A census of the Critically Endangered Bengal Florican Houbaropsis bengalensis was conducted between March and May 2012 on and surrounding the Tonle Sap floodplain in Cambodia, which supports the last extant population of the Indochinese subspecies blandini. We found a decline in the number of displaying males of 44–64% since a comparable estimate from the same sites in 2005 to 2007. The estimated population, including five individuals at one previously unsurveyed site, is now 216 (95% CI 156–275) displaying males, plus potential non-displaying males and an unknown number of females. If numbers continue to be lost at a similar rate, it is possible that blandini would become extinct within 10 years. Although the population faces multiple threats, this critical situation has primarily been caused by the recent, rapid conversion of the florican’s grassland habitat to intensive, industrial-scale, irrigated rice cultivation. To protect the Bengal Florican from extinction in South East Asia, existing Bengal Florican Conservation Areas (BFCAs) need expansion and improvements, including strengthened legal status by prime ministerial sub-decree and better demarcation, patrolling and management. As priorities, both irrigated rice and scrub encroachment within the BFCAs needs to be reversed, local communities better supported, and land outside the BFCAs monitored and strategically managed for florican conservation. Where possible, further BFCAs need to be established. Land purchase may also be an effective conservation measure; leasing land earmarked for cultivation would be cheaper, but less secure
SummaryIn 2013 a prediction was made that the South-East Asian subspecies of Bengal Florican Houbaropsis bengalensis blandini would be extinct within 10 years. In 2018 we conducted a survey in the Tonle Sap floodplain, Cambodia, of the last population of Bengal Florican in South-East Asia. We found that the rate of decline in displaying males was 55% over five years, a decline comparable to that recorded between 2005–2007 and 2012. The estimated number of displaying males in 2018 was 104 (95% CI: 89–117), down from 216 (156–275) in 2012. We also conducted surveys by flushing birds in the non-breeding season, which indicated that the sex ratio of males to females is 3:1. We therefore estimate that the total population of adult Bengal Floricans in Cambodia in 2018 was 138 (119–156), making H. b. blandini the most threatened bustard taxon. The number of sites that support displaying male Bengal Floricans was reduced from 10 to four between 2012 and 2018. Between 2012 and 2018 we monitored numbers of displaying males in most years at the sites that support 80% of the total population. The only site where numbers of birds are stable is Stoung-Chikraeng Bengal Florican Conservation Area, where there were 44 (25–63) displaying males in 2018. This is the only site that has an ongoing NGO-government conservation programme. Our data indicate that Bengal Floricans are lost from sites when the area of grassland falls below 25 km2. We found evidence that displaying male Bengal Floricans abandon display territories when grassland is lost, this also creates hope that they may disperse and could colonise newly created habitat. All remaining sites that support Bengal Floricans in Cambodia are imperilled and we outline what must be done to reduce the possibility that H. b. blandini will be extinct by 2023.
We used information derived from expert elicitation to measure progress in conservation of the Bengal Florican (Houbaropsis bengalensis) by calculating six metrics, namely: (a) current threat impact, (b) research need, (c) research achievement, (d) management need, (e) management achievement, and (f) percentage threat reduction. We then used the metrics to identify priority threats, namely predation by dogs, hunting, power lines, and vegetation changes caused by human activities. The metrics indicate that although there has been little progress in addressing predation and power lines, reductions in hunting have been achieved and practitioners have a good understanding of how to ameliorate vegetation changes. We assessed conservation needs across all sites that support Bengal Florican, and highlight conservation achievements at Stoung‐Chikreang Bengal Florican Conservation Area (BFCA), Manas National Park and Kaziranga National Park. We used our results to develop a framework for prioritizing collaboration on tackling priority threats. We highlight D'Ering Wildlife Sanctuary in India as one of the highest priority sites for Bengal Florican conservation, and propose that conservation in Stoung‐Chikreang Bengal Florican Conservation Area (BFCA), Manas National Park and Kaziranga National Park must be continued, scaled‐up and good‐practice replicated at Koklabari, Baray BFCA and Koshi Tappu Wildlife Reserve. If these plans are followed, then we believe that priority threats can be adequately addressed and the extinction of Bengal Florican can be prevented.
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