IUCN captive management guidelines support ex situ conservation of the Bengal florican Houbaropsis bengalensis blandini
S IMO N P. MAHOOD,CHAMNAN HONG,MIC HAEL MEY E RHOF F,PAU P. F ERR ANDO PHEARUN SUM,VIRAK SON,PENGANN OUCH and STEPHEN T. GAR N E T T
Abstract Ex situ conservation of species is risky and expen- sive, but it can prevent extinction when in situ conservation fails. We used the IUCN Guidelines on the Use of Ex Situ Management for Species Conservation to evaluate whether to begin ex situ conservation for the South-east Asian sub- species of Bengal florican Houbaropsis bengalensis blandini, which is predicted to be extinct in the wild within 5 years. To inform our decision, we developed a decision tree, and used a demographic model to evaluate the probability of estab- lishing a captive population under a range of husbandry scenarios and egg harvest regimes, and compared this with the probability of the wild population persisting. The model showed that if ex situ conservation draws on inter- national best practice in bustard husbandry there is a high probability of establishing a captive population, but the wild population is unlikely to persist. We identified and evaluated the practical risks associated with ex situ con- servation, and documented our plans to mitigate them. Modelling shows that it is unlikely that birds could be re- leased within 20–30 years, by which time genetic, morpho- logical and behavioural changes in the captive population, combined with habitat loss and extinction of the wild population, make it unlikely that Bengal florican could be released into a situation approximating their current wild state. We considered the philosophical and practical impli- cations through a decision tree so that our decision to begin ex situ management is not held back by our preconceived notions of what it means to be wild.
SIMON
P.MAHOOD* (Corresponding author,
orcid.org/0000-0001-9459-1064)
and STEPHEN T. GARNETT (
orcid.org/0000-0002-0724-7060) Research Institute for the Environment and Livelihoods, Charles Darwin University, Ellengowan Drive, Casuarina, Northern Territory 0810, Australia E-mail
simonpeter.mahood@
cdu.edu.au
CHAMNAN HONG* and VIRAK SON* Department of Freshwater Wetland Conservation, Ministry of Environment, Phnom Penh, Cambodia
MICHAEL MEYERHOFF and PAU P. FERRANDO Angkor Centre for Conservation of Biodiversity, Kbal Spean, Cambodia
PHEARUN SUM Wildlife Conservation Society, Phnom Penh, Cambodia
PENGANN OUCH Department of Wildlife and Biodiversity, Forestry Administration, Ministry of Agriculture, Forestry and Fisheries, Phnom Penh, Cambodia
*Also at: Wildlife Conservation Society, Phnom Penh, Cambodia
Received 20 May 2019. Revision requested 9 September 2019. Accepted 21 December 2019. First published online 26 March 2021.
Keywords Bengal florican, bustard, captive management, decision tree, demographic modelling, ex situ conservation, extinction, IUCN guidelines
Supplementary material for this article is available at
doi.org/10.1017/S0030605319001510
Introduction
2011), with 34 animals and 35 plants categorized as Extinct in the Wild and thus relying entirely on persistence of pop- ulations in captivity (IUCN, 2019). Successful case studies include the California condor Gymnogyps californianus in the Americas (Snyder & Snyder, 2000) and crested ibis Nipponia nippon in Asia (Xi et al., 2002). The hope that these examples engender, coupled with the dire situation facing an increasing number of species in the wild (Butchart et al., 2010), manifests in recommendations for captive breeding in the IUCN Red List accounts of 2,199 threatened or Near Threatened species (IUCN Conservation Planning Specialist Group, 2019). However, zoos can conserve only a small proportion of threatened species (Balmford et al., 1996), and the familiarity of successful case studies masks the fact that ex situ management is difficult, risky, time-consuming and financially costly, and can increase the risk of extinction forwild populations by removing individuals fromthe wild to create founder populations (Snyder et al., 1996). A compre- hensive global evaluation of conservation reintroduction, reinforcement or replacement case studies found that 72% of those with a known outcome succeeded and 28% failed; not eliminating the cause of decline was the greatest cause of failure (Bubac et al., 2019). Faced with data that indicate a rapidly declining population, conservation managers must make a timely, informed decision regarding whether or not to proceed with ex situ management (McGowan et al., 2017). A failure to act quickly on available evidence of spe- cies declines can lead to extinctions (Martin et al., 2012), but making the wrong decision can also increase the risk of extinction (Snyder et al., 1996). Management of species occurs along a continuum of
E
states ranging from free-ranging self-sustaining wild popu- lations to species that exist only in captivity (Redford et al.,
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (
http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited. Oryx, 2021, 55(6), 903–915 © The Author(s), 2021. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605319001510
x situ management is increasingly used to prevent species extinctions (Seddon et al., 2007; Redford et al.,
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 |
Page 149 |
Page 150 |
Page 151 |
Page 152 |
Page 153 |
Page 154 |
Page 155 |
Page 156 |
Page 157 |
Page 158 |
Page 159 |
Page 160 |
Page 161 |
Page 162 |
Page 163 |
Page 164