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            "note": "<p xmlns=\"http://www.w3.org/1999/xhtml\" id=\"title\"><strong>Contents</strong></p><ul xmlns=\"http://www.w3.org/1999/xhtml\" style=\"list-style-type: none; padding-left:0px\" id=\"toc\"><li><a href=\"zotero://open-pdf/541250_A28UV4J2/1\">Introduction</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/3\">Materials and Methods</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/3\">Field Data Collection</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Ethical Note</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Data Analysis</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Proportions of Time Spent in All-Male and Mixed-Sex Groups and Their Relationship With Male Age</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Changes in Male Associations and Time to Sighting Independence</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Effect of Male Age and the Presence or Absence of Females on Male Association Patterns</a><ul style=\"list-style-type: none; padding-left:36px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/4\">Older males as preferred associates</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/5\">Age-peer associations among males</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/5\">Male Associations in the Presence and Absence of Females</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/6\">Restriction on All-Male Group Size</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/6\">Preferred Male Associations and Stability of Associations</a></li></ul></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/6\">Results</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/6\">Proportions of Time Spent in All-Male and Mixed-Sex Groups and Their Relationship With Male Age</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/6\">Effect of Male Age and the Presence or Absence of Females on Male Association Patterns</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/7\">Older Males as Preferred Associates</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/7\">Age-Peer Associations Among Males</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/8\">Male Associations in the Presence and Absence of Females</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/9\">Restriction on All-Male Group Size</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/9\">Preferred Male Associations and Stability of Associations</a></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/9\">Discussion</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/10\">Proportions of Time Spent in All-Male and Mixed-Sex Groups and Their Relationship With Male Age</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/10\">Effect of Male Age on Association Patterns: Reasons for Adult Male Associations</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/12\">Male Associations in the Presence and Absence of Females</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/12\">Restriction on All-Male Group Size</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/13\">Preferred Male Associations and Stability of Associations</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/13\">Conclusion</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Data Availability Statement</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Ethics Statement</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Author Contributions</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Funding</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Acknowledgments</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">Supplementary Material</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_A28UV4J2/14\">References</a></li></ul>",
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            "note": "<p xmlns=\"http://www.w3.org/1999/xhtml\" id=\"title\"><strong>Contents</strong></p><ul xmlns=\"http://www.w3.org/1999/xhtml\" style=\"list-style-type: none; padding-left:0px\" id=\"toc\"><li><a href=\"zotero://open-pdf/541250_VZUMSXHK/5\">INTRODUCTION</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/5\">Two back-to-back Asian Elephant conservation planning workshops</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/6\">Range-wide Mapping Workshop Goals and Objectives</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/6\">Goals</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/6\">Main objectives</a></li></ul></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">CURRENT PROJECT STATUS</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">Project Objective 1: To develop a synthetic, spatially explicit summary of the status and distribution of the species across its historical range</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">Project Objective 2: To establish biological conservation priorities for the species in all the major, ecologically distinct settings in which it occurs</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">Project Objective 3. To arrive at those priorities through a consensual process involving all the major current data holders and active conservation agencies/groups working on the species</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">Please note that the three inter-linked objectives listed above are considered together in the report that follows.</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">Activities undertaken, results achieved, and products generated</a><ul style=\"list-style-type: none; padding-left:36px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/7\">The workshop process</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/8\">Threats analysis</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/9\">Developing a synthetic spatially explicit biological vision for saving Asian Elephants</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/10\">Turning the biological vision into operation goals: identifying a core set of populations needed to save Asian Elephants across the species’ range</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/12\">The status of Asian Elephants</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/13\">Why elephant surveys and monitoring programs are needed</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/14\">Survey priorities identified as a result of the range-wide analysis described in this report</a></li></ul></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/41\">Project Objective 4: To identify priority actions and to seek to identify organizations and individuals who can implement high priority projects</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/41\">Activities undertaken, results achieved, and products generated</a><ul style=\"list-style-type: none; padding-left:36px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/41\">Development of Conservation Objectives</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/42\">Development of Objectives Targets and Actions</a></li></ul></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/50\">Project Objective 5: To generate funds</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/50\">Activities undertaken, results achieved, and products generated</a></li></ul></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/50\">ASSESSMENT OF THE PROJECT’S IMPACT</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/50\">COOPERATION AND COLLABORATION</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/50\">EQUIPMENT PURCHASED</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/51\">LITERATURE CITED</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/53\">ANNEX 1: RANGE CATEGORIES AND EVIDENCE CODES</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/55\">ANNEX 2: SURVEY METHOD CODES</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/56\">ANNEX 3: LAND TENURE DEFINITIONS</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/57\">ANNEX 4: FORM A – POINT LOCATIONS FOR WILD ASIAN ELEPHANT OBSERVATIONS</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/58\">ANNEX 5: FORM B – WILD ASIAN ELEPHANT POPULATIONS AREA-BASED (POLYGON) DATA SHEET</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/59\">ANNEX 6: LIST OF PARTICIPANTS</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/64\">ANNEX 7: AGENDA RANGE-WIDE MAPPING AND STRATEGIC CONSERVATION PLANNING WORKSHOPS FOR ASIAN ELEPHANTS, PHNOM PENH, 20–24TH OCTOBER 2008</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_VZUMSXHK/69\">ANNEX 8: OCTOBER 2008 ASIAN ELEPHANT WORKSHOPS DATA SHARING/DATA-USE AGREEMENT</a></li></ul>",
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            "title": "Range-wide mapping workshop for Asian elephants (Elephas maximus), Cambodia, October 2008",
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                    "firstName": "Simon",
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            "abstractNote": "Two back-to-back Asian Elephant conservation workshops were held in Phnom Penh, Cambodia, October 20–24th, 2008. The first workshop, which was coordinated by WCS and funded by WCS and the USFWS/AsECF, is the subject of this report and focused on a range- wide status review and population assessment, during which all Asian Elephant populations were mapped and a core (or high priority) set of populations for conservation action was identified using primarily biological criteria. The second workshop, which was coordinated by the IUCN/SSC Asian Elephant Specialist Group (AsESG) (and funded by the AsESG, WWF/AREAS, and WCS) took these “where to save the species” data and used them to inform a conservation strategy for Asian Elephants throughout their range (i.e. “how to save the species”). The process used at both workshops was designed to be fully participatory and representatives from all 13 Asian Elephant range States attended the workshops, as did other elephant conservationists from outside these States.\nDuring the first workshop, the participants reviewed the existing maps and data, mapped and characterized known populations of Asian Elephants, as well as areas that may sustain populations but where recent survey data are lacking. During the mapping process the elephant’s range was categorized into Confirmed, Possible, and Recoverable areas (polygons). The participants also identified land which may act as linkages between known populations, and areas where the species might be restored in future. Finally, the participants selected a core set of elephant populations based on biological criteria that would meet a largely biological definition of what it will take to “save Asian Elephants” (see “Developing a synthetic spatially explicit biological vision for saving Asian Elephants” below).\nThe workshop participants agreed that the following values should inform a 100-year Asia-wide vision for Asian Elephant conservation: representation across ecological and genetic “settings”; resiliency and functionality; replication to avoid catastrophic loss; and human needs and aspirations. In discussions about how to turn the agreed vision components (i.e. the “values” listed above) into an operational version of the Vision, a key point was the question of how to best incorporate replication across the different habitat types (ecological “settings”) occupied by Asian Elephants. The participants agreed to use the WWF Global 200 Ecoregions/Biomes as a practical classification of habitat types. The workshop participants also agreed to recognize three subspecies: the Asian mainland plus Sri Lanka (Elephas maximus indicus), Sumatra (E. m. sumatranus), and Borneo (E. m. subsp.), notwithstanding the doubts expressed recently by Cranbrook et al. about the origin of the putative Bornean subspecies.\nThe data compiled during the first of the two back-to-back workshops was used to identify which elephant population populations would be selected if the following rules were adopted:\n Include at least 1 population in every range State (a political, not biological value);\n Include all subspecies;\n Include all populations known or suspected to contain >100 elephants per Global 200\nEcoregion/Biome (or include the 2 largest populations if none >100);\n Include at least 2 populations per Global 200 Ecoregion/Biome;\n Include all Confirmed Range polygons that are contiguous to the polygons selected using\nthe above rules.\n3\nUsing these rules the elephant populations listed in Table 1 and shown in Figures 1–8 were identified. In summary, the rules (which are an attempt to help define what the Vision Statement means in practical operational terms) give a set of populations that:\n Encompass 53 populations (Table 1);\n Represent 50.3% of the current Confirmed, Possible, and Recoverable range of Asian\nElephants (Table 2);\n Represent (very) approximately 75% of the global population of Asian Elephants;\n Represent 22 different ecological settings (Global 200 Ecoregions/“Biomes”), which are\nall those currently occupied by Asian Elephants (Figure 2; Table 2);\n Include – by definition – all 13 Range States and all three subspecies (Sumatra, Borneo,\nand mainland Asia + Sri Lanka; Table 3).\nThese populations can be thought of as a core, or minimum, set of populations that will need to be conserved if we are to be able to say that we have fulfilled the biological components of the Vision Statement.\nThe data compiled at the workshop and the subsequent analyses paint a rather dire picture of the status of Asian Elephants. The 878,639 km2 that represents the sum of all the Confirmed, Possible, and Recoverable range polygons combined represents only 10.2% of the 8,613,003 km2 historical range for the species. Thus almost 90% of the species’ historical range has been lost. Only 29.1% of the entire range (Confirmed, Possible, and Recoverable categories) is within protected areas (PAs) as defined by IUCN (Table 4).\nIn earlier work, Sukumar estimated the minimum viable area for long-term conservation of an elephant population (defined as 500 breeding individuals, a 1:5 male:female sex ratio, and a density of 0.5 elephants/km2) to be 4,400 km2. Notwithstanding the acknowledged difficulties of estimating minimum viable population areas, only 20 of the 53 core populations identified during the workshop have areas larger than this minimum and 7 of these are transnational populations (which brings both opportunities and challenges for management; Table 5).\nIn terms of elephant numbers, with a small number exceptions discussed in the report, all we really know about the status of Asian Elephants is the location of some (probably most) populations. The conservation community still has very little idea about the size (and almost no formal measure of the trend) of most elephant populations, including the great majority of the core populations identified during the October 2008 workshop. Thus the oft-repeated global population ‘estimate’ of about 30,000 to 40,000 or 50,000 Asian Elephants is in reality no more than a crude guess, which has been accepted more or less unchanged for a quarter of a century despite major loss of elephant habitat over this period. Indeed, for a large part of the species’ range we do not even know where the populations are, or indeed if they are still extant, and this is clearly shown by the large areas of Possible Range identified during the workshop. This problem is most acute in the following ecological settings (“Biomes”): Kayah-Karen/Tenasserim moist forests; Naga-Manapuri-Chin Hills moist forests; North Indochina subtropical moist forests; Tropical & Subtropical Moist Forests; Tropical Moist Deciduous & Semi-Evergreen Forests; and in the following Range States, Myanmar, Bangladesh, and Cambodia. All these areas are therefore priorities for surveys. In addition, another high priority is to assess through surveys whether those areas of Possible Range and Recoverable Range apparently forming links between Confirmed Range polygons do in fact still constitute elephant habitat because if they do they will help reduce the fragmented nature of much of the species’ range (especially that in Thailand and Indochina).",
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            "note": "<p xmlns=\"http://www.w3.org/1999/xhtml\" id=\"title\"><strong>Contents</strong></p><ul xmlns=\"http://www.w3.org/1999/xhtml\" style=\"list-style-type: none; padding-left:0px\" id=\"toc\"><li><a href=\"zotero://open-pdf/541250_MFK9LDZ6/1\">Abstract</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/1\">Background</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/1\">Results</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/1\">Conclusions</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/1\">Background</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/3\">Methods</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/3\">Study population</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/3\">Constructing life tables</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/4\">Calculating post-reproductive life</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/4\">Sensitivity of PrR to length of study</a></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/4\">Results</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/4\">Post-reproductive representation</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/5\">Sensitivity of PrR to length of study</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/6\">Discussion</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/9\">Conclusions</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Supplementary information</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Abbreviations</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Acknowledgements</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Authors’ contributions</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Funding</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Availability of data and materials</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Ethics approval and consent to participate</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Consent for publication</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Competing interests</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">Author details</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/10\">References</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_MFK9LDZ6/11\">Publisher’s Note</a></li></ul>",
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            "title": "Asian elephants exhibit post-reproductive lifespans",
            "creators": [
                {
                    "creatorType": "author",
                    "firstName": "Simon N.",
                    "lastName": "Chapman"
                },
                {
                    "creatorType": "author",
                    "firstName": "John",
                    "lastName": "Jackson"
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                {
                    "creatorType": "author",
                    "firstName": "Win",
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                    "firstName": "Virpi",
                    "lastName": "Lummaa"
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                    "firstName": "Mirkka",
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            "abstractNote": "BackgroundThe existence of extended post-reproductive lifespan is an evolutionary puzzle, and its taxonomic prevalence is debated. One way of measuring post-reproductive life is with post-reproductive representation, the proportion of adult years lived by females after cessation of reproduction. Analyses of post-reproductive representation in mammals have claimed that only humans and some toothed whale species exhibit extended post-reproductive life, but there are suggestions of a post-reproductive stage for false killer whales and Asian elephants. Here, we investigate the presence of post-reproductive lifespan in Asian elephants using an extended demographic dataset collected from semi-captive timber elephants in Myanmar. Furthermore, we investigate the sensitivity of post-reproductive representation values to availability of long-term data over 50 years.ResultsWe find support for the presence of an extended post-reproductive stage in Asian elephants, and that post-reproductive representation and its underlying demographic rates depend on the length of study period in a long-lived animal.ConclusionsThe extended post-reproductive lifespan is unlikely due to physiological reproductive cessation, and may instead be driven by mating preferences or condition-dependent fertility. Our results also show that it is crucial to revisit such population measures in long-lived species as more data is collected, and if the typical lifespan of the species exceeds the initial study period.",
            "publicationTitle": "BMC Evolutionary Biology",
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            "volume": "19",
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            "journalAbbreviation": "BMC Evol Biol",
            "DOI": "10.1186/s12862-019-1513-1",
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            "tags": [
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                {
                    "tag": "Demography",
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                    "tag": "Fertility",
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                    "firstName": "Rajapandian",
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                {
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                    "firstName": "Miguel B.",
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                    "firstName": "Thorsten",
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            "abstractNote": "Aim Climate change alters the water cycle, potentially affecting the distribution of species. Using an ensemble of species distribution models (SDMs), we predicted changes in distribution of the Asian elephant in South Asia due to increasing climatic variability under warming climate and human pressures. Location India and Nepal. Methods We compiled a comprehensive geodatabase of 115 predictor variables, which included climatic, topographic, human pressures and land use, at a resolution of 1 km2, and an extensive database on current distribution of elephants. For variable selection, we first developed 14 candidate models based on different hypotheses on elephant habitat selection. For each candidate model, a series of 240 individual models were evaluated using several metrics. Using three climatic and one land use change datasets for two greenhouse gas scenarios, ensemble SDMs were used to predict future projections. Results Nine predictor variables were selected for ensemble SDMs. Elephant distribution is driven predominantly by changes in climatic water balance (>60%), followed by changes in temperature and human-induced disturbance. The results suggest that around 41.8% of the 256,518 km2 of habitat available at present will be lost by the end of this century due to combined effects of climate change and human pressure. Projected habitat loss will be higher in human-dominated sites at lower elevations due to intensifying droughts, leading elephants to seek refuge at higher elevations along valleys with greater water availability in the Himalayan Mountains. Main conclusions Changes in climatic water balance could play a crucial role in driving species distributions in regions with monsoonal climates. In response, species would shift their range upwards along gradients of water availability and seasonal droughts. Conservation and management of elephant populations under global change should include design of movement corridors to enable dispersal of the elephant and other associated species to more conducive environments.",
            "publicationTitle": "Diversity and Distributions",
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            "date": "2019",
            "volume": "25",
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            "rights": "© 2019 The Authors. Diversity and Distributions Published by John Wiley & Sons Ltd",
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                    "tag": "Asian elephant",
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                    "tag": "South Asia",
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            "note": "<p xmlns=\"http://www.w3.org/1999/xhtml\" id=\"title\"><strong>Contents</strong></p><ul xmlns=\"http://www.w3.org/1999/xhtml\" style=\"list-style-type: none; padding-left:0px\" id=\"toc\"><li><a href=\"zotero://open-pdf/541250_GLDMVPES/1\">Abstract</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/1\">Introduction</a></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/2\">Methods</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/2\">Interview survey</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Data analyses</a></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Results</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/1\">Outline placeholder</a><ul style=\"list-style-type: none; padding-left:24px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Grid cells surveyed</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Elephant presence</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">A posteriori test for false negatives</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Spatio-temporal patterns</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Changes in elephant distribution</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/3\">Human--elephant conflict</a></li></ul></li></ul></li><li style=\"padding-top:8px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/4\">Discussion</a><ul style=\"list-style-type: none; padding-left:12px\"><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/4\">Elephant distribution</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/6\">Population subdivision</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/7\">Sexual segregation</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/7\">Seasonality of ranges</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/7\">Changes in elephant distribution</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/8\">Human--elephant conflict</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/8\">Importance as a survey method</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/8\">Management implications</a></li></ul></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/9\">Acknowledgements</a></li><li style=\"padding-top:4px\"><a href=\"zotero://open-pdf/541250_GLDMVPES/9\">References</a></li></ul>",
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            "title": "First country-wide survey of the Endangered Asian elephant: towards better conservation and management in Sri Lanka",
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                    "creatorType": "author",
                    "firstName": "Prithiviraj",
                    "lastName": "Fernando"
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                    "firstName": "M. K. Channa R. De",
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            "abstractNote": "The Endangered Asian elephant Elephas maximus comes into widespread conflict with agrarian communities, necessitating active management. The species’ distribution is of primary importance for management planning. However, data-based countrywide distribution maps have not been available for any of the 13 Asian elephant range states. We conducted a 5 × 5 km grid-based questionnaire survey in Sri Lanka to produce an island-wide elephant distribution map. Elephants occur over 59.9% of Sri Lanka and people are resident in 69.4% of elephant range, indicating the challenge of separating people and elephants at a landscape scale. Elephants in Sri Lanka have lost 16.1% of their range since 1960 but their current distribution remains largely contiguous. We found the range of adult males was 15.1% greater, and less seasonal, than that of herds, possibly because males have a higher tolerance for conflict with people. The distribution of conflict coincided with the co-occurrence of humans and elephants. We conclude that a human–elephant coexistence model is the only viable option for effectively mitigating human–elephant conflict and conserving elephants in Sri Lanka. The findings are currently being used to effect a paradigm change in elephant conservation and management in the country.",
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            "abstractNote": "Because of their enormous size, elephants have long been irresistible for kings as symbols of their eminence. In early civilizations—such as Egypt, Mesopotamia, the Indus Civilization, and China—kings used elephants for royal sacrifice, spectacular hunts, public display of live captives, or the conspicuous consumption of ivory—all of them tending toward the elephant’s extinction. The kings of India, however, as Thomas R. Trautmann shows in this study, found a use for elephants that actually helped preserve their habitat and numbers in the wild: war.             Trautmann traces the history of the war elephant in India and the spread of the institution to the west—where elephants took part in some of the greatest wars of antiquity—and Southeast Asia (but not China, significantly), a history that spans 3,000 years and a considerable part of the globe, from Spain to Java. He shows that because elephants eat such massive quantities of food, it was uneconomic to raise them from birth. Rather, in a unique form of domestication, Indian kings captured wild adults and trained them, one by one, through millennia. Kings were thus compelled to protect wild elephants from hunters and elephant forests from being cut down. By taking a wide-angle view of human-elephant relations, Trautmann throws into relief the structure of India’s environmental history and the reasons for the persistence of wild elephants in its forests.",
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