biology and conservation
Transcript of biology and conservation
Partnering for greater success - Kainer et al.
Partnering for greater success: Local stakeholders and research in tropical
biology and conservation
Karen A. Kainer1, 2
, Maria DiGiano3, Amy Duchelle
2, Lúcia H.O. Wadt
4, Emilio Bruna
1, 5,
Jonathan L. Dain1
1Center for Latin American Studies, University of Florida, P.O. Box 115530, Gainesville, FL,
32611-5530, USA
2School of Forest Resources and Conservation, University of Florida, P.O. Box 110410,
Gainesville, FL, 32611-0410, USA
3School of Natural Resources and the Environment, Gainesville, P.O. Box 116455, Gainesville,
FL, 32611-6455, USA FL, USA
4Centro de Pesquisa Agroflorestal do Acre (Embrapa Acre), Caixa Postal 321, Rio Branco, Acre,
69908-970, Brazil
5Department of Wildlife Ecology and Conservation, University of Florida, P.O. Box 110430,
Gainesville, FL, 32611-0430, USA
Received___________; revision accepted___________.
Partnering for greater success - Kainer et al.
ABSTRACT 1
Local communities are important stakeholders in resource management and conservation efforts, 2
particularly in the developing world. Although evidence is mixed in suggesting that these 3
resident stakeholders are optimal forest stewards, it is highly unlikely that large tracts of tropical 4
forests will be conserved without engaging local people who depend on them daily for their 5
livelihoods. Stakeholders, who reside in biodiverse ecosystems like tropical forests, are the 6
largest direct users and ultimate decision makers of forest fate, can be great investors in 7
conservation, harbor local ecological knowledge that complements Western science, and 8
frequently have long-term legitimate claims on lands where they reside. Research partnerships 9
with local stakeholders can increase research relevance, enhance knowledge exchange and result 10
in greater conservation success. Different phases of the research cycle present distinct 11
opportunities for partnership, with flexibility in timing, approaches and strategies depending on 12
researcher and local stakeholder needs and interests. Despite being the last step in the research 13
process, dissemination of results can be the best starting point for researchers interested in 14
experimenting with local stakeholder engagement. Still, tropical biologists might not choose to 15
partner with local people because of lack of institutional rewards, insufficient training in 16
stakeholder engagement, insecure research infrastructure in community settings, and time and 17
funding limitations. Although not appropriate in all cases and despite significant challenges, 18
some biological scientists and research institutions have successfully engaged local stakeholders 19
in the research process, proving mutually beneficial for investigators and local people alike and 20
resulting in important innovations in tropical biology and conservation. 21
22
Keywords: Community; dissemination, returning results, participatory research 23
1
Partnering for greater success: Local stakeholders and biological/conservation 24
research in the tropics 25
26
THE NEED FOR TROPICAL BIOLOGY AND CONSERVATION TO BE MORE INCLUSIVE OF HUMANS and 27
human activities is indisputable. The largest professional society of tropical biologists has 28
expanded their mission to reflect these 21st century realities, clearly articulating the need to move 29
“beyond paradise”- beyond the vision of protecting an undisturbed wilderness to one that more 30
fully embraces humans as integral components of tropical ecosystems (ATBC 2004). While their 31
primary research focus will continue to be biodiversity and ecosystem function, tropical 32
biologists are now expected “to actively assist in developing action plans for long-term 33
conservation, use, and management of tropical landscapes” (ATBC 2004, p.3). This updated 34
mission requires integration of the broader set of values and concerns held by rural people, 35
adoption of interdisciplinary and participatory approaches that embrace a larger community of 36
social scientists and rural communities, and enhanced linkages between science and policy 37
(ATBC 2004). While there is consensus that this shift needs to occur, there are many challenges 38
to moving beyond disciplinary foundations in the biological sciences to more effectively address 39
human needs and interests. Societal engagement needs to occur at multiple levels to develop 40
systems that sustain global biodiversity and human well-being. In this paper, we focus on efforts 41
to integrate research and the exchange of knowledge with local people living in and around 42
tropical ecosystems, particularly in tropical forests. Although evidence is mixed in suggesting 43
that these resident stakeholders are optimal forest stewards (Agrawal and Gibson 1999), it is 44
highly unlikely that large tracts of tropical forests will be conserved without engaging the local 45
people who depend on them daily for their livelihoods (Scherr et al. 2002). We aim to illustrate 46
2
not only why research partnerships with local people often make sense, but also share some 47
strategies for integration of local stakeholders into the research process and institutionalization of 48
these efforts. 49
50
WHY PARTNER WITH LOCAL PEOPLE? 51
LARGEST DIRECT USERS AND ULTIMATE DECISION-MAKERS.–Rural communities are the largest 52
direct users of tropical forests. Forests yield food, construction materials, medicines, fuel, and 53
cash, as well as local ecosystem services such as flood control, soil enrichment and stabilization 54
− all critical to sustain and improve rural livelihoods. In addition to this practical supply of local 55
goods and services, forest-dwelling people often value forests for cultural, ancestral, and spiritual 56
factors more elusive to quantification. 57
Their close proximity to tropical forests also means that local people frequently exercise 58
final, on-the-ground decisions about forest fate. Although certainly privileged and constrained 59
by an array of extra-local drivers (Kaimowitz & Angelsen 1998, Wood 2002, Chomitz et al. 60
2007), they are often the ultimate decision-makers, determining whether forests will be 61
converted (or not) and whether resources will be used sustainably (or not). If tropical forests 62
were not considered critical at other levels of society, this local influence might not be contested. 63
Tropical forests, however, provide innumerable products and services appreciated at larger 64
regional, national and international scales, including timber and non-timber forest products and 65
multiple ecosystem services such as biodiversity conservation, carbon storage and sequestration, 66
and watershed protection. Most recently, the crucial role of tropical forests in global climate 67
regulation has captured international scientific and public attention; almost 1/5 of all greenhouse 68
gases originate from tropical deforestation (Stern 2006). 69
70
3
SIGNIFICANT OWNERSHIP AND CONTROL. –Increasingly, local de facto influence over tropical 71
forest fate is turning into legal authority. Almost 25% of all tropical forests are currently owned 72
or legally managed by local communities (White & Martin 2002). This proportion represents a 73
doubling of the previous 15 years total, and is expected to double again in the next 15 years as 74
decentralization and devolution of public forests to local control proceed (Molnar 2003). These 75
devolution and decentralization efforts have been motivated by various political, economic and 76
social factors. For example, it has been suggested that governments rarely have the resources to 77
monitor and regulate vast forest expanses or the ability to manage them effectively. Economic 78
arguments in favor of decentralizaton and devolution have centered on restructuring ownership 79
systems (or land tenure) to encourage greater economic efficiency and attract foreign investment. 80
Social movements, over decades and across the globe, have made successful claims that local 81
people substantially contribute to forest management and conservation, and therefore should be 82
granted rights of access and control of resource-rich areas. Human rights organizations have also 83
raised ethical arguments when protesting displacement of local peoples to create national parks 84
and other conservation units. The bottom line, however, is that local people not only inhabit 85
spaces we are trying to conserve, but also have significant rights and perhaps motivations to be 86
considered potential conservation partners (Vermeulen & Sheil 2006, Sunderland et al. 2007). 87
88
INVESTORS IN CONSERVATION. –Some studies have highlighted the abilities of local groups to 89
maintain or increase tropical forest cover in countries like Nepal (Guatam et al. 2002), Mexico 90
(Bray et al. 2004), Indonesia (Shiel & Boissière 2004) and Brazil, even in the face of acute 91
agricultural expansion (Nepstad et al. 2006). This is not meant to suggest that all communities 92
have the ability or desire to halt deforestation or increase forest cover within their domain. In 93
fact, local control may not be enough to conserve forests when economic benefits of conversion 94
4
outweigh forest conservation values (Wunder 2000). However, research does indicate that some 95
are investing their time, labor and financial resources in these activities. Molnar et al. (2007) 96
estimate that communities dedicate between $1.5 and 2.5 billion per year to forest conservation 97
and management, an annual amount approximately equal to protected area budgets in developing 98
countries. These estimates of community investment are derived from data on cash expenditures 99
and in-kind labor directed to activities such as fire control, guarding land and resources, 100
biological monitoring and habitat restoration (Molnar et al. 2007). 101
102
COMPLEMENT TO WESTERN SCIENCE. –Local people know resources in ways scientists and off-site 103
managers typically do not (Moller et al. 2004, Chalmers & Fabricius 2007) (Table 1). Western 104
science, which generates knowledge through strict and universally agreed-upon rules, is the 105
conventional source of information for almost all formalized forest management. This approach 106
contrasts with local ecological knowledge which is generated on site by trial and error and is 107
often cumulative, passed down through generations to explain relationships between humans and 108
their environment. Engaging local experts, combining methods, and exchanging information and 109
insights generated by these different knowledge systems can lead to more effective working 110
partnerships between local people and outsiders to co-manage forests, a joint management 111
approach that is gaining currency in practice. 112
113
INCREASE RESEARCH RELEVANCE TO LOCAL REALITIES. –Research carried out in conjunction with 114
local people, close to the resource, has a greater chance of being relevant to local realities and 115
needs. Partnering makes it more likely that local people will take ownership of research results, 116
whether obtained through experimentation or observation. As local people increase their 117
knowledge and direct experience with the scientific research process, results will be better 118
5
understood. Similarly, when encouraged to reach their own conclusions, local people are more 119
likely to accept them (Sheil & Lawrence 2004) and apply them in management decisions. 120
121
RELATIVE NUMBERS AND PERMANENCE ON LANDSCAPE. –White & Martin (2002) estimate that 122
400 to 500 million non-indigenous people directly depend on tropical forests for their 123
livelihoods, in addition to the approximately 60 million indigenous people who reside in tropical 124
rainforests. Based on these numbers and their relative permanence on the landscape, partnering 125
in conservation and conservation research, although certainly not without challenges, seems 126
imminently logical (Campos & Nepstad 2006). Partnering specifically with those living close to 127
protected areas offers an additional opportunity to effectively expand park boundaries (Bawa 128
2006). People living in and around protected areas will likely remain there long after research 129
projects end, after governments change hands, and after scientists leave. Time horizons dictated 130
by grant cycles limit effectiveness of many well-intentioned conservation projects (Bawa 2006) 131
while joint learning between scientists and local people through research and other discovery 132
processes may facilitate improved management that will last longer than project cycles. 133
134
LONG-TERM LEGITIMATE CLAIMS. –In addition to the above efficiency arguments, there are also 135
ethical reasons to integrate local stakeholders into tropical research projects. While many 136
tropical forest benefits accrue at higher transnational and global scales (i.e., biodiversity 137
conservation, carbon storage and sequestration), the costs of maintaining them are 138
disproportionally borne at lower national and regional scales, with the largest burden typically 139
felt at the local level (Wells 1992). Communities attempting to address their own livelihood 140
needs are often expected to attend to additional, much broader international forest conservation 141
objectives. It seems only fair that tropical forest research agendas, which are typically set at 142
6
national if not international levels, should be determined with input from those who have resided 143
in the forest for generations and increasingly aspire to (and are expected to) manage their forest 144
ecosystems with greater economic and ecological sophistication. 145
146
STRATEGIES FOR EFFECTIVE LOCAL PARTNERSHIPS 147
If research partnerships with local communities are accepted as an important strategy of tropical 148
conservation and restoration efforts (ATBC 2004), how can we go about developing them? How 149
can we integrate rural communities and their support organizations into the research process and 150
enhance knowledge exchange? Lessons from predecessors focused on tropical agricultural 151
research and community forestry can help inform this expanded research mission. 152
153
LEARNING FROM PREDECESSORS. –Over the past four decades, researchers and research 154
institutions have developed and tested diverse approaches and methods for partnering with rural 155
people to improve agricultural and forest-based livelihoods. The Green Revolution of the 1960s, 156
which produced new high-yielding grain varieties, resulted in tremendous advances in food 157
production across the globe, but tended to favor only those farmers who were already in 158
relatively advantageous positions (Whyte 1986). The rural majority, small-scale, resource-159
limited farmers who were largely passed over by the Green Revolution, began to receive some 160
attention in the 1970s with publication of Schumacher’s (1973) Small is Beautiful and 161
subsequently World Neighbors’ Two Ears of Corn (Bunch 1982). Conceptual and practical 162
approaches to research also emerged with an emphasis on “farmer first” (Chambers 1983; 163
Chambers et al. 1989) and the Farming Systems Research and Exension (FSRE) approach 164
(Hildebrand 1981, Hildebrand 1986). These new perspectives were highly innovative not only in 165
their focus on smallholders, but also in their assumption that farmers should be partners in 166
7
research endeavors to design and evaluate new technologies (Ashby 1990a, b). These scientists 167
advocated “on-farm” research, arguing that conducting experiments with farmers in situ, despite 168
the risks and potential loss of experimental control, greatly improved the speed, science and 169
application of agricultural advancement. FSRE practitioners also developed methods that 170
allowed multidisciplinary teams of scientists to engage in joint research activities, seeking to 171
understand the farm as a complex, interconnected system rather than a series of isolated farm 172
components defined by disciplinary lenses (Hildebrand & Waugh 1986). These early 173
experiences in interdisciplinarity (Rhodes 1984) underscored the tremendous benefits of strong 174
research collaborations between biologists and social scientists – a benefit still considered so 175
vital today that it is embedded in one of three guiding principles for tropical biologists (ATBC 176
2004). 177
The Farming Systems Research and Extension approach also highlighted the importance 178
of the household as the central decision-making unit of the farming system (Poats & Feldstein 179
1989). Over time, the assumed homogeneity of the farm household was dispelled as gendered 180
differences in household roles and their impact on resource use decisions became evident 181
(Overholt et al. 1985). These themes of participation, gender, and people-centered research have 182
more recently been extended to natural resource management and community forestry (Arnold 183
1992, Thomas-Slayter et al. 1993, FAO 1999). Fresh methodological advancements through the 184
Center for International Forestry Research (CIFOR) and others have more fully integrated 185
fundamental issues of biodiversity, ecosystem services, and ecological integrity with the 186
livelihood concerns of forest-based and other natural resource dependent groups (Wollenberg et 187
al. 2000, Campbell & Luckert 2000, Evans et al. 2006). Similarly, local ecological knowledge 188
has also come to the fore when expanding to forest-focused rural peoples (Berkes et al. 2000). 189
The hard-won lessons of these agricultural and forestry predecessors working in the developing 190
8
world can serve tropical biologists well as they pursue their broader participatory and 191
interdisciplinary research agenda in partnership with local stakeholders. 192
193
INTEGRATION AND THE RESEARCH CYCLE. –How might some of these strategies, tools and 194
approaches be applied during the research cycle? There is now a relatively large body of 195
academic and practitioner experiences with tropical resource management and conservation 196
found under the rubric of “participatory” or “collaborative” research (Slocum et al. 1995, Evans 197
et al. 2006, Arnold & Fernandez-Gimenez 2008, Lynam et al. 2007). These research 198
frameworks consider a continuum that ranges from non-participation to full partnerships, in 199
defining research agendas, executing projects, interpreting, using and disseminating results 200
(Castillo et al. 2005). One innovative book jointly evaluates the success of participatory research 201
projects from the perspectives of both lead scientists and local collaborators – the latter being a 202
voice rarely heard in the scientific literature. This dual reporting pushes the envelope of full 203
partnership by effectively demonstrating differences in evaluation measures: complementary 204
views of certain projects and quite contrasting views of others (Fortmann 2008). Our intent is not 205
to thoroughly critique the details of engaging local people in the research process, but rather to 206
highlight a few key opportunities within this process where biological scientists have and will 207
continue to develop local research partnerships (Figure 1). 208
The initial stage of research design, specifically development of research questions, is a 209
key moment for engaging stakeholders in the research process. While not always possible or 210
appropriate, partnering at this stage can build in greater research relevance, trust amongst 211
partners, and overall buy-in to the research project (Barnard 2006). Similarly, local feedback at 212
the research design phase on preconceived research ideas can help redirect or refine research to 213
better meet the needs and realities of local contexts. For example, experimental treatments for 214
9
silvicultural management may be redefined to integrate an already-practiced treatment or one 215
that is more likely to be applied given local constraints. Finally, researcher-community partners 216
should consider developing a cooperative research agreement whereby expectations, 217
responsibilities and negotiated terms of collaboration are transparent (Firehock 2003). 218
Thoughtful communication at the beginning will pay off throughout the collaborative process. 219
Fundraising for ecological research is always a concern, and inclusion of local people 220
when setting research agendas certainly complicates matters. Nonetheless, explicit inclusion of 221
local capacity building, dissemination of results and other types of partner engagement activities 222
can be advantageous in making the case for research funding. The U.S. National Science 223
Foundation emphasizes “broadening participation of underrepresented groups”, “enhancing 224
networks and partnerships” and “disseminating results broadly to enhance scientific and 225
technological understanding” (NSF 2007). Applicants for the doctoral dissertation research 226
abroad field grants sponsored by the U.S. Department of Education Fulbright Hays Program 227
must demonstrate appropriate contacts and affiliations abroad as well as plans to share research 228
results with host-country scholars and officials. Insertion of budgetary lines to fund activities 229
that attend to local partner needs, including attention to direct resource users, as related to the 230
project, even if they are not completely funded, can go a long way to strengthening researcher-231
community relations. Formal partnerships are also required for granting of research visas to 232
foreigners in many tropical countries. 233
Implementation, from data collection to interpretation, is another phase of research in 234
which local stakeholders might be effectively integrated. Concerns over data quality can be a 235
concern to tropical biologists engaged in collaborative projects. However, recent experiences 236
with the use of parataxonomists − field-based inventory specialists who are usually residents in 237
the ecosystem studied, however, have been largely positive −finding that these “specialists” have 238
10
been cited as key assets in tropical conservation (Janzen 2004, Basset et al. 2004, Sheil & 239
Lawrence 2004). Continued refinement of the limitations and applications of paratoxonomy 240
coupled with solutions for improving species identification consistency show great promise 241
(Baraloto et al. 2007). Researcher interactions with local people during data collection may also 242
provide day-to-day opportunities for debate over observations, findings and interpretation of 243
results (Parrado-Rosselli 2007). For scientists who can successfully partner with local 244
stakeholders during research implementation, the rewards can involve in-depth knowledge 245
exchange and interpretation of findings from diverse perspectives that can strengthen 246
understanding of tropical ecosystems and build more sustainable conservation strategies. 247
Results dissemination is likely the research phase where scientists can most readily 248
integrate local stakeholders into the research process. While dissemination comes at the end of 249
the research process, it may be a logical first step for researchers interested in experimenting 250
with local stakeholder engagement. The extension of ecological findings can take on various 251
formats including interactive workshops, extension pamphlets, manuals, flannel boards, 252
illustrated stories, school curricula, coloring books, radio, field visits, and more (Shanley et al. 253
1996, Shanley 1998, Shanley & Laird 2002). The dissemination phase also provides an 254
opportunity to thank local people for their engagement in the research process. Simple gestures 255
such as presenting certificates of participation or holding community celebrations can reinforce 256
the give and take needed to foster genuine partnerships between scientists and local stakeholders. 257
In both dissemination of results and giving closure to the research process, scientists are only 258
constrained by their creativity. 259
260
WHAT HOLDS US BACK? 261
11
There are multiple reasons why tropical biologists might not choose to engage with local people. 262
Below, we highlight some of the difficulties in harmonizing distinct local and scientific agendas, 263
as well as how some of these challenges might be confronted through institutionalization and 264
other means. 265
266
NOT APPROPRIATE IN ALL CASES. –Some tropical research is less applicable to local people and 267
their management systems than others. Does a scientist constructing a molecular phylogeny of 268
dragonflies need to develop his/her research questions in collaboration with communities? Some 269
kinds of science clearly do not benefit from local engagement, and can be efficiently executed 270
without this type of local partnership. However, much can be still gained from explaining the 271
objectives and outcomes of such research to local communities. In addition to establishing 272
positive relationships with community members who might one day host future researchers, 273
transparency regarding specimen collection and the motivation for conducting such research can 274
help assuage concerns about access to biological or cultural patrimony. 275
276
LACK OF FACILITIES. – Even if science can benefit by embedding a research project in a 277
community-managed forest or locally-run conservation unit, there will likely be less 278
infrastructural and logistical support to execute research. Internet access, detailed soils maps, 279
and the accumulated body of knowledge that comes from working in a well-established research 280
station will be lacking. Also absent will be a group of scholars with specialized scientific 281
expertise, although they may find “in-community” collaborators with a wealth of ecological 282
knowledge that complements their own. Linkages with local universities and research groups 283
can also alleviate some of these challenges, but there are clearly trade-offs in conducting 284
research “on-station” vs. “in-community”. Two innovative tropical research centers have 285
12
reconciled some of these trade-offs by creating spaces that foster high quality scientific research 286
and joint learning in conjunction with local stakeholders: Ashoka Trust for Research and 287
Ecology and the Environment (ATREE) in India and the Institute for Ecological Research (IPÊ) 288
in Brazil. Such institutes adopt the regional landscape as their research sites, integrate university 289
training and research directly into their programs, and simultaneously engage local stakeholders 290
in highly successful conservation/sustainable development partnerships. 291
292
REQUIRES ADDITIONAL RESOURCES. – Engaging local stakeholders at any degree of intensity is 293
time-consuming and may require extra funding. As Shanley et al. (this volume) point out; 294
donors must be on board if research in tropical biology and conservation is to be significantly 295
expanded to integrate local stakeholders. Notwithstanding, one only has to look as far as IPÊ 296
and ATREE to see unquestionable evidence that donors are interested in investing in successful 297
collaborative research and action partnerships. 298
299
UNCERTAIN FUTURE FOR FIELD SITES. – Linked to these trade-offs, there is potentially greater risk 300
in investing in a research site that lacks the security of a biological station or formal protected 301
area. Losing a precious replicate, or even an entire experiment, to cattle herbivory or escaped 302
fire is a legitimate concern, and establishing long-term studies can be a risky proposition. Early 303
and continuing investment in community relations, including shared responsibilities and benefits, 304
can alleviate some of these risks −the more knowledgeable and vested local people are in the 305
research, the greater the security of the research endeavor. 306
307
LACK OF INSTITUTIONAL REWARDS.–Until the engagement of local stakeholders is considered part 308
of the job, tropical biologists are less likely to invest in local collaborative partnerships. Many 309
13
scientists in academia have found that engaging local communities in science is not typically 310
rewarded (Barnard et al. 2006); furthermore, potentially lower productivity (as currently defined 311
in academic circles) resulting from the challenges described above may even hinder professional 312
advancement. Scientists rarely receive significant institutional credit for research products such 313
as manuals or locally-oriented education materials that are not peer-reviewed. It is no surprise, 314
therefore, that many tropical researchers consider information transfer a separate and perhaps 315
lower endeavor (Shanley & Laird 2002). It is logical to consider the scientific process complete 316
once findings are published in scientific journals; indeed refereed publications are central to 317
fundraising and career advancement (Shanley & Laird 2002). 318
This aspect of scientific culture, however, is being challenged in some circles (Shanley 319
this volume). On one end, scholars fearful of an overemphasis on “career assessment by 320
numbers” (Kelly and Jennions 2006) are critically examining the growing popularity of impact 321
factors and the h-index, questioning if “institutions have a misguided sense of the fairness of 322
decisions reached by algorithm” (Lehmann et al. 2006). On the other end, universities, 323
particularly those with a land-grant mandate to solve problems, and research institutions such as 324
the Center for International Forestry Research are increasingly attempting to integrate measures 325
of research impact on target stakeholders. Considering the next generation of tropical 326
researchers, graduate training programs such as the University of Florida’s Tropical 327
Conservation and Development Program are attempting to institutionalize host-country partner 328
engagement by linking student academic credits and field research funding to engagement of 329
local people (Duchelle et al. this volume). 330
331
DON’T KNOW HOW.–The outlook and skills necessary to engage communities are often not found 332
in organizations that collect and analyze scientific data (Shanley & Laird 2002). Tropical 333
14
researchers are trained in modern scientific methods and perhaps local languages, not the 334
engagement of stakeholders. Similarly, collaborative research methods are not as well-known to 335
biological scientists. During formative graduate training, few courses are offered in which 336
students can garner skills in information exchange, group facilitation, and negotiation with 337
partners (although see Duchelle et al. this volume). And even if courses are offered, they are 338
generally viewed as extra-curricular and tacked on to an already heavy course load. 339
Notwithstanding, methods and approaches for partnering in research with rural people have been 340
developed by predecessors, and are growing. Furthermore, research protocols have been 341
developed that lay out clear guidelines for ethical and effective research within community-based 342
collaborative projects (see Firehock 2003). 343
344
MAY BE UNCOMFORTABLE.–Finally, collaborating with local people may take scientists out of 345
their comfort zone. The intellectual tendency of tropical researchers to stay firmly grounded in 346
their biological roots is comforting (Robinson 2006), while the idea of nurturing different 347
relationships and networks, possibly with groups critical and perhaps suspicious of researchers, 348
is daunting. New languages and cultures can also create discomfort; for non-natives, an 349
imperfect grasp of the local language can make communication difficult, while for host-country 350
nationals, local dialects, speech patterns and ethnic, gender and class divisions can make 351
interactions awkward. Even disseminating research findings to local stakeholders is not without 352
risks, as results can be challenged, misinterpreted and even co-opted to pursue other agendas 353
(Barnard et al. 2006). This can make researchers, who are usually exceptionally cautious in their 354
research interpretations and pronouncements, uncomfortable. Nonetheless, some biologists are 355
learning by doing, gradually becoming comfortable with the ambiguities of conducting research 356
with local stakeholders. Parrado-Rosselli (2007) describes an incremental process whereby the 357
15
research relationship with a Colombian Indigenous group grew increasingly collaborative over 358
time, ultimately resulting in better understanding of fruit availability and seed dispersal and more 359
sustained conservation efforts at the local level. The growing numbers of refereed publications 360
that relate experiences such as the above are evidence that sectors of the scientific community 361
are comfortable with and value collaborative research partnerships with local stakeholders. 362
363
CONCLUSIONS 364
Although not without challenges, we believe that when appropriate, engaging local stakeholders 365
in the scientific research process has the potential to be mutually beneficial for investigators and 366
local people, and can result in important innovations in tropical biology and conservation. 367
Institutionalization of these approaches may be critical to helping researchers interested in 368
engaging local people overcome some of these challenges. These include research centers such 369
as ATREE and IPÊ who at their core bridge scientific research and training with direct 370
engagement of local stakeholders; graduate education programs that train and encourage 371
upcoming scientists in how to form collaborative partnerships with local stakeholders; some 372
evidence of change in donor culture; and recent publications of participatory research tools and 373
experiences in tropical biology and conservation that provide guidance. Tropical biologists who 374
are interested in engaging local people, however, need not wait for institutional and cultural 375
change before experimenting with their own brand of partnerships with local stakeholders. 376
377
ACKNOWLEDGEMENTS 378
We gratefully acknowledge the invitation and challenge laid out by symposium organizers to the 379
2007 Annual Meeting of the Association of Tropical Biology and Conservation (ATBC) in 380
Morelia, Mexico. They inspired us to address the “limited practical transfer of the immense 381
16
scientific research output to local communities” and other decision-makers. We also thank our 382
many research colleagues, on paper and in person, who have stimulated our creativity and 383
challenged our thinking of community-based research partnerships. Finally, we are most grateful 384
to the many local stakeholders who have engaged us in their experiments, shared their 385
observations, and challenged us to be better scientists. 386
387
LITERATURE CITED 388
AGRAWAL, A., AND C. C. GIBSON. 1999. Enchantment and disenchantment: the role of 389
community in natural resource conservation. World Development 27:629-649. 390
ARNOLD, J. E. M. 1992. Community forestry: ten years in review (revised edition). Food and 391
Agriculture Organization of the United Nations, Rome. 392
ARNOLD J. S., AND M. E FERNANDEZ-GIMENEZ. 2008. Engaging communities through 393
participatory research. In E. M. Donaghue and V. S. Sturtevant (Eds.). Forest community 394
connections: implications for research, management and governance. Resources for the 395
Future, Washington, DC. 396
ASHBY, J. 1990a. Evaluating technology with farmers: a handbook. Centro International de 397
Agricultura Tropical, Cali, Colombia. 398
ASHBY, J. 1990b. Small farmers’ participation in the design of technologies. In M. A. Altieri 399
and S. B. Hecht (Eds.). Agroecology and small farm development, pp. xx-xx. CRC 400
Press, Boca Raton, FL. 401
ATBC (ASSOCIATION FOR TROPICAL BIOLOGY AND CONSERVATION). 2004. Beyond Paradise–402
Meeting the Challenges in Tropical Biology in the 21st Century. ATBC, Washington, DC. 403
17
BARALOTO, C., E. FERREIRA, C. ROCKWELL, AND F. WALTHIER. 2007. Limitations and 404
applications of parataxonomy for community forest management in southwestern 405
Amazonia. Ethnobotany Research and Applications 5: 77-84. 406
BARNARD, G., L. CARLILE, AND D. B. RAY. 2006. Maximising the impact of development 407
research: How can funders encourage more effective research communication? 408
International Institute for Environment and Development (IIED), London. 409
BASSET, Y., V. NOVOTNY, S. E. MILLER, G. D. WEIBLENS, O. MISSA, AND A. J. A. STEWART. 410
2004. Conservation and biological monitoring of tropical forests: the role of 411
parataxonomists. Journal of Applied Ecology 41: 163-174. 412
BAWA, K. S. 2006. Globally dispersed local challenges in conservation biology. Conservation 413
Biology 20: 696-699. 414
BERKES, F., J. COLDING, AND C. FOLKE. 2000. Rediscovery of traditional ecological knowledge 415
as adaptive management. Ecological Applications 10: 1251-1262. 416
BRAY, D. B., E. A. ELLIS, N. ARMIJO-CANTO, AND C. T. BECK. 2004. The institutional drivers of 417
sustainable landscapes: A case study of the “Mayan Zone” in Quintan Roo, Mexico. 418
Land Use Policy 21: 333-346. 419
BUNCH, R. 1982. Two ears of corn: a guide to people-centered agricultural improvement. 420
World Neighbors, Oklanhoma City, OK. 421
CAMPBELL, B., AND M. LUCKERT (Eds.). 2002. Uncovering the hidden harvest; valuation 422
methods for woodland and forest resources. Earthscan, London, UK. 423
CAMPOS, M. T., AND D. C. NEPSTAD. 2006. Smallholders, the Amazon’s new conservationists. 424
Conservation Biology 20: 1553-1556. 425
CASTILLO, A., A. TORRES, A. VELÁZQUEZ, AND G. BOCCO. 2005. The use of ecological science 426
by rural producers: a case study in Mexico. Ecological Applications 15: 745-756. 427
18
CHALMERS, N., AND C. FABRICIUS. 2007. Expert and generalist local knowledge about land-428
cover change on South Africa’s wild coast: Can local ecological knowledge add value to 429
science? Ecology and Society 12(1): 10. 430
CHAMBERS, R. 1983. Rural development: putting the last first. Longman, Harlow, UK. 431
CHAMBERS, R., A. PACEY, AND L. A. THRUPP (Eds.). 1989. Farmer first: farmer innovation and 432
agricultural research. Intermediate Technology Publications, London, UK. 433
CHOMITZ, K.M., P. BUYS, G. DE LUCA, T.S. THOMAS, AND S. WERTZ-KANOUNNIKOFF. 2007. At 434
Loggerheads? Agricultural expansion, poverty reduction, and environment in the tropical 435
forests. World Bank, Jakarta, Indonesia. 284p. 436
EVANS, K. W. DE JONG, P. CRONKLETON, D. SHEIL, T. LYNAM, T. KUSUMANTO, AND C. J. P. 437
COLFER. 2007. Guide to participatory tools for forest communities. Center for 438
International Forestry Research (CIFOR), Bogor, Indonesia. 439
FAO (FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS). 1999. Community 440
forestry publications. FAO, Rome. 441
FIREHOCK, K. 2003. Protocol and guidelines for ethical and effective research of community 442
based collaborative processes. Community Based Collaboratives Research Consortium, 443
University of Virginia, Blacksburg, VA. 444
FORTMANN, L. 2008. Participatory research in conservation and rural livelihoods: doing science 445
together. Wiley-Blackwell, Chichester, United Kingdom. 446
GUATAM, A. P., E. L. WEBB, AND A. EIUMNOH. 2002. GIS assessment of land use/land cove 447
changes associated with community forestry implementation in the Middle Hills of 448
Nepal. Mountain Research and Development 22: 63-69. 449
HILDEBRAND, P. E. 1981. Combining disciplines in rapid appraisal: the sondeo approach. 450
Agricultural Administration 8: 423-432. 451
19
HILDEBRAND, P. E. (Ed.). 1986. Perspectives on farming systems research and extension. Lynne 452
Rienner Publishers, Boulder, CO. 453
HILDEBRAND, P. E., AND R. K. WAUGH. 1986. Farming systems research and development. In P. 454
E. Hildebrand (Ed.). Perspectives on farming systems research and extension, pp. 12-15. 455
Lynne Rienner Publishers, Boulder, CO. 456
JANZEN, D. H. 2004. Setting up tropical biodiversity for conservation through non-damaging 457
use: participation by parataxonomists. Journal of Applied Ecology 41: 181-187. 458
KAIMOWITZ, D., AND A. ANGELSEN. 1998. Economic models of tropical deforestation – A 459
review. Center for International Forestry Research (CIFOR), Bogor, Indonesia. 139p. 460
461
KELLY, C.D., AND M.D. JENNIONS. 2006. The h index and career assessment by numbers. 462
Trends in Ecology and Evolution 21:167-170. 463
LEHMANN, S., A.D. JACKSON, AND B.E. LAUTRUP. 2006. Measures for measures. Nature 464
441:1003-1004. 465
LYNAM, T., W. DE JONG, D. SHEIL, T. KUSUMANTO, AND K. EVANS. 2007. A review of tools for 466
incorporating community knowledge, preferences, and values into decision making in 467
natural resources management. Ecology and Society 12: 5. 468
MOLLER, H., F. BERKES, P. O. LYVER, AND M. KISLIOGLIU. 2004. Combining science and 469
traditional ecological knowledge: Monitoring populations for co-management. Ecology 470
and Society 9(3): 2. 471
MOLNAR, A. 2003. Forest certification and communities: Looking forward to the next decade. 472
Forest Trends, Washington, DC, USA. . 473
MOLNAR, A., M. LIDDLE, C. BRACER, A. KHARE, A. WHITE, AND J. BULL. 2007. Community-474
based forest enterprises in tropical forest countries: Status and potential. International 475
20
Tropical Timber Organization, Forest Trends, and Rights and Resources Initiative. 476
Washington D.C. 477
NEPSTAD, D., S. SCHWARTZMAN, B. BAMBERGER, M. SANTILLI, D. RAY, P. SCHLESINGER, P. 478
LEFEBVRE, A. ALENCAR, E. PRINZ, G. FISKE, AND A. ROLLA. 2006. Inhibition of 479
Amazon deforestation and fire by parks and Indigenous lands. Conservation Biology 20: 480
65-73. 481
NSF (NATIONAL SCIENCE FOUNDATION). 2007. Merit Review Broader Impacts Criterion: 482
Representative Activities. Washington D.C. 483
OVERHOLD, C., M. B. ANDERSON, K. CLOUD, AND J. E. AUSTIN (Eds.). 1985. Gender roles in 484
development projects: a case book. Kumarian Press, West Hartford, CT. 485
PARRADO-ROSSELLI, A. 2007. A collaborative research process studying fruit availability and 486
seed dispersal within an Indigenous community in the Middle Caqueta River region, 487
Columbian Amazon. Ecology and Society 12: 39. 488
POATS, S. V., AND H. S. FELDSTEIN. 1989. Introduction. In H. S. Feldstein and S. V. Poats 489
(Eds.). Working together: gender analysis in agriculture, pp. 1-5. Kumarian Press, Inc., 490
West Hartford, CT. 491
RHOADES, R. E. 1984. Breaking new ground: anthropology in agricultural research. 492
International Potato Center, Lima. 493
ROBINSON, J. G. 2006. Conservation biology and real-world conservation. Conservation 494
Biology 20: 658-669. 495
SCHERR, S.J., A. WHITE, AND D. KAIMOWITZ. 2002. Making markets work for forest 496
communities. Forest Trends, Washington, DC, USA. 497
SCHUMACHER, E. F. 1973. Small is beautiful: economics as if people mattered. Perennial 498
Library, New York, NY. 499
21
SHANLEY, P. 1998. Extending ecological research to meet local needs: a case from Brazil. In T. 500
C. H. Sunderland, L. E. Clark, and P. Vantomme (Eds.). Non-wood forest products of 501
Central Africa: current research issues and prospects for conservation and development, 502
pp. xx-xx. Food and Agriculture Organization of the United Nations, Rome. 503
SHANLEY, P., AND S. A. LAIRD. 2002. “Giving back”: making research results relevant to local 504
groups in conservation. In S. A. Laird (Ed.). Biodiversity and traditional knowledge: 505
equitable partnerships in practice, pp. xx-xx. Earthscan Publications Ltd., London. 506
SHANLEY, P., L. LUZ, J. GALVÃO, AND M. CYMERYS. 1996. Translating dry data for forest 507
communities: science offers incentives for conservation. Rural Development Forestry 508
Network Paper 19e, Overseas Development Institute, London. 509
SHEIL, D., AND A. LAWRENCE. 2004. Tropical biologists, local people and conservation: new 510
opportunities for collaboration. Trends in Ecology and Evolution 19: 634-638. 511
SHEIL, D., AND M. BOISSIÈRE. 2006. Local people may be the best allies in conservation. 512
Nature 440: 868. 513
SLOCUM, R., L. WICHHART, D. ROCHELEAU, AND B. THOMAS-SLAYTER (Eds.). 1995. Power, 514
process and participation: tools for change. Intermediate Technology Publications, 515
London. 516
STERN, N. 2006. The Economics of Climate Change: The Stern Review. Cambridge University 517
Press, Cambridge, UK. 518
SUNDERLAND, T. C. H., C. EHRINGHAUS AND B. M. CAMPBELL. Conservation and development 519
in tropical forest landscapes: a time to face the trade-offs? Environmental Conservation 520
34: 276-279. 521
22
THOMAS-SLAYTER, B., A. L. ESSER, AND M. D. SHIELDS. 1993. Tools of gender analysis: a guide 522
to field methods for bringing gender into sustainable resource management. Program for 523
International Development and Social Change, Clark University, Worcester, MA. 524
VERMEULEN, S. AND D. SHEIL. 2006. Partnerships for tropical conservation. Oryx: 41: 434-440. 525
WELLS, M. 1992. Biodiversity, conservation, affluence and poverty: Mismatched costs and 526
benefits and efforts to remedy them. Ambio 21:237-243. 527
WHITE, A., AND A MARTIN. 2002. Who owns the world’s forests? Forest Trends, Washington, 528
DC. 529
WHYTE, W. F. 1986. The need for a new strategy. In P. E. Hildebrand (Ed.). Perspectives on 530
farming systems research and extension, pp. 1-12. Lynne Rienner Publishers, Boulder, 531
CO. 532
WOLLENBERG, E., D. EDMUNDS, AND L. BUCK. 2000. Anticipating change: Scenarios as a tool 533
for adaptive forest management. Center for International Forestry Research (CIFOR), 534
Bogor, Indonesia. 535
WOOD, C. H. 2002. Land use and deforestation in the Amazon. In C. H. Wood, and R. Porro 536
(Eds.). Deforestation and land use in the Amazon, pp.1-38. University of Florida Press, 537
Gainesville, FL. 538
WUNDER, S. 2000. The economics of deforestation. The example of Ecuador. Macmillan, St. 539
Antony’s Series, Houndmills, UK. 262p. 540
23
TABLE 1. Comparison of two knowledge systems: local ecological knowledge and Western 541
science. 542
Local ecological knowledge Western science
Temporal depth across generations with a rare
historical perspective.
Studies are usually short-term.
Knows local site, but less likely to understand
how it relates to larger spatial patterns and
processes.
Can attain spatial breadth that may link local
site to larger spatial scales, particularly with
new technologies.
Ability to understand and relate local resource
changes and land use outcomes to observed,
complex social and ecological influences.
Ability to monitor and predict large-scale
processes and drivers that escape local
observation.
Ability to observe and record unusual
occurrences and extremes.
Tendency to focus on averages and patterns.
Unusual events may be considered outliers.
Integrated or holistic understanding that may
recognize spiritual and cultural dimensions.
Tendency to break things down into parts for
in-depth understanding; however, integration of
natural and social sciences helps incorporate
spiritual and cultural dimensions.
Rapid and inexpensive gathering of qualitative
information, but perhaps lacks quantitative
precision.
Focus on obtaining and analyzing numerical
data. Precise with what examined. Often
costly.
Intimate involvement may better position local
people to identify problem-oriented hypotheses
and questions.
Focus on identifying theoretical hypotheses and
questions coupled with powerful tools for
testing why.
543