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Thoughts on Approaches to Designing and Conducting
Ecological Knowledge Social Research

Anthony Davis

Professor
Department of Sociology and Anthropology

St. Francis Xavier University
Antigonish, Nova Scotia

In my view, a key concern is development of designs and methodologies that allow for the documentation and analyses of experience and/or cognitive map differences and variations within as well as between the various collectives and communities of interest claiming ecological knowledge. The importance of this is underscored by the actual and potential consequences of designating any particular cognitive map, socio-political process or extractive interaction within an ecosystem as an the embodiment of 'knowledge'. This concern expresses the anticipated relation, within and between the communities of interest, of 'power' with 'knowledge'. That is, the act of designating particular understandings as 'knowledge' will likely empower or further empower those within social and institutional settings understood to be the bearers of knowledge. Empowerment may translate, in fact, as little more than further entrenchment of existing social, economic and political cleavages within and between communities of interest. Such a development, to say the least, contributes little to the possibility of social research contributing to the reconciliation of competing and conflicting ecological knowledge claims.

There are several considerations that I think must be built into designs and methodologies that are intended to contribute meaningfully to social research documentation and understandings of ecological knowledge claims. An important consideration to this process is the manner in which these claims may inform both harvesting behaviour as well as formation of fisheries management policies. Expressed as a series of questions, these considerations translate as,

  • What do we mean by 'ecological knowledge', both in terms of its 'knowledge' and its 'ecological' content?
  • Who are the bearers of 'ecological knowledge' within each community of interest?
  • What are the best means to identify the bearers of this knowledge?
  • What are the best suited means to document and to describe this knowledge?
  • What are the possible and practical/sensible relationships of such knowledge to fisheries management and harvester/community socio-economic and ecological sustainability?
  • What are the ways and means whereby the results of social research focused on ecological knowledge can be most effectively disseminated with regard to their potential, and hopefully, positive meanings for the human condition within fisheries and as embedded in fisheries management policies?

The working seminar will likely chew through these and many other linked questions and issues. From the outset, it is critical that substantial, defensible and examinable answers be provided to the issues associated with these what, who and how questions. Additionally, it seems inescapable that the specific research tools and methods needed to document the various 'communities' of ecological knowledge will differ with respect to the 'knowledge claims' under study. For instance, the sampling procedures, key informant identifier processes and the sorts of questions asked will vary depending on whether one is working with fisheries scientists/marine ecologists-biologists, commercial marine harvesters, First Nations or recreational fishers.

For this thought exercise I have chosen to focus on American Eel fisheries and systems of ecological knowledge. This fishery is associated with at least three contending systems of 'ecological knowledge': the knowledge claimed by fisheries scientists/marine biologists and ecologists, the knowledge accumulated by non-native commercial and recreational harvesters, and Mi'kmaq knowledge of American Eel behaviour and habitat. Additionally, there seems to have been little, if any, social research in North America focussed on eel fisheries and knowledge systems. Finally, the eel fisheries seem to have experienced little by way of systematic interest or attention from fisheries managers; yet, are understood as particularly important to the Mi'kmaq and characterised by Mi'kmaq participation. Is the marginality of American Eel in fisheries science/management related in any way to the marginality, in economic and political terms, of the Mi'kmaq?

By way of a specific comment on design and methodology, I have participated in both qualitative and quantitative research processes. In working with non-native marine harvesters, I have come to prefer a two-tier methodological approach. This approach begins with the quantitative designs and devices associated with stratified random sampling as the means to identify and initially describe the pertinent 'categories of people' as well as key attributes of human action/organisation/background. A rank order of peer-specified local knowledge experts would be created from the quantitative work.

The quantitative phase might also be employed to detail core aspects of social background, family/kin/organisational 'rootedness' in fishing such as duration of participation, interruptions, attachments to and satisfaction with fishing as well as the extent to which participation is 'nested' within/in relation to kin and family participation in fishing. For example, in quantitative research it is possible to document whether a respondent began fishing with kin/family, whether their father/grandfathers fish/fished, and whether they are currently fishing with kin/family (sons, brothers, fathers, grandfathers, or other relatives). It is also important to document qualities of current fishing practices and 'fishing power'. That is, it is important to detail the fisheries engaged (e.g., lobster, groundfish, pelagics, crab etc.), fishing licenses currently held, fishing gear used (traps, nets, trawl, hook and line), as well as technical characteristics of the current fishing boat (age of vessel, length of vessel, engine power, electronic aids, and such).

Once completed, the quantitative phase is followed by qualitative research during which one focuses effort on working with the persons identified by peers during the first phase as the recognised local ecological knowledge experts. The qualitative work is focused on generating the 'thick descriptions' elemental to documenting human action and understandings. The second phase of this research design is domain-centred. The researcher would begin by working with the most commonly peer-acknowledged local expert. This work would employ various devices such as family/kin and occupational history descriptions (a genealogical approach), nautical charts, observations during fishing trips (not essential, but useful), and other devices to document experiences, identify and 'name' locations, and to detail knowledge of fishing grounds and species (lobster/American Eel) behaviour as well as ecological associations and interactions. The rank-order list of acknowledged local ecological knowledge experts would be worked through until it becomes clear that 'information saturation' has been achieved for the locality and species concerned.

In principle, this approach engages a defensible and legitimating design/methodology with respect to the 'meaning' of data/information gathered respecting non-native marine harvester ecological knowledge. Of course, one of the major limitations of this approach is that it is both time and material resources hungry, requiring intensive engagement over a lengthy period of time. Yet, I cannot conceive of any other approach that would permit social researchers to demonstrate a sufficient and defensible systematic methodological foundation for what is claimed as documentation/description, let alone as findings, conclusions and understandings.

I have a particular interest in using and developing mapping as an aspect of research design and methods, particularly as applicable to human extractive interactions within natural resource settings. I have employed primitive mapping in some previous research, mainly interviewing marine harvesters about fishing practices and strategies with the aid of nautical maps. I found these maps to be invaluable as the harvesters could easily relate their practices, memories, and understandings to the spatial and 'physical features' dimensions represented in the map, e.g., water depth, ocean floor topography, and 'fishing spots'. Recollections, 'stories' and specific observations for various fisheries, locations and times of year were often cued through reference to and discussion of fishing 'places' and 'ground'. Nautical maps also proved useful in aiding reconstructions of fishing histories and experiences, including stories respecting the experiences of others in specific reference to particular places, often named, located on the fishing ground. The use of multiple copies of a locality's nautical/coastal maps would likely be necessary to record/document relative time-referenced and framed information, i.e., Map copy 1 for early experiences, Map Copy 2 for when first taking a boat as captain, Map Copy 3 for mid-career experiences, Map Copy 4 for current or recent experiences, observations.

Finally, I have learned that recollections are most readily detailed and associated with the particular boat fished on at the time. Consequently, it is useful to reconstruct fishing histories and relative chronologies through reference to and descriptions of the boats fished on. In my experience, while dates, including specific years, are rarely recalled with any accuracy, technical attributes of all boats fished on are clearly recalled, particularly if discussions/interviews begin with the first boat and systematically work forward through all boats fished on until the present day (or retirement). Questions can be productively asked respecting matters such as experiences had, observations made, locations, times of year, and so on with reference to the boat being fished on and the captain/crew being fished with 'at that time'. Working through the rank-ordered list of peer acknowledged local ecological knowledge experts in this manner should provide a very thorough description of local understandings, experiences, and observations respecting matters such as ecological relationships and species behaviours associated with particular 'places' within the fishing ground.

I also think that it is critical to develop a way to determine the extent to which specific attributes, ecological claims, and such are commonly described among and expressed as 'local knowledge' by those identified as experts. In one informal experiment I worked with a key informant and paper readouts from his echo sounder as a way of identifying locally important fishing places as well as various biotic and abiotic attributes associated with these places. I then made up a 'key' from this information and prepared several sheets with unlabeled echo sounder readouts of these places. These sheets were shown to other key informants fishing on the ground. They were asked whether or not they recognised the places represented by the echo sounder images. If they did, they were asked to describe the biotic and abiotic qualities that they associated with these places as well as to relate any experiences they associate with the locations. I did this in an unsystematic manner, essentially as an attempt at developing a way to describe and to test the extent to which understandings of the fishing ground were held in common. While never taken to its conclusion or developed to its full potential, not surprisingly this 'test' strongly associated detailed understandings and ability to identify 'places' with the most experienced harvesters. That is, the most experienced were more likely to identify the 'places' and to associate similar biotic and abiotic attributes. I suspect that there is considerable potential in developing elements of this sort of procedure with respect to documenting and verifying various core attributes of local ecological knowledge. I also suspect that this sort of technique would allow for reasonably comprehensive descriptions and understandings of the socio-economic and political attributes, conditions and contexts associated with becoming a bearer of detailed ecological knowledge. An approach reflecting these qualities but drawing on small scale maps could be developed for any aquatic environment, including estuaries, rivers and lakes.

This design has potential when working with non-native fish harvesters, recreational fishers and, possibly, First Nation harvesters. Certainly at least aspects of the qualitative strategies and approaches outlined would be applicable to working with First Nations harvesters and fisheries scientists. In these two communities qualitative approaches would be essential and most sensible. Working with First Nations persons on ecological knowledge issues would, first, entail developing a means to identify those considered by the Mi'kmaq to be most knowledgeable. For instance, given the fact that the scale and characteristics of Mi'kmaq participation in American Eel fisheries are apparently unrecorded by government offices, identifying knowledge experts will require working with existing community organisations and leadership. This research would also need to be framed with reference to the mores of community conduct and regard respecting ecological knowledge. Likely, Mi'kmaq would need to be engaged in the design of research processes and tools such as interview forms. Mi'kmaq would also need to participate as interviewers, particularly given that the Mi'kmaq language may need to be employed when working with community elders and that the Mi'kmaq have concerns about the control and dissemination of 'their knowledge'.

Identifying fisheries scientists with whom to work does not pose a similar difficulty. For instance, core current and past American eel fisheries science and biology/ecology researchers are retrievable from authorship and citation references. Certainly a design employing an intensive interview with follow-up seems best suited. In addition to gathering the intellectual and research experience genealogy through detailing background educational, employment and research experiences, questioning might focus productively on 'black box' topics such as the reasons for the apparent absence of information respecting matters such as eel reproductive behaviours and elver biomass relation with reproductive dynamics/sustainability. Explanations respecting the reasons for the rather extraordinary absence of First Nations and recreational harvesting from fisheries assessments would also be useful. In this work it would be important to detail the researchers' actual field experiences and observations, in addition to their work with official statistics. If there has been direct participation in field research, details such as location and time of year would be critical to assessing researchers' observations. Where actual field research has been conducted, a follow-up interview might productively employ close-scaled topographic/nautical maps for the purpose of cueing recollections and contextualising/referencing observations/experiences. Finally, this interview, as with all of the others, should provide opportunity for the researchers to comment upon matters such as research needs respecting understandings of the American Eel and its ecology, the relation between existing knowledge and fisheries management initiatives (e.g., experimental elver fisheries), and explanations for the recent declines in eel and eel landings.

Identifying non-native recreational eel fishers may also prove a challenge, particularly if licensing information is not readily available. In the absence of such information, one approach would be to find one recreational user; and, towards the end of the interview, request the names of and contact information for additional users. In short, employ a network approach, focused on the domain of a local estuary, river or lake. A similar qualitative strategy to the one outlined above would prove useful in so far as it would detail personal background, attributes of experiences in the recreational eel fisheries, and knowledge of the fishing grounds. Recreational fishers may have considerable information to add respecting the characteristics of eel populations as well as environmental factors potentially influencing population trends, distributional variations/changes, and population dynamics.

As an aspect of working with each of the communities of users, it would be interesting to document the extent and character of relations and interactions that each community has had or currently has with the other. Learning of these qualities would assist in determining the extent to which each communities' concerns and understandings respecting the Eel and the Eel fisheries have arisen from either their own experiences or a combination of experiences and interactions. Antidotal material suggests that the Eel fishery has been and remains of considerable importance for both the Mi'kmaq and the Acadian French communities. These communities have been and remain closely associated within Maritime Canada, allied historically and, to this day, often living in adjacent settlements. Of course, relations between them have not always been cooperative as fully evident in the recent Burnt Church, New Brunswick, conflicts respecting Mi'kmaq participation in the commercial lobster fishery.

Finally, I think that social research can have a central role in documenting and giving voice to ecological knowledge systems. But, with this role comes the rather onerous responsibility of assuring that the documentation and 'voice' provided contribute meaningfully to something other than the entrenchment of cleavages, vested interests and power inequities. Additionally, the association of social research outcomes with the championship of particular approaches to resource management certainly requires that the 'evidence' clearly, unequivocally, and confidently supports the positions taken. That is, championing implementation of management policy carries the risk of achieving little more than failure and the consequences of same as experienced in the lives and well-being of harvesters, their families and their communities. It seems to me that championship underwritten by anything less than evidence-rooted and tested 'knowledge' is little more than an ideological, self-indulgent and irresponsible act. Few social researchers and scientists must live with the consequences of their failed management preferences, i.e., lost employment, economic hardship, and crises in personal, family and community life. As one New Brunswick marine harvester was reported as telling the Kirby Commission, all fisheries scientists, researchers and policy makers should have their incomes reflect annual returns to the fisheries they study and the harvesters they 'manage'. Perhaps, if such were the situation, scientists, researchers and managers would be more careful and concerned about the meaning and the impacts of the management policies with which 'others' must live.