d.). Interview project: traditional use study, stories and legends of the Carrier. Transcripts retrieved July 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Tobey, M.L. (1981). Handbook of North American Indians Vol. 6. Washington, CL: Ed. June Helm. Smithsonian Institution. Retrieved July 2006 from Tl'azt'en Treaty Office library, Tache Native Reserve, BC. Thompkins, H., Gilbert, R., & Yukon Cultural Services (2007). Historical climatology of the southern Yukon: Paleo-climatic reconstruction using documentary sources from 1842-1852. In Occasional papers in Yukon history, no. 4, viii, 127 p. Whitehorse, YT: Yukon Cultural Services Branch, 2007. Trosper, R. L. (2003). Resilience in pre-contact Pacific Northwest social ecological systems. Conservation Ecology 7, 1-6. 126 Turner, N.J., Ignace, M.B. & Ignace, R. (2000). Traditional ecological knowledge and wisdom of aboriginal people in British Columbia. Ecological Applications, 10, 1275-1287. Turner-Turner, J. (1888). Three years hunting and trapping in America and the great north-west. London, UK: Maclure. Usher, P.J. (2000). Traditional ecological knowledge in environmental assessment and management. Arctic, 53, 183-193. Vanstone, J. (1974). Athapascan adaptations: hunters and fishermen of the sub arctic forests. Chicago, IL: Aldine Publishing Co. Viljugrein, H., LingjAjarde, O.C., Stenseth, N.C. & Boyce, M.S. (2001). Spatio-temporal patterns of mink and muskrat in Canada during a quarter century. Journal of Animal Ecology, 70, 671-682. Vistnes, I., and Nellemann, C. 2001. Avoidance of cabins, roads, and power lines by reindeer during calving. Journal of Wildlife Management, 65, 915-925. Vors, L.S., Schaefer, J.A., Pond, B.A., Rodgers, A.R. & Patterson, B.R. (2007). Woodland Caribou Extirpation and Anthropogenic Landscape Disturbance in Ontario. Journal of Wildlife Management, 1, 1249-1256. Watson, D.S. (1933). Ogden's diary: traits of American Indian life and character by a fur trader. San Francisco, CA: Grabhorn Press. Weber, W., White, L.J.T., Vedder, A. & Naughton-Treves, L. (2001). African rain forest ecology and conservation: an interdisciplinary perspective. New York, NY: Yale University Press. Weclaw, P. & Hudson, J.R. (2004). Simulation of conservation and management of woodland caribou. Ecological Modeling, 177, 75-94. Weladji, R.B., Holand, O., and Almoy, T. (2003). Use of climatic data to assess the effect of insect harassment on the autumn weight of reindeer (Rangifer tarandus) calves. Journal of Zoology, 260, 79-85. Weladji, R.B., Klein, D.R., Holand, O. & Mysterud, A. (2002). Comparative response of Rangifer tarandus and other northern ungulates to climatic variability. Rangifer, 22, 29-46. Wenzel, G.W. (1999). Traditional ecological knowledge and Inuit: reflections on TEK research and ethics. Arctic, 52, 113-124. Willems-Braun, B. (1997). Buried epistemologies: the politics of nature in post-colonial British Columbia. Annals of the Association of American Geographers, 87, 3-31. 127 Wilmeth, R. (1975). Proto-historic and historic Athapascan occupation of British Columbia: the archaeological evidence. The Western Canadian Journal of Anthropology 5, 4-20. Wilson, C. & Harrington, C. R. (1992). Climate in Canada, 1809-20: three approaches to the Hudson's Bay Company archives as an historical database. Retrieved November 2008, from Arctic & Antarctic Regions Electronic Database, University of Northern British Columbia. Wimberly, M.C. (2002). Spatial simulation of historical landscape patterns in coastal forests of the Pacific Northwest. Canadian Journal of Forestry Research, 32, 1316-1328. Winterhalder, B.P. (1994). Historical ecology: Cultural Knowledge of Changing Landscapes. New York, NY: School of American Research, Advanced Seminar Series Press. Wittmer, H.U., Sinclair, A.R.E. & McLellan B.N. (2005). The role of predation in the decline and extirpation of woodland caribou. Oecologia, 2, 257-267. Wong, C., Sandmann, H. & Dorner, B. (2003). Historical variability of natural disturbances in British Columbia: A literature review. Kamloops, BC: FORREX-Forest Research Extension Partnership. Wood, M.D., & Terry, E.L. (1999). Seasonal movement and habitat selection by woodland caribou in the Omineca Mountains, north-central British Columbia. Phase 1: The Chase and Wolverine herds (1991-1994) (Program Report 201). Prince George, BC: Peace/Williston Fish and Wildlife Compensation Program. Wright, J.V. (1995). A history of Native People of Canada, Vol. 1-2. Archaeological Survey of Canada. Ottawa, ON: Wright, J.V. (1999). A history of Native People of Canada, Vol. 3. Ottawa, ON: Archaeological Survey of Canada. Yesner, D.R. (1989). Moose hunters of the boreal forest? A re-examination of subsistence patterns in the western sub arctic. Arctic, 42, 97-108. 128 APPENDIXES APPENDIX IV: Result Tables,OtherWrittenSources. TUt CODE Caribou Observations STATEMENT GEOGRAPHIC LOCATION DATE SOURCE g j "Enough [caribou] to live on it for people" all around from Stoney Creek well down to Blackwater around Prince George area." Study area. 1800s #2 Tl'azt'en B5 "Caribou up there before [...] they shot it all [...] That mountain [...] Sidney Williams. Yeah, but right there [pointing on map] [Tsitsutl Mountain]." Mt. Sidney Williams & Mt. Tsitsutl. 1890 #2 Tl'azt'en CI "Caribou, there used to be caribou in Sidney Williams but in future days they moved out of there, there's no caribou over there. And just on the next big mountain there used to be caribou but they moved out too, they moved farther north. Around Bear Lake and there." Mt. Sidney Williams & Mt. Tsitsutl. < 1940 #3 Tl'azt'en C3 "Years ago there used to be caribou in that mountain over there, Grizzly Mountain. They moved out too." Mt. Shass. < 1950 #3 Tl'azt'en D1 "They were killing too many. But there were caribou before? Yeah, very much. Yeah, lots of caribou, but there was no moose." Trap line around Whitefish Lake. 1800s1900s #4 Tl'azt'en D4 "Yes [caribou] around Whitefish Lake, that's where our trap line is, you know." Trap line around Whitefish Lake. <1940 #4 Tl'azt'en El "As far caribou was concerned within the territory that I was in, and been in many times since, the wolverine range was the closest I have ever knew of caribou, except for one instance. We had a fishing camp on Tezzeron Lake and I didn't see them, but one fisherman came in one day and he said, "I saw a bunch of caribou crossing the lake." [...] There is a long sandy bar across the Lake is the shortest distance to cross the lake and yeah, he said they [there?] were 7 caribou [...] because you know that's highly unusual, because where do they come from? Well, the only place they could have come from at that particular time would have been maybe from the Wolverine range." Tezzeron Lake, sandbar. 1980 #5 Nonaboriginal 129 E2 "North West of Germansen Landing, it's in the same area of the Kemess mine right now. If you are familiar with Two Daddy Lake that's the Brother's Lake area. And there were about, oh, I don't know how big the herd would be but some of the outfitters in that area have said that at one point in time all the different bands of caribou probably numbered 3 to 5 thousand caribou." Germansen Landing, Brothers Lake. 1950s #5 Nonaboriginal E3 "A fellow of the name of Archie Prince, he had a trap line on what he called Caribou Lake which is now called Manson Tube Lake, there is a little park there right now, and I had hunting and fishing cabin up there for many years. And he said that back when he was a young fellow he was on the trap line they called it Caribou Lake because somebody had seen some caribou there, whether he'd seen it or not I don't know, but somebody has seen caribou on there." Manson Lake. < 1950 #5 Nonaboriginal F1 "Oh, well, like I said up way in the mountains [...] We finally got some team of horses with that we travel way up to the mountains and my dad used to get, he hunted caribou up on the mountains, there were some like at the bottom down the valley. He knows where they are to hunt them. I must have been 5-6 years old at that time. Up the Nation to our trap line, that's where all they used to be." Nation lakes. Early 1900 #6 Nak'azdli G1 "There used to be caribou here? Well, with the old-timers I talked with. How many I don't know. Well, the older people they used to talk of it, like one mountain over that way, there used to be caribou there. That's what they say. How long ago I don't know. As you said, there used to be. [...] I know that, Shass mountain. And the mountains over that way [pointing north]. Sidney Williams too." Mt. &Shass Mt. Sidney Williams. Early 1900s #7 Nak'azdli G3 "Up north, Spatzisi Park and around the Nations [...] Oh yeah there's lots of caribou up there. I used to see sixty at the time." Spatzisi Park and Nation lakes. 1950s #7 Nak'azdli G8 "But before moose arrived caribou were not just in alpine country. They were everywhere." [Trap line of interviewee in 'Salmon Lake country']. Stuart Lake area, Salmon Lake. 1800s #7 Nak'azdli 130 G1 "Always there around the winter. They roam around Nation River. We see some swimming across. [Q: Is Caribou Flats near Nation River?] No, just about halfway from here to Nation, 30-35 miles. [Q: Why is it called Caribou Flats?] It's a flat meadow; old-timers always saw the caribou there, that's why they called it that. Even in the summer, they saw caribou there. I have never seen one in the summer but the old timers did." Caribou Flats: 30-35 miles north of Ft. St. James on North Road, Nation River. 7 <1950 #7 Nak'azdli HI-3 "Not really around here; the close I would hear of the caribou is up in the mountains. I don't think they had hardly any caribou around here in this area. I don't know I never heard about that. Just in the mountains when they go out hunting. In the summer they'd go caribou hunting and my mum was telling us that they go in the mountain during the summer and my dad used to kill lots of caribou, about 50 to ten and they skinned it all... Yeah, they said it was deer or caribou, that's all they had before that and fish." Nation Lakes, Southern Omineca. 1890 1940 #8 Nak'azdli 11-3 "Everywhere in [DAKELH NAME], there used to be, crossing to Whitefish Lake. There used to be our trap line right there, that big mountain, they call it Grizzly Mountain, there used to be caribou, that's what my father said. And now no caribou at all, just deer. Oh yeah, long ago that's what they lived on, before, before, when my father, in the 18th hundreds, they said they used to be caribou up there. There used to be deer too, all right. And no moose at all, the first moose that they saw, they saw it in that place. Caribou were not there when I was growing up." Whitefish Lake. 1800s & 1900s #9 Tl'azt'en L2 "Well, I don't know about caribou, they always told stories about it. I don't know how it was long time ago because I couldn't see and my dad said there were lots of caribou." "1932 saw first caribou. There used to be lots then. My grandfather's fathers that's what they hunted and they were all over." [Translation by Veronica Campbell], Trap line around Middle River. Early 1900s # 10 Tl'azt'en Trap line around Middle River, 1932 # 11 Tl'azt'en L2 7 Caribou Flats may have been located in the 48-56 Km (30-35 miles) transect between the intersection of North Road with Willowy River (54° 48' 48" N 124° 10' 16" W) and Cripple Lake rec. site (54° 54' 44" N 124° 12' 1" W). Currently named Butchers Flats (54° 52' 23" N 124° 14' 52" W - UTM: 10U 419916 6081396). [any idea why?] 131 THEME Moose distribution CODE STATEMENT GEOGRAPHIC LOCATION DATE SOURCE Al "One day the hunters saw new tracks. They followed it for two days, catch it, and then invited all the people. After that [time], they started to see moose a little, and after some time moose came. [...] I don't even know. Me, I wasn't even born yet when this things." Stuart Lake area. Late 1800s to early 1900s #1 Tl'azt 'en B4/ B8 "No moose prior to 1896. They found out it came from Alaska [...] then moose was extinct until the 20s, 30s, then there was lots of moose." Study area. 1896 #2 Tl'azt 'en C6 "No, in the early days before my time my grandfather used to talk about moose, there was no moose in this area. The whole area around here - no moose, they used to go all the way up north like around Bear Lake and all that area to hunt moose, then stayed up there for all the season and moose was around. But here around this area there was no moose. And my dad and somebody, I forgot the name, before my time, use to talk about it. The guy's name I forgot, his dad long time ago went up in Trembleur (Lake) and shot the first moose. First moose in this area, and then they started coming this way, because the snow in that area, in area up north is always too deep, ten-twelve feet deep, they started moving down this way. That's why the moose came around here, all kinds of moose, hanging around for quite a while." Trembleur Lake. Early 1900s #3 Tl'azt 'en CIO "... It was quite before my time, way before my time. I don't know when, my grandfather's dead, in his younger days I guess. I couldn't recall when it came, but I know it did come. I say this guy here saw his first moose up in Trembleur. First moose." "Yeah, lots of caribou, but there was no moose. My uncle he walked for four days before he caught that one moose. Four days [...] but they weren't many at the time, that's when they started... 1898." Trembleur Lake. Late 1800s or early 1900s #3 Tl'azt 'en Stuart Lake area. 1898 Stuart Lake area. 1800s D1 E4 "I do remember talking to long timer Indians when I first came here, you know, men that were already in their seventies at that time and started (hunting and trapping) #4 Tl'azt 'en #5 Nonabori ginal 132 F2 when they were kids. They remembered eating beaver, and that a moose was a new delicacy when they finally moved into the area. So you know, there was a time when the moose migrated here, I guess from Alaska." "I think later in the years they started coming because I remember [...] I was a child and my mother was looking for a baby-sitter for us, someone that had to look after us because they heard somebody had killed a moose, thirty miles from here, Fort St. James, and a bunch a them were going to get it, and my mum was going with them. Everybody was surprised somebody caught a moose. That's why; they didn't even know what it looked like at the time." 30 miles from Ft. St. James. 8 < 1940 #6 Nak'a zdli G9 "1911-12. My uncle talked about it. They never seen, first time they heard of it was from Fort George. They were very rare at that time. I remember my uncle telling me they followed one, it crossed the Nation River, they followed it for 7 days and then they killed it." Nation River. 19111912 #7 Nak'a zdli 12 "And there used to be no moose until my father was working for the Hudson Bay. They went to Prince George and Portage from Fort St. James, using the river. That's where they've seen that moose for the first time, they said it came out of the blue just to stare at. That moose was so awesome for them; they couldn't believe it was so large. That's the first time in the 19th hundreds. That's when, yeah, the 19th hundreds, that's when they first saw moose. Before, they used to go from Fort St. James to Cree country, and bought with them Indian food like dried black bear sand stuff like that. They brought it down there, and traded it for moose hide. They never did see a moose but they did buy moose hide from them. But that's the first time they ever saw a moose, then they started to come in, that's when they started seen and kill moose. No matter how far you'd go to kill a moose." Route from Prince George to Ft. St. James. 1900s #9 Tl'azt 'en LI "Tache, around Tache, he said that he remembers the time when he first saw moose tracks. First time in all their life, [...] after 1918." Tache. After 1918 #11 Tl'azt 'en 8 On the map related to moose, I located this point to the northwest of Fort St. James as Nak'azdli often hunted north of Fort St. James. However, the point could be located anywhere within a radius of 30 miles from the Fort. 133 APPENDIX II: Collateral Information on the Historical Landscapes of the Study Area Gathered from Interviews. SUBTHEMES Traditional uses of caribou CODE B7 DESCRIPTION SOURCE "We used caribou for foodstuff, blankets, and bones as scrapers, sinew, and stomach as container for animal fat." #2, Tl'azt'en #7 Nak'azdli G2 "For raw hide, snowshoes, that's what they used it for (caribou hide), and clothing. Yeah, cloth is warm and the fur is hollow." Starvation F3 "Well there used to be black bear and things like that I guess, some ducks, things that we live on. Fish in Dough Lake, all kinds. When we were little we had plenty, even in the hunger years in the 30s people were suffering but we never run out of food, we had a variety of bear, goat, caribou meat, everything, not too much of this food wrap. Everything we used to go we used to take some people up with us those days." #6 Nak'azdli Caribou hides preparation F4 "They fixed up everything from the caribou hide to the dried meat, even the bones they smoked for the future, and they saved it and cut it up. And then the hide too, she used it. She'd get a pole [...] She put the caribou hide over this pole and my mother took all the flesh out [...] they are very tough animals, very good. That time he caught them, I was about 5-6 years old, I remember one time he killed about 10 of them." "Well, dad used to, we've done a lot of that in the bush. Caribou. The horns we used to use them to make a cross cut saw, an old cross cut saw [...] we also made nice knifes with it. We used the caribou horns for the handling, all kinds of handles." "Just smoke himself, he couldn't even see his hand, nothing. He took out his boots and put it out in the smoke too, everything he had he made sure he smoked. He didn't get it (disease). He didn't get it. It works that, smoking." ".. .My dad used to kill lots of caribou, about 50 to ten and they skinned it all and my mother dried all the meat and she worked on the skins. She used to make all the skins. They had a certain way of working on the hides you know, like they used some kind of tool, not like the tools we use now, they had a bone structure made like this and there was a sharp edge on one side or maybe both sides, I don't know; and they used to make a pole. Smoothen out a pole and then put a skin over it and scrape it." #6 Nak'azdli F6 Ceremony to prevent illness during epidemics F8 H2 #6 Nak'azdli #6 Nak'azdli #8 Nak'azdli 134 - Continue - Migrations A2 "Crossing point for caribou in Middle River ..." #1 Tl'azt'en #2 Tl'azt'en B2 "In the winter they would cross and go up to the other mountains, Mitchell and Takla Range on that side, they crossed back and forth." B8 "At Rainbow Lodge, in the narrows. From there they would go up Mission Ridge and Johansson. Few caribou started to cross back in 1950s, two or three only, but they would never remain permanently as before." #2 Tl'azt'en Famine B6 Widespread famines in the region lead hunters to harvest the entire herd of southern Takla, "60-70 of it." After the episode, only few caribou remained. #2 Tl'azt'en Predation BIO "[Wolves] probably hunt on caribou. I think that's what mostly kills the caribou, but when they came back in the 40s the wolves were ramping, they were all over the place. There was lots of moose but even the moose population went down in the early 40s." #2 Tl'azt'en Mining C8 "Yeah there were blasts for mines; they were looking for gold up in Sidney Williams. I don't know when, it was not in my time; my grandfather was talking about it. That's why he said there were lots of caribou before there, but when they went there to hunt again caribou, they found none. They found the site where they have been blasting. I don't know how they got up there but they were blasting around that area so all the caribou moved out of there. They don't go there anymore, they went in Tsitsutl the next mountain to look for caribou and there's nothing there either. So, up, around Bear Lake that area, Johansson, lots of caribou there..." #3 Tl'azt'en D2 "Yeah, they were all over it. There were lots of caribou. Then all the sudden they started dying out." #4 Tl'azt'en Contact with moose G4 "I think is when he moose arrived. I know that when the moose arrived the elk went also. You know. There used to be elk around here. In Stoney Creek there used to be lots. After 191012 never saw them anymore. I don't remember those days but that's what old-timers told me." #5 Nak'azdli Overharvesting by native hunters G5 G7 "I know in one place where we hunt there is a bunch of people that kill too many caribou, and we noticed a decline. You go next year and there is nothing there. We only hunt just enough for ourselves, you know my niece, nephews and uncles. But there are too many hunters out there." #5 Nak'azdli 135 APPENDIX IV: Result Tables,OtherWrittenSources. DESCRIPTION GEOGRAPHIC LOCATION SOURCE Carrier Lake. HBCA B.188/a/l, December 12, 1820, Mountains. HBCA B.188/a/2, October 30, 1823 ".. Kase the Chief of Pinchi made us a Visit, for the purpose of delivering... 25 skins, and the best part of the meat of a Rein Deer... this Indian... killed seven deer within these four days, circumstance of rare occurrence in this quarter." Study area. HBCA B.188/a/13, January 11, 1829 "An Indian [...] has killed two Moose Deers." Study area. HBCA B.188/a/17, March 16, 1832 "Dechanyai killed a reindeer." Study area. HBCA B.188/a/17, March 29, 1832 "Indians shot 3 carriboux beyond Carrier Lake." Carrier Lake. HBCA B.188/a/19 February 12, 1842 "All the Indians have now left here for their several hunting grounds - caribou are reported to be numerous in the mountains opposite Tache." Shass Mountain. HBCA B.188/a/20, fo. 129, March 6, 1851 "Indians gave in a few bustards they also killed a carribeaux at the village along the Lake." Pinchi. HBCA B.188/a/20, October 16, 1852 "Prince and Brother also arrived from an excursion. They I believe have made a good hunt of carriboux and a few furs." Study area. HBCA B188/a/20 March 17,1852 "[Indians?] Came back from hunting. Many deer are now being killed by the [Indians?] side of Necoslie." Fort St. James HBCA B188/a/22 March 5, 1895 "The Marie des dent Biches Boy arrived & brought one Large Beaver & one small whole [sic], he is at present in the vicinity of Carriers Lake but complains of a scarcity of beaver - has killed no Rein Deer as yet." "Calunda and his nephew arrived from his hunting ground, having previously been to hunt Cariboux [sic] in the mountains, where they also have a number of Siffleux and hunt the mountain goat..." 136 APPENDIX IV: Result Tables, Other Written Sources. SUBTHEMES Caribou Observations DESCRIPTION GEOGRAPHIC LOCATION DATE SOURCE "As for the fauna, its representatives are fairly numerous. The natives class them into venison and fur animals. Among the former are the moose and the caribou, whose habitat is mostly on the mountains of the north..." New Caledonia. 18591910 Morice (1897) "We have no buffalo or deer, except the caribou [...] and not many even of those." New Caledonia. "Sicannies" [Sekani] .. .they remain on this side of the mountain where they find buffaloes, moose and deer. On the other side, none of these animals, except a few struggling ones are to be found." Rocky Mountain portage. 25 April 1815 1810 J. Stuart, (Morice 1897; 95) Harmon (1904; 156) "On the 4th inst. Accompanied by several of our people I set off for Tachy, a village, toward the other end of this Lake... From that place we proceeded up a considerable River [Tachie River?], about half a day's march, to another village, inhabited chiefly by Sicannies... their principal food consists of salmon, white fish, and trout; and they, at times, kill a beaver, or a caribou. The country around the Lake is hilly..." Takla Lake. 7 Nov. 1811 Harmon (1904; 179) "We saw no large animals, excepting the caribou; but we were informed, that black bears, and other kind of the larger animals, exist in considerable numbers, in that region." Fraser Lake. 30 Nov. 1811 Harmon (1904; 183) "Long ago, my parents hunted for the caribou. They had to go to the mountains to do this. Mother says she was just a newlywed and didn't know the traditional ways of hunting [...] She said, 'Benoit went hunting one day, and noticed fresh tracks, he told us to be quiet and to keep the dogs quiet. When he walked up a ridge, he saw a large number of caribou feeding. He shot eleven caribou, and brought the meat back to the camp." Nak'azdli traditional territory. 1800s1900s Nak'azdli elders society (2001; 31) "From there we went through Caribou Flats towards the shoemaker area." Caribou Flats. As above Nak'azdli elders society (2001; 36) 137 Betsy Leon tells about her fathers hunt in the month of august. "Then my father Benoit Prince, Jean Marie Prince and Charlie Murdoch would go on Duneza, this side of Wolverine. One can get lots of groundhogs and caribou on that mountain." William Julian (1917) recounts abundance of wildlife from his grandfather Thomas Julian. "In the earlier years, caribou, deer and bears were plentiful in this area. As I have been told, the caribou gathered in a herd of hundred or more. They fed in the lowlands. They were everywhere, and people killed these animals with bow and arrows. The Indians killed only what they needed. The meat of the caribou was dried. From the tanned hides, the women made coats, pants, mitts and moccasins. The bones were made into knives and hide scrapers." Duneza Mountain, north of Chuchi Lake (Swannell ranges). 18771960 Nak'azdli elders society (2001; 37) Carp Lake lowlands. 1800s1900s Nak'azdli elders society (2001;54) Use of caribou antlers "The Carrier easily found out (Beaver under ice) by sounding the ice in different directions with caribou horns..." Study area. 1800s1900s Morice (1906; 66) Caribou "There are no large animals except Carruban which is too sly for us..." Study area. 18001830 Lamb (1960) "We have mentioned venison. By this we mean the flesh not only of caribou and moose, which could be procured only at a distance from beaten tracks, on or near the mountains, whereon the hunters roamed for weeks at a time ..." Study area. 18901900 Morice (1910) "The caribou danced and the musk-rat sang O! Skette. The cariboo swung his head to right and left as he danced, hoping to catch some of the fire with his head dress..." [In "The creation of Fire"]. Study area. Carrier legend Somerset (1895) In 'Clothing': 1) "Clothing and moccasins were made from the hides of caribou and the beaver, for clothing the latter being the warmer." 2) "Sinews of the caribou, and elk, were used as thread for piercing together clothing, moccasins, and blankets." Stuart Lake area. "Early days" Hall (1992; 10) In 'Livelihood': 1) "Bears were snared with twisted, four-strand babiche (rope) of caribou hide. 2) "In the spring, the Carriers scraped the cambium, or sap off the jack pine, (Knotty pine), using a piece of concave bone from a caribou. Later, pieces of metals or knives were used." Stuart Lake area. "Early days" Hall (1992; 15) 138 In 'the Imposition of the Swan's Down.' "As I mentioned earlier there were no moose, but there were plenty of caribou, elk and some deer. The smoked hides of these animals were used at potlatches." Stuart Lake area. "Early days" Hall (1992; 18) In 'Some of My Father's Experiences'. "The next morning he had gone north of the mountain and killed 20 caribou." Nation River from McLeod. Late 1800s or early 1900s Hall (1992; 118) GEOGRAPHIC LOCATION DATE SOURCE New Caledonia. 1880s Morice (1930) "Sicannies" [Sekani] .. .they remain on this side of the mountain where they find buffaloes, moose and deer. On the other side, none of these animals, except a few struggling ones are to be found." "There are few moose; and the Natives, occasionally, kill a black bear. Cariboo are also found, at some seasons." "The Sekani picked a leaning tree, and climbed the tree, where they carried the babiche (rope) and dried shoulder blades of the moose. They would begin to rub the shoulder blades against the tree and make loud noises. This is what attracted the bull moose." North West end of Rocky Mountain portage. 1810 Harmon (1904) McLeod Lake. 1800/ 1900 Harmon (1904) Sekani territory. Late 1800s early 1900s Nak'azdli elders society (2001) "At this time the Lht'at'en people (Sekani) told the people here that it was heard from the Beaver Indians , that large animals with horns were all coming soon. Now at this time the caribou moved from the lowlands to the mountain country. The people had to hunt upon the mountains for the caribou. It was a long way to go to the mountains, as the caribou were getting scarce. So my dad told me this. He was just a young man then, when he first saw the tracks of what looked like two animals. One was big, the other was small. On the ground, there were three or four inches of fresh snow and he was able to track the animals. The animals kept traveled on, eating ends of willows. My father got close to Benoit Ah'uille's trapline and turned around, leaving Great Beaver Lake. Late 1800s or early 1900s Nak'azdli elders society (2001) - Continue - THEME Moose distribution DESCRIPTION "We have mentioned venison. By this we mean the flesh not only of caribou and moose, which could be procured only at a distance from beaten tracks, on or near the mountains, whereon the hunters roamed for weeks at a time 139 the tracks. It was late at night when he got back to the cabin at Eagle lake [...] So the story goes on that Benoit Ah'uille followed the tracks as far as Beaver Lake and he too, turned around leaving the tracks. The next one to follow the animals was Leon (Cho) Prince. His trapline was on Stuart River. He followed the animals for a long distance and gave up and turned around. Then it was told that around Christmas time, the Stoney Creek people told their stories about the tracks. They said it must be what the Lht 'at 'en people meant, when they said that large animals with horns would be coming in the future. They called it Huda in their language. We call it Duni, but the white people called it moose. In a year or two, they became frequent in numbers. My father told to me this story." Moose seldom seen around Stuart Lake. Stuart Lake area 18661888 "Moose... killed within 18 miles of Fort St. James." Moose killed near the junction of Stuart and Nechako rivers. 1876 Stuart/ Nechako Junction. 1860s (In Spalding, 1990) TurnerTurner (1888 ) Anderson (1872) 140 APPENDIX V: Interview Guide Interview guide: • • • • • • • • • • • • Caribou and habitats Moose and habitats Locations of caribou in space and on a temporal scale Locations of moose in space and on a temporal scale Relationship between moose and caribou Shift between caribou and moose Relationship between wolves, caribou and moose Natural disturbance Long term climate change and weather events Hunting strategies and harvest of caribou Landscape change in the study area during the time frame of the research Socio, economic and cultural changes in the area during the time frame of the research 141 Page 2/2 Research The historical decline of woodland caribou in the Fort Saint James area INFORMED CONSENT FORM FOR INTERVIEWEES - Side 2 • I am aware that our interview will be taped. In case I do not want our interviews to be taped, I am aware that the interview will not take place. • I agree the tapes to be deposited in Tl'azt'en Natural Resources library and to be accessed by other researchers. • I do NOT agree to allow the tapes available to other researchers and ask that they be destroyed after use (the tapes will be kept for 3 years in a locked file in Dr. Gail Fondahl's office, and then destroyed). • I would like my input to be acknowledged in all products of the research and attributed directly to me. • I wish to preserve my anonymity, and prefer to be identified as unnamed member of my community (or indicate other identity here: \ • I wish to receive a copy of summary findings resulting from this research (please provide address below) Address: 143