Shifted baselines and the policy placebo effect in conservation
SAMANTHA LOVE L L,AYA N A E LIZABETH JOHNSON ROB IN RAMDEEN and LOREN MCCLENACHAN
Abstract Coastal ecosystems have been degraded by human activity over centuries, with loss of memory about past states resulting in shifted baselines. More recently conservation ef- forts have resulted in localized recoveries of species and eco- systems. Given the dynamism of ecosystem degradation and recovery, understanding how communities perceive long- term and recent changes is important for developing and implementing conservation measures. We interviewed stakeholders on three Caribbean islands and identified a shifted baseline with respect to the extent and degree of long-term declines in marine animal populations; stake- holders with more experience identifiedmore species as de- pleted and key species as less abundant than those with less experience. Notably, the average respondent with,15 years of experience listed no species as depleted despite clear evi- dence of declines. We also identified a phenomenon we call the policy placebo effect, in which interviewees perceived some animal populations as recently recovering following passage of new conservation legislation but in the absence of evidence for actual recovery. Although shifted baselines have a negative effect on conservation as they can lower recovery goals, the outcomes of a policy placebo effect are unclear. If the public prematurely perceives recovery, motivation for continued conservation could decline. Alternatively, perception of rapid success could lead com- munities to set more ambitious conservation goals.
Keywords Historical ecology, local ecological knowledge, marine conservation, marine protected areas, policy pla- cebo, recovery, shifting baselines
Supplementary material for this article is available at
https://doi.org/10.1017/S0030605318000169
Introduction I
nformation on long-term change is important for conser- vation andmanagement, particularly in coastal ecosystems,
SAMANTHA LOVELL* and LOREN McCLENACHAN (Corresponding author) Environmental Studies Program, Colby College, 5351 Mayflower Hill Drive, Waterville, Maine, USA. E-mail
lemcclen@colby.edu
AYANA ELIZABETH JOHNSON, Ocean Collective, Brooklyn, New York, USA ROBIN RAMDEEN,Waitt Institute, Montserrat, West Indies *Also at: Environmental Defense Fund, Washington, DC, USA
whose history of degradation can be obscured by a lack of ecological data from the past (Jackson et al., 2001). Failure to document past change can lead to the shifting baseline syndrome, in which knowledge of past ecosystem produc- tivity is lost over the course of generations (Pauly, 1995). Shifted baselines have been documented among marine resource users; for example, in both Mexico and Brazil older fishers named more fish species and fishing sites as depleted than younger fishers (Sáenz-Arroyo et al., 2005; Giglio et al., 2015). In Curaçao and Bonaire (Netherlands), fishers’ baselines were not shifted because stories of plentiful past catches were passed down within these communities, whereas scuba divers had unrealis- tically positive perceptions of the health of the reefs and fish populations because they lacked this information (Johnson & Jackson, 2015). Such shifted baselines have im- plications for conservation, as they may lead to reduced restoration targets for exploited species (McClenachan et al., 2012, 2018). Change in Caribbean marine ecosystems has been docu-
mented over century-long time scales, with historical losses of large vertebrates fundamentally altering trophic dynamics (McClenachan et al., 2006; McClenachan & Cooper, 2008), losses of herbivorous fishes such as parrotfish (Scarus spp.) contributing to declines in reef accretion rates (Cramer et al., 2017), and reductions in the spatial distribution of coral reef habitats (McClenachan et al., 2017). In recent decades, the three-dimensional structure of Caribbean reefs has been re- duced (Alvarez-Filip et al., 2009), and hard coral cover de- clined on average by 50% between the 1970s and early 2000s, with shifts to non-framework building species (Jackson et al., 2014). Together with ongoing overfishing, these changes have led to declines in the density of both exploited and unexploited reef fishes (Paddack et al., 2009). A phase shift from coral to algal dominance was triggered and maintained by a combination of a disease in the sea urchin Diadema antillarum in the early 1980s, overexploitation of parrotfish and other algal grazers (Jackson et al., 2014), and land-based pollution (Cramer et al., 2012, 2015). More recently, climate change, disease, and invasive species have added additional stresses (Hoegh-Guldberg et al., 2007;Green et al., 2012;Randall &van Woesik, 2015). Despite these longer-term declines in Caribbean marine
Received 2 August 2017. Revision requested 20 October 2017. Accepted 18 January 2018. First published online 18 October 2018. Oryx, 2020, 54(3), 383–391 © 2018 Fauna & Flora International doi:10.1017/S0030605318000169
ecosystems, some recent conservation efforts have been suc- cessful, and localized recoveries of marine species and eco- systems are occurring. Although Caribbean green turtle
Page 1 |
Page 2 |
Page 3 |
Page 4 |
Page 5 |
Page 6 |
Page 7 |
Page 8 |
Page 9 |
Page 10 |
Page 11 |
Page 12 |
Page 13 |
Page 14 |
Page 15 |
Page 16 |
Page 17 |
Page 18 |
Page 19 |
Page 20 |
Page 21 |
Page 22 |
Page 23 |
Page 24 |
Page 25 |
Page 26 |
Page 27 |
Page 28 |
Page 29 |
Page 30 |
Page 31 |
Page 32 |
Page 33 |
Page 34 |
Page 35 |
Page 36 |
Page 37 |
Page 38 |
Page 39 |
Page 40 |
Page 41 |
Page 42 |
Page 43 |
Page 44 |
Page 45 |
Page 46 |
Page 47 |
Page 48 |
Page 49 |
Page 50 |
Page 51 |
Page 52 |
Page 53 |
Page 54 |
Page 55 |
Page 56 |
Page 57 |
Page 58 |
Page 59 |
Page 60 |
Page 61 |
Page 62 |
Page 63 |
Page 64 |
Page 65 |
Page 66 |
Page 67 |
Page 68 |
Page 69 |
Page 70 |
Page 71 |
Page 72 |
Page 73 |
Page 74 |
Page 75 |
Page 76 |
Page 77 |
Page 78 |
Page 79 |
Page 80 |
Page 81 |
Page 82 |
Page 83 |
Page 84 |
Page 85 |
Page 86 |
Page 87 |
Page 88 |
Page 89 |
Page 90 |
Page 91 |
Page 92 |
Page 93 |
Page 94 |
Page 95 |
Page 96 |
Page 97 |
Page 98 |
Page 99 |
Page 100 |
Page 101 |
Page 102 |
Page 103 |
Page 104 |
Page 105 |
Page 106 |
Page 107 |
Page 108 |
Page 109 |
Page 110 |
Page 111 |
Page 112 |
Page 113 |
Page 114 |
Page 115 |
Page 116 |
Page 117 |
Page 118 |
Page 119 |
Page 120 |
Page 121 |
Page 122 |
Page 123 |
Page 124 |
Page 125 |
Page 126 |
Page 127 |
Page 128 |
Page 129 |
Page 130 |
Page 131 |
Page 132 |
Page 133 |
Page 134 |
Page 135 |
Page 136 |
Page 137 |
Page 138 |
Page 139 |
Page 140 |
Page 141 |
Page 142 |
Page 143 |
Page 144 |
Page 145 |
Page 146 |
Page 147 |
Page 148