1 Using strategic foresight to assess conservation opportunity 2 3 Carly N. Cooka,b*, Brendan A. Wintlea, Stephen C. Aldrichc, Bonnie C. Wintlea 4 5 a School of Botany, University of Melbourne, Parkville, VIC 3010 Australia 6 b School of Biological Sciences, Monash University, Clayton, VIC 3800 Australia 7 c 8 * Corresponding author: carly.cook@monash.edu Bio-Era, 621 River Road, Stockbridge, VT 05772 United States of America 9 10 1 11 Abstract 12 The nature of conservation challenges can foster a reactive, rather than proactive approach 13 to decision-making. Failing to anticipate problems before they escalate results in the need 14 for more costly and time consuming solutions. Proactive conservation requires forward- 15 looking approaches to decision-making that consider possible futures without being overly 16 constrained by the past. Strategic foresight provides a structured process for considering 17 the most desirable future, and mapping the most efficient and effective approaches to 18 promoting that future. Strategic foresight is an ideal process for seeking, recognizing and 19 realizing conservation opportunities because it explicitly encourages a broad-minded, 20 forward-looking perspective on an issue. Despite its potential value, the foresight process is 21 rarely used to address conservation issues, and previous attempts have generally failed to 22 influence policy. We present the strategic foresight process as it can be used for proactive 23 conservation planning, describing some of the key tools in the foresight tool-kit and how 24 they can be used to identify and exploit different types of conservation opportunities. We 25 emphasize the value of the process using a case study that employed foresight to deliver a 26 strategic plan for climate change adaptation in New York State. The benefits of strategic 27 foresight for identifying conservation opportunities are the focus of the examples we 28 present here, which along with a better understanding of the foresight process and tools, 29 we hope will encourage decision-makers to explore strategic foresight as a way to support 30 more proactive conservation policy, planning and management. 31 2 32 Introduction 33 Policy-making around conservation tends to be reactive, responding only after a problem 34 has occurred, rather than proactive, where problems are anticipated and averted 35 (Sutherland et al. 2011). Proactive policies, such as using environmental flows to prevent 36 tree mortality on flood plains, avoid the need for time consuming and costly reactive 37 responses, such as restoration (Palmer et al. 2008). The often complex and unpredictable 38 nature of many conservation problems can foster this reactive approach because it can be 39 difficult to anticipate problems before they escalate. Despite this uncertainty, 40 environmental decision-makers draw heavily on forecasting probable futures, which 41 involves extrapolating from the past to estimate future conditions (Armstrong 2001), rather 42 than preparing for a range of possible futures. This limits the opportunity to respond quickly 43 to changes in the environment (Dortmans 2005). Moreover, it is a serious impediment to 44 conservation planning in the familiar situation where past conditions are not representative 45 of those yet to come (Carpenter 2002), leading to inaccurate forecasts, because inputs or 46 assumptions were inappropriate. . 47 While past lessons can be informative, they may limit a more creative consideration of 48 future possibilities over longer-term planning horizons (>25 years)(Glenn & Gordon 2009). 49 Strategic foresight aims to promote thinking about possible futures without being overly 50 influenced by the past. A desirable future is first envisaged, and possible pathways and 51 obstacles between there and the present are explored. While forecasting is a tool that can 52 be used within a foresight process, it is the forward thinking approach that considers 53 multiple possible futures and how to achieve the most desirable of those futures that 54 distinguishes strategic foresight from forecasting. 55 Better conservation outcomes are more likely when a structured process is used to consider 56 the likely outcomes of alternative interventions, their consequences for biodiversity, and to 57 identify options that are robust to uncertain futures. Strategic foresight is a method for 58 long-term strategic planning that is a natural fit with addressing conservation problems. It 59 systematically considers a range of possible, probable, or desirable futures, their potential 60 consequences for current and future decisions, and how to promote the most desirable 61 future while avoiding the less desirable (Inayatullah 2007; Cook et al. in press). This 3 62 approach promotes proactive policy-making because it is designed to create a longer-term 63 perspective, explore key uncertainties and potential surprises, decrease reaction time to 64 rapid changes, anticipate unintended consequences, encourage big-picture thinking and 65 shape a preferred future (Cook et al. in press). 66 The broader perspective offered by strategic foresight is useful for realizing ‘conservation 67 opportunity’, defined as circumstances under which conservation goals can be achieved that 68 may not have been previously recognized (Moon et al. this issue). The concept of 69 ‘conservation opportunity’ emerged from the generally poor translation of science into 70 action (Knight et al. 2008) and the understanding that conservation requires an opening for 71 action (Moon et al. this issue). There are three different types of conservation opportunities: 72 potential opportunities, where barrier(s) must be removed to facilitate actions that will 73 generate desirable conservation outcomes; traction opportunities, where a window of 74 opportunity is created by a change in a system that can be exploited to achieve desirable 75 outcomes; and existing opportunities, where everything is in place to take an action that will 76 achieve change (Moon et al. this issue). To maximize the benefits associated with an 77 opportunity, it is important to have tools to recognize potential problems early, identify 78 creative solutions quickly, and consider the consequences of alternative interventions 79 before they are implemented. 80 The aim of this paper is to evaluate the potential of strategic foresight for recognizing and 81 realizing conservation opportunity. First, we briefly outline the foresight process, to 82 illustrate the basic steps involved. Next, we introduce some of the tools that can be used to 83 achieve the different steps. We focus on their suitability for different kinds of conservation 84 opportunities, as characterized by Moon et al (this issue), and provide examples throughout 85 to illustrate the practice and benefits of employing a foresight process. 86 87 What is strategic foresight? 88 Strategic foresight is a versatile process that has been widely adopted in business, the 89 military and economics, and has been used to guide policy development in health, 90 education, biosecurity, transport and policing. The diversity of foresight tools gives the 91 process enormous flexibility, including exploring future market conditions (Wack 1985), 4 92 anticipating unexpected or novel threats (Amanatidou et al. 2012), considering unintended 93 consequences of existing policies (Leigh 2003), and developing new policies that will be 94 robust to a range of future conditions (Van Rij 2010). Broadly, the strategic foresight process 95 involves six steps (Cook et al. in press): 1) setting the scope; 2) collecting inputs; 3) analyzing 96 signals; 4) interpreting the information; 5) determining how to act; and 6) implementing the 97 outcomes. To achieve maximum benefit, it is important that the objectives of the exercise 98 are clear at the outset and that all the steps are completed. 99 Setting the scope of an exercise requires understanding the system of interest, including its 100 geographic, ecological, social and economic limits, and the critical issues and actors in the 101 system (Fig. 1). For example, the Yellowstone to Yukon (Y2Y) large-scale conservation 102 initiative (www.y2y.net) involves a geographically defined system crossing five US states, 103 two Canadian provinces, and two territories, with a range of land tenures and levels of 104 protected area status. Critical issues for the Y2Y initiative include human-wildlife 105 interactions, the fragmenting impact of roads, economic costs and engaging a broad range 106 of stakeholders. The ‘actors’ in this system comprise community groups, government 107 agencies, funders, Native American and First Nations communities, scientists and 108 businesses. 109 Once the limits of the system are defined, the next task is to understand the dynamics and 110 drivers of the system to recognize problems and identify solutions. By collecting and 111 synthesizing a wide range of inputs on past and current trends, participants can explore the 112 system’s dynamics, identify drivers and search for signals of change (Fig. 1). The potential 113 impact of trends and drivers in the system can be explored using driver analysis and trend 114 impact analysis, and cross impact analysis can be used to consider how the system can be 115 manipulated to create opportunities (Table 1). In the Y2Y example, a key driver is population 116 growth in the region, which is increasing pressure for additional infrastructure, such as a 117 proposed new dam that could have significant implications for the Y2Y initiative. 118 One of the main elements of interpreting the wealth of information collected during the 119 foresight process is to consider key uncertainties and their interactions with a range of likely 120 futures. Scenario planning is one approach that offers a useful framework for this (discussed 121 below). It is also important to reveal assumptions and unacknowledged sources of bias in 5 122 how important actors perceive the system and what kinds of futures might unfold. The 123 interpretation stage also involves deciding on a desirable future, using tools such as 124 visioning (Peterson et al. 2003), which can then be used to consider how the possible and 125 probable futures differ from present conditions and from the desired future. 126 Realizing a vision may involve multiple actions. ‘Determining how to act’ (Fig. 1) usually 127 involves devising a strategic plan that clearly identifies who should be involved, the 128 resources required, and the most efficient and effective pathway to overcoming barriers. 129 Backcasting is one approach to identifying multiple pathways to a desired endpoint 130 (discussed below). It is particularly well-suited to large-scale, complex problems 131 characterized by high uncertainty, which makes it ideally suited to conservation problems 132 (Manning et al. 2006). 133 The final step in the foresight process is ‘Implementing the outcomes’ (Fig. 1). 134 Unfortunately, this step is often neglected, particularly in conservation examples (Cook et al. 135 in press). However, the focus of strategic foresight on pre-empting social, political and 136 economic barriers should facilitate effective implementation. 137 138 Key foresight tools for recognizing and realizing conservation opportunity 139 There are good examples of how strategic foresight can be applied to conservation 140 problems, particularly using horizon scanning (Sutherland et al. 2014) and scenario planning 141 (WCS and Bio-Era 2007). However, at present, conservation science is underutilizing 142 strategic foresight, and often failing to capitalize on the strengths of the process by using 143 single tools rather than the complete foresight process (Cook et al. in press). The foresight 144 tool-kit (Table 1) is well-suited to identifying conservation opportunities, and mapping out a 145 path to realize them. The choice of which foresight tools to use depends on the purpose of 146 the exercise. Here we introduce three tools particularly useful for identifying different kinds 147 of conservation opportunity described by Moon et al. (this issue). 148 6 149 Scanning 150 Scanning involves collecting and organizing diverse streams of information (Amanatidou et 151 al. 2012). It forms the basis of most foresight exercises (Glenn & Gordon 2009), and involves 152 desktop searches, surveillance software, and/or expert workshops. In general, scans can 153 identify novel issues (horizon scanning), they can explore and provide surveillance of issues 154 that have already been identified (issue-centred scanning), and the two types of scans can 155 be used in concert to generate hypotheses then explore and monitor those issues 156 (Amanatidou et al. 2012). This flexibility makes scanning well-suited to seeking 157 opportunities across many contexts. 158 At a global scale, annual horizon scanning is used to identify emerging conservation issues 159 (e.g., Sutherland et al. 2014). Early detection enables decision-makers to act strategically 160 and in a timely manner to minimize the negative consequences of threats or maximize the 161 benefits associated with new opportunities. These annual scans extend the traditional view 162 of horizon scanning, conducting the first three steps in the foresight process (Sutherland et 163 al. 2011; Fig. 1). The scans start with literature searches and active consultation with large 164 numbers of people to identify relevant issues, then experts are gathered in workshops to 165 select the most important issues, both threats and opportunities (Sutherland et al. 2011). 166 ‘Issues’ are drawn from a wide range of disciplines, some scientific or technical (e.g. 167 ‘nanotechnologies’), and some political, economic or social (e.g. ‘decline in engagement 168 with nature’). In many cases, participants also identify new opportunities, such as using 169 environmental DNA (a molecular technique to amplify small quantities of genetic material) 170 to detect the presence of species. 171 Scanning can also be automated using software to identify relevant information from the 172 huge volume of online content, including research papers, grey literature, news media, and 173 social media (e.g., Twitter) (Amanatidou et al. 2012). These tools often form the basis of 174 issue-centred scans, providing constant surveillance of important issues (Amanatidou et al. 175 2012), such as tracking infectious diseases in real time (Chan et al. 2010) by combining 176 surveillance with knowledge about the drivers of disease (e.g., population growth or 177 encounters with wildlife) to act as early warning systems (Lyon et al. 2013). 178 7 179 Scenario planning 180 Scenario planning explores current trends, drivers of change, key uncertainties, the 181 relationships among these different elements and how they might influence the future 182 (Schoemaker 1993). This requires detailed information about a system, which can be as 183 broad as the global climate or as narrow as the business environment for a particular 184 company. Generally, multiple scenarios are created by participants (often called scenario 185 development or scenario analysis) and can be based on empirical evidence (e.g., long-term 186 datasets (WCS & Bio-Era 2007), spatially explicit data (Santelmann et al. 2004), or qualitative 187 data (perceptions of experts and stakeholders (Schoemaker 1993)). Scenarios can be 188 expressed as stories to help illustrate the quantitative scenarios. For example, providing 189 details such as, major, unexpected environmental disasters create unprecedented demand 190 for environmental action to illustrate a scenario of sudden environmental change and strong 191 support for conservation action (WCS & Bio Era 2007). By exploring the dynamics of a 192 system, scenario planning helps participants think about possible futures that may arise 193 under different conditions (Peterson et al. 2003), and what those different futures might 194 mean for current decisions (Schoemaker 1995)(the planning aspect of scenario planning). By 195 identifying and challenging assumptions about how the system operates, scenario planning 196 promotes broad and creative thinking, and can lead to previously unseen perspectives 197 (Schoemaker 1993). 198 In the conservation literature, what are described as scenario planning exercises sometimes 199 contain many of the steps in the complete foresight process. These exercises may include 200 setting the scope, collecting inputs, analysing this information and interpreting this 201 information in relation to what it means about possible, probable and desirable futures 202 (e.g., WCS & Bio-Era 2007). This suggests that the conservation community could benefit 203 from a deeper understanding of the foresight process to ensure all steps are conducted and 204 the full benefits of the process are realized by implementing the outcomes of the process. 205 206 Backcasting 207 Backcasting helps to map a logical series of actions to a goal (Dreborg 1996). Some obstacles 208 can appear so large that it is challenging to see a clear way forward. However, starting with 209 a goal and working backwards breaks down a large problem into smaller, achievable actions 8 210 (Manning et al. 2006). Like scenario planning, backcasting can also help participants to think 211 creatively by shifting the focus from present conditions to a situation sufficiently far off in 212 the future to envisage radical change (Cinq-Mars & Wiken 2002). Participants are not limited 213 to seeking solutions to present problems. 214 The systematic process of backcasting makes it ideally suited to assessing the feasibility of 215 solutions to complex problems, particularly where major changes are required over long 216 timeframes (Dreborg 1996). In the Netherlands, backcasting has been used to map a path to 217 achieve sustainable urban development (Dassen et al. 2013), envisaging a desirable future 218 city that articulates the goal of sustainable development, and identifying a set of actions to 219 promote each of these goals. Importantly, explicit consideration was given to the 220 contribution different actors could make in achieving these goals to make the importance of 221 their participation more tangible. 222 223 Using strategic foresight to recognize opportunity 224 Strategic foresight can be useful for identifying all three types of conservation opportunity. 225 The different strengths of individual foresight tools make them better suited to identifying 226 particular kinds of opportunities. A well-designed foresight process is capable of analyzing a 227 system for current and emerging barriers to potential opportunities, monitoring a system for 228 traction opportunities, and mapping a path to realizing existing opportunities. We highlight 229 some foresight tools that are particularly well-suited to recognizing conservation 230 opportunities; however, we note that there are many other tools in the foresight tool-kit 231 that may be more relevant for some situations. 232 233 Potential opportunities 234 Recognizing potential opportunities involves first imagining possible futures, and then 235 identifying and prioritizing removal of the barriers preventing the most desirable outcomes. 236 Considering possible and probable future scenarios – as is done in scenario planning 237 (Peterson et al. 2003) – can be a useful way to identify the barriers associated with potential 238 opportunities that prevent them becoming existing opportunities (Knight et al. 2006). 239 Examining the properties of the system and how they vary under different scenarios can 9 240 reveal whether the same opportunities will be present across all or only some scenarios. 241 Consider these different scenarios: 1) catastrophic weather events generate public support 242 for addressing climate change, or 2) poor economic growth leads to polluting industries 243 being prioritized over environmental protection. The first scenario creates an opportunity 244 for action on climate change, while this is unlikely under the second scenario. ‘Landscape 245 futures’ is a tool that can identify opportunities that may only arise under some 246 circumstances (Bryan et al. 2011). It combines scenario planning with conservation planning, 247 and underpinned by spatial and other data sources, it has been used to inform landscape- 248 scale decisions by explicitly considering the impact of different policy options and assessing 249 where in the landscape opportunities may arise in the future (Bryan et al. 2011). 250 Where opportunities vary across scenarios it can be helpful to keep track of which scenario 251 is emerging by monitoring indicators of change. Indicators relevant to conservation 252 opportunity may include increases in extreme weather events and changes in public 253 attitudes (WSC & Bio-Era 2007). Tracking changes in these signposts can provide advanced 254 warning that a particular course of action may be necessary to avert an undesirable future. 255 Issue-centred scanning is an ideal tool for such a task. It can also be used to identify shifts in 256 systems that remove barriers preventing potential opportunities from becoming traction or 257 existing opportunities. 258 259 Traction opportunities 260 Recognizing traction opportunities relies on a sound understanding of a system and regular 261 monitoring; two things that foresight exercises can deliver. By scanning open source content 262 on the Internet (e.g., Twitter and other social media), scanning tools can be used to track 263 public opinion (Amanatidou et al. 2012) and predict how people will act (e.g., how they 264 might vote in an election or their intention to boycott a company). Up-to-date and 265 comprehensive surveillance of an issue through issue-centred scanning is particularly 266 important when the traction opportunity may only appear locally or for a short time (Moon 267 et al. this issue). For example, recognizing a shift in public opinion can create a temporary 268 opening to advance a conservation objective. This might include guiding companies towards 269 environmentally responsible practices, or seizing an opportunity to advance sustainable 270 industries through increased demand for ‘green’ products or services. 10 271 Increased discussion of conservation issues or number of people attending demonstrations 272 might also indicate a change in public attitudes, presenting an opportunity to make a policy 273 change. For example, the west coast of New Zealand quickly transitioned from a timber to a 274 tourism industry in 1999 in response to a rapid shift in public support for conservation 275 (Swarbrick 2012). Nature-based tourism continues to be a major industry, providing ongoing 276 opportunities to advance a conservation agenda. The foresight process provides all the 277 ingredients for addressing a case like this. First, a desirable future (moving towards a more 278 sustainable industry) can be agreed through visioning, a shift in public support can be 279 recognized through scanning, and the magnitude of barriers to this transition (loss of jobs 280 and income from the timber industry) could be explored through scenario planning. 281 282 Existing opportunities 283 Backcasting is particularly useful when an existing opportunity has been recognized to map 284 out a feasible multi-stage strategy for potentially complex implementation (Robinson 2003). 285 Manning et al. (2006) identified large-scale ecological restoration as an issue that could 286 benefit from backcasting. Restoration is complex and resource intensive over large areas, so 287 the scale of the problem can overwhelm decision-makers because they cannot visualize the 288 proposed changes. This has impeded large-scale restoration in the past, and backcasting 289 provides a method to deconstruct the problem into tractable steps that decision-makers can 290 implement. 291 Some conservation opportunities may already exist but are unknown or poorly understood. 292 Horizon scanning is capable of identifying existing opportunities not previously identified 293 (e.g., genetic control of invasive species; Sutherland et al. 2014). Opportunities may also 294 exist in other disciplines, or in new technologies that could benefit conservation research or 295 practice. Technology is revolutionizing invasive species monitoring and control methods. 296 Invasive predators can now be recognized from a paw print when the animal walks through 297 a tunnel-like structure. Detecting an unwanted individual triggers the instant delivery of a 298 fatal toxin and sends a signal to alert managers to the event (Provisional patent number: 299 615797; Helen Blackie personal communication). Likewise, the Internet has facilitated online 300 citizen science initiatives (e.g., www.zooniverse.org; CSA 2014), engaging the public in 301 science and sharing biological challenges with hundreds of thousands of Internet users. 11 302 Complex problems, such as refining the crystal structure of proteins that have long alluded 303 scientists have been solved leading to the design of new drugs to treat diseases (Schrope 304 2013). Scanning tools provide a method to detect these opportunities much sooner. 305 Given uncertain futures, we should favour actions that are likely to deliver the benefits of an 306 opportunity over the long-term (Schoemaker 1995). Scenario planning is useful for assessing 307 the flexibility of existing opportunities and the different strategies for realizing these 308 opportunities. The scenario planning process can consider any realistic period in the future 309 and the best strategy for realizing conservation opportunities can depend on whether the 310 goal is short-term or long-term gain. There may be positive conservation outcomes from 311 exploiting an existing opportunity now, but those benefits may not remain constant over 312 time and may not exist at all under some scenarios. For example, opportunities for large- 313 scale restoration may rely on acquiring land in the short-term because increases in land 314 values and land use change may put those areas out of reach in the future. The scenario 315 process provides a powerful way to explicitly consider uncertainty about the future and 316 factor it into current decisions. 317 318 319 Rising Waters case study: Using foresight to identify opportunities for climate change adaptation 320 In 2008, The Nature Conservancy (TNC) undertook a foresight exercise to consider how 321 communities within the Hudson River Estuary Watershed (HREW) in New York state, USA, 322 could adapt to the impacts of climate change (TNC 2009). Major changes have been 323 predicted for this area, which could have serious implications for the four million people 324 living within the HREW, and the forestry and agricultural industries present. The watershed 325 serves as a system with easily definable geographic and functional limits, providing a clear 326 scope for the exercise, along with a 20 year timeframe. The foresight process was designed 327 and facilitated by an experienced, professional futurist and included a diverse group of over 328 160 stakeholders from government, industry, emergency services, health care, local 329 communities and environmental groups. 330 The complexity of many conservation problems means that solutions may be multifaceted 331 (Arlettaz et al. 2010) and rely on the cooperation of a range of different stakeholders. 332 Participatory foresight processes such as this ensure a range of perspectives and different 12 333 dimensions of the problem are captured (Bengston et al. 2012) and can facilitate more 334 effective and lasting solutions by giving stakeholders ownership over the potential actions 335 developed (Iversen 2005). This level of stakeholder input into the process far exceeds 336 traditional planning approaches, providing a more detailed view of the social, economic and 337 political issues likely to define potential and traction opportunities. 338 The whole scenario planning process took 18 months and was divided into three broad 339 phases (learning, creating, and applying) designed around a series of workshops and 340 working group meetings (Fig. 2). While no formal scanning process was conducted, inputs 341 were collected through extensive literature reviews and included scientific predictions for 342 environmental changes in the region under the Intergovernmental Panel on Climate 343 Change’s predictions. This first phase also involved a workshop with a range of stakeholders 344 to discuss and supplement the information collected, identify important issues and analyse 345 signals (Fig. 2). In association with working groups, this process selected important existing 346 issues (e.g., climate change, aging infrastructure), drivers (e.g., land use decisions, oil prices), 347 actors (e.g., government, media), and key uncertainties (e.g., will adaptation be sensitive to 348 natural processes?). The issues were barriers that indicated the presence of potential 349 opportunities, while drivers highlighted factors that could lead to traction opportunities. The 350 careful consideration of the actors and uncertainties was critical to determining how to 351 convert potential opportunities to existing opportunities, and a step generally neglected in 352 traditional planning approaches. 353 In a second phase, four alternative scenarios were created and refined (Fig. 2). These 354 scenarios centred on the key uncertainties described above, varying trends in the important 355 drivers and the responses of actors. Scenarios were described using evocative titles (e.g., 356 procrastination blues) and illustrative details: government officials and the public do little to 357 prepare for climate change until extreme weather events cause severe local damage and 358 catalyse demands for action. The initial procrastination limits available response options. For 359 each scenario, indicators for the different drivers (e.g., price of key commodities) were 360 selected to act as signposts that could be monitored to indicate the trajectory of future 361 conditions. This step allows groups to be responsive to changes that indicate traction 362 opportunities. This adds a dynamic element to the planning process that is also not part of 363 traditional planning processes. 13 364 A third workshop was conducted to select actions and strategies for converting potential to 365 existing opportunities to achieve the most favourable outcomes across each scenario. 366 Working groups considered the feasibility of these actions in terms of the probable costs 367 and value of proposed solutions to consider which options were most robust to different 368 futures and highly implementable. Helping communities to develop emergency action plans 369 scored highly across all scenarios developed. Some actions that were most effective under 370 one scenario proved least effective under another. Considering how robust actions are to 371 possible future scenarios is a major advance on traditional planning approaches and 372 essential to developing strategies with a high probability of converting potential to existing 373 opportunities. 374 While the report developed detailed and appropriate actions, no measures of success were 375 created to determine whether the process actually changed behaviour. At the completion of 376 the Rising Waters project several regional working groups were developed. However, it is 377 unclear the extent to which the strategies developed on the basis of these scenarios were 378 implemented or the degree to which the exercise met its objectives. This is a criticism often 379 levelled at traditional planning approaches, where implementation and evaluation are rarely 380 built into the process. However, had the Rising Waters project followed all the steps in the 381 foresight process the project would not have been completed before the agreed actions 382 were implemented. To this end, including a backcasting exercise may have assisted in 383 providing a more detailed plan for action. This highlights the importance of completing all 384 the steps in the foresight process to achieve the best outcomes. 385 386 Discussion 387 Our review has largely focused on the potential benefits of foresight for recognizing 388 different types of conservation opportunity. The advantages of the foresight process include 389 a move away from reactive decision-making to a more proactive and responsive approach 390 to conservation planning. Despite these benefits being realized in other disciplines (e.g., 391 business, public health and biosecurity) and the growing use of foresight tools for 392 environmental management, to date, examples of strategic foresight actually influencing 393 conservation policy and action are rare. This is in part due to the relative infancy of 394 environmental applications of foresight, and the tendency for exercises to focus on the use 14 395 of a single tool rather than a comprehensive process. However, we speculate that the poor 396 uptake of foresight in conservation planning is also driven by short-term political cycles, 397 which leads to reactive decision-making with a focus on existing opportunities rather than 398 developing a more considered and longer-term plan to realize potential opportunities. The 399 foresight process fosters a more strategic approach but requires following a strategy from 400 conception through to implementation. 401 While growing in profile, the foresight process is largely unfamiliar to conservation planning, 402 and previous foresight applications in conservation have been so broad that they may 403 become too abstract and divorced from fine-scale decision-making. For example, the 404 ‘Millennium Ecosystem Assessment’ suggested significant changes to policies, institutions, 405 and practices, but lacked a clear plan to achieve the necessary changes at policy-relevant 406 scales (Tallis & Kareiva 2006). Widespread adoption of strategic foresight in conservation is 407 unlikely until some tractable examples of its successful application become more widely 408 known. However, there are very few publicly available examples of foresight exercises that 409 employ all the steps in the foresight process, as illustrated by the Rising Waters case study 410 presented above. Often key steps are neglected and it is challenging or impossible to assess 411 the outcomes of the exercises, which would require clear measures of success to be 412 articulated. For example, scanning applications for disease risk can measure success in 413 terms of preventing disease in a particular country, with the associated environmental 414 benefits and financial savings to industry (Lyon et al. 2013). At least in the short-term, using 415 strategic foresight to recognize conservation opportunities may require engaging specialists 416 in strategic foresight that can guide and focus the process to ensure all the steps are 417 conducted and the potential benefits are realized. 418 Documenting successful examples of foresight processes that realize conservation 419 opportunity will make the approach more appealing to decision-makers and illustrate the 420 advantages over more traditional planning approaches. We encourage conservation 421 scientists and decision-makers, in conjunction with specialist facilitators, to roadtest and 422 refine the foresight process, with particular emphasis on implementation. 423 Strategic foresight is well-suited to identifying conservation opportunities but has been 424 underutilized in conservation relative to other disciplines (Cook et al. in press). While there 15 425 is increasing recognition that forward looking approaches are needed in conservation to 426 recognize emerging issues (e.g., horizon scanning) and consider a how the future might 427 influence the choices we make in the present (e.g., scenario planning), generally these tools 428 are used in isolation rather than as part of a foresight process. The stages of the foresight 429 process, from setting the scope to taking action, have direct parallels with the steps for 430 recognizing and realizing conservation opportunity (Moon et al. this issue). The foresight 431 tool-kit offers many tools to structure and guide the process of seeking opportunity. This 432 approach has been used successfully for many years in other disciplines and will add value 433 to our attempts to create a more desirable future for global biodiversity. 434 435 Cited Literature 436 Amanatidou, E., M. Butter, V. Carabias, T. Könnölä, M. Leis, et al. 2012. 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Large-scale management experiments and learning by doing. Ecology 71:2060-2068. Wildlife Conservation Society (WCS), and Bio-Era. 2007. Futures of the wild. A project of the Wildlife Conservation Society’s Futures Group. Wildlife Conservation Society and Bio-Era, New York. 527 19 Table 1. Some of the many strategic foresight tools available to structure a foresight exercise. Some tools can be used in more than one step depending on the purpose of the exercise. (Adapted from Cook et al. in press) Steps Setting the scope Collecting inputs Analyzing signals Interpreting information Determining how to act Implementing the outcomes Issues trees: used to identify the key elements of an issue that need to be considered (HSC 2014) Horizon scanning: used to collect and organize a wide array of information to identify emerging issues (Glenn & Gordon 2009) Driver analysis: a process to identify and group trends, determine the drivers of these trends, and the relationships between drivers (HSC 2014) Scenario planning: a tool to explore alternative visions of the future based on key uncertainties and trends (Peterson et al. 2003) Backcasting: used to visualize barriers to achieving a goal and the steps needed to overcome those obstacles (Dreborg 1996) Action research: an iterative process for improving action designed around planning, acting, learning and reflecting (McNiff & Whitehead 2003) Stakeholder analysis: a process to identify stakeholders with an interest in an issue (Reed et al. 2009) Literature review: summary of relevant published information Statistical modelling and analysis: using mathematical concepts to describe a system, study the effects of different components, and make predictions about system behavior and the effects of alternative actions (Glenn & Gordon 2009) Causal layered analysis: a tool to expose hidden assumptions and help create a new narrative to promote a desired change (Glenn & Gordon 2009) Roadmaps: for identifying the actions required to overcome any barriers (HSC 2014) Adaptive management: a process for learning about the effectiveness of management by monitoring outcomes (Walters & Holling 1990) System maps: conceptual representation of a system, with a set of elements and the relationships between Workshops: assembles expert to identify the most significant emerging issues via an iterative scoring process (Sutherland et Trend impact analysis: projection based on past trends to infer the consequences of similar or different trajectories in key Visioning: Participants describe the ideal scenario in detail. They share and refine the vision, often exploring barriers and key actors, Decision modelling: alternatives are scored against multiple, weighted criteria or objectives to determine which Change management: an approach to transitioning individuals or groups to a desired state (Andrews et al. 2008). 20 them (HSC 2014) al. 2011) variables (Glenn & Gordon 2009) the resources required and the steps involved in achieving the vision (Glenn & Gordon 2009) alternative performs best across all objectives (Glenn & Gordon 2009) Cross impact analysis: structures thinking about how one event impacts the likelihood of other events. Probabilities are assigned subjectively or are underpinned by mathematical relationships. (Glenn & Gordon 2009) Futures wheel: a structure brainstorming tool exploring the primary, secondary and tertiary impacts of a trend or event (Glenn & Gordon 2009) Risk analysis: a process for assessing and dealing with hazards (Burgman 2001) 21 Figure captions: Figure 1. The stages of the strategic foresight process and some of the many tools that can be used to assist at each stage. Definitions of each of these tools can be found in Table 1. 22 Figure 2. The three phases of the Rising Waters foresight project (learning, creating and applying) and the different steps in this process, centred around a series of workshops with stakeholders (W1, W2, W3), smaller working group meetings and scenario team meeting (T1, T2, T3, T4), which further developed and analysed the issues that emerged from the workshops with stakeholders. 23