Ex situ conservation of the Bengal florican 907
TABLE 1 Step 3: evaluation of biological and practical considerations associated with ex situ conservation of the Bengal florican Houbaropsis bengalensis blandini.
Considerations
Required number of founders
Number of individuals to be maintained ex situ
Likely duration of ex situ programme
Relative risk of behavioural adaptation to ex situ conditions
Inbreeding Disease management
Plans for a release/ reintroduction
Egg harvest method
Geographical location of facility
Nature of facility Design of facility Equipment Staff numbers & skills Desired state1 Likely state1
Harvest 5–10 eggs per year for at least 5 years Harvest as many eggs as possible from doomed popula- tions; harvest eggs only from July onwards from popu- lations with a hope of persistence
.20 breeding age females, more if possible
.50 years: under above-average scenario minimum of 30 years needed until ex situ population is established
Moderate, managed through handling protocols & cage design
Moderate, managed through maximizing the number of founders, genetic testing of all indivi- duals&planned mating through use of a studbook
Single species facility with stringent quarantine procedures
Only at such a time that it does not jeopardize the captive population
Close supervision of search teams by ACCB & WCS staff
Proximate to native range (cannot locate inside breeding range because of seasonal flooding) Single species
Large enclosures with ample space for flying replicate wild conditions
State of the art Dedicated Bengal florican staff team
Marking of individuals Colour rings & microchips on all birds, database (Species360, 2020) & stud book kept up to date
Behavioural management Birds handled as infrequently as possible Level of public display
Birds not on public display
58–85% chance that this can be achieved over 50 years under above-average scenario, depending on number of eggs harvested annually
58% chance that this can be achieved under above- average scenario if 5 eggs harvested per year
High; behavioural adaptation to captivity is initially de- sirable to minimize adult mortality; birds bred for release will be managed differently, to minimize adaptation Moderate, managed as in the desired state
Captive facility only keeps species that originate from Cambodia, standard quarantine & disease risk reduction procedures are in place
Unlikely to be possible before 2050, for which it is impossible to predict suitability of wild conditions
Local people asked to report nests to WCS, eggs harvested from nests by ACCB staff Proximate to native range
Multi-species, located at ACCB, an animal rescue, rehabilitation & captive breeding centre managed by Allwetterzoo Münster, Germany
Small enclosures, breeding & non-breeding birds kept separately, birds not encouraged to fly for fear of injury; priority given to minimizing mortality
All necessary equipment, & backup equipment, has been purchased & is ready to use
Dedicated bird keeper & veterinarian, florican staff will not work on husbandry of other bird species, to minimize disease risk
As desired state
Birds for captive breeding will be habituated as chicks, to facilitate easy handling & reduce mortality
Birds not on public display, all visitors to the facility will be escorted by staff
1ACCB, Angkor Centre for Conservation of Biodiversity; WCS, Wildlife Conservation Society.
logistical risks (Step 4: Table 2) were populated in advance with issues for consideration, using IUCN/SSC (2014). Participants were also invited to identify additional issues, which were then added to the tables. The whole group as- sessed the biological risks associated with ex situ manage- ment, using the decision tree (Steps 4 and 5) for the population as a whole, and for each of the four remaining subpopulations. Results were summarized by the facilitator. A basic plan for ex situ management was developed based on the outcome and outputs of the meeting (Step 5: Table 3).
Results
Using the decision tree, the group decided to proceed with ex situ management of the Bengal florican, despite the risks, because of rapid, and potentially accelerating, declines in the wild population, the likelihood that threats could not be controlled in the wild before the taxon was rendered extinct, and the relatively high probability of establishing a captive population (Fig. 1). The demographic modelling indicated there is a 58% probability of a captive population persisting for 50 years under the above-average scenario of egg harvest
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
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