search.noResults

search.searching

saml.title
dataCollection.invalidEmail
note.createNoteMessage

search.noResults

search.searching

orderForm.title

orderForm.productCode
orderForm.description
orderForm.quantity
orderForm.itemPrice
orderForm.price
orderForm.totalPrice
orderForm.deliveryDetails.billingAddress
orderForm.deliveryDetails.deliveryAddress
orderForm.noItems
Georeferencing Sunda pangolin records 67


FIG. 2 Biplot of Sunda pangolin rescues, roadkills and sightings during 2011–2020 in Singapore (Fig. 1) with the associated R2 values.


Heng et al., 2023). However, further studies are needed to determine whether the increase in rescued individuals re- presents a rise in the number of pangolins requiring rescue, increased rescue capacity or more public reporting. Our finding that many pangolin rescues and roadkill


occur along the fringes of core forested areas can help indi- cate hotspot areas where mitigation actions should be fo- cused. These actions could include erecting barriers at road sides, creating wildlife crossings to improve ecological connectivity, and implementing animal detection systems for motorists. Such measures have been shown to reduce wildlife mortality elsewhere (Rytwinski et al., 2016). Of the two current wildlife bridges in Singapore (Fig. 1), at least one is known to be used by Sunda pangolins (NParks, 2015). An underground culvert along Rifle Range Road has also been used by pangolins for crossing (NParks, unpubl. data, 2023), suggesting similar structures could be beneficial at rescue and roadkill hotspots. Identifying these hotspots can also aid public outreach efforts to encourage wildlife- friendly driving or increased reporting of distressed animals. Although hotspot identification was not our initial focus in creating this database, it is a useful starting point for further studies. We found that subadults and adult males were rescued most often and were the main roadkill victims. This could


be because of their dispersal or roaming behaviour, with movement outside forests and into urban areas putting them at a higher risk of collision with vehicles. This behav- iour is consistent with that seen in Temminck’s ground pan- golins Smutsia temminckii:males travel further than females and young pangolins sometimes travel tens of kilometres before establishing a stable home range (Pietersen et al., 2014). Gray et al. (2023) found no statistical difference in daily movement between Sunda pangolin sexes, but on aver- age males moved longer distances. Threat mitigation and post-rescue release strategies could focus on at-risk groups (e.g. releasing adult males far away from urban areas) to help achieve better conservation outcomes. The presence of pangolins in the urban environment far


from core forested areas indicates they sometimes foray into more urbanized areas of Singapore before being seen or requiring rescue. How they move through the city remains unclear because there is insufficient knowledge of the spe- cies’ ecology, such as its dispersal ability and response to habitat disturbance. Further research using telemetry or camera traps could reveal movement pathways and inform pangolin rescue strategies. This database has already been put to use for pangolin conservation. By March 2023, it had been used to provide spatiotemporal pangolin data for environmental impact as- sessments in four development projects in or around pango- lin habitats. Because of their rarity and cryptic behaviour, pangolins are often not detected during environmental im- pact assessment surveys in areas where they occur (M.A.H. Chua, pers. obs.), so the georeferenced database can be a useful aid to inform decision-making for land development projects. Access to the database is available for conservation purposes upon request to the Singapore Pangolin Working Group. It is not openly available because of the need to pro- tect this highly trafficked, Critically Endangered species. A limitation of the database is that it is based on public


reports and rescue data that have not been collected system- atically. Additionally, the database does not focus on pan- golins in their natural habitats, so should not be viewed as a complete representation of pangolin distribution in Singapore. The main challenge that we encountered was the lack of accurate location information in the data, result- ing in the removal of 65 records. When reporting wildlife re- cords, we recommend the use of precise location data, for example by using GPS pin drops or by referring to nearby landmarks. To implement this in Singapore, the Singapore Pangolin Working Group has established a standardized form for reporting sightings of live, injured and dead pan- golins; it includes mandatory fields and records are added to a central database that also collates records of rescued individuals (Singapore Pangolin Working Group, 2024). The Singapore Sunda pangolin georeferenced database


FIG. 3 Sunda pangolin rescues in Singapore from September 1996 to June 2021 by sex and age.


demonstrates the value of citizen science and collating wild- life data from various sources. Beyond our initial findings,


Oryx, 2025, 59(1), 65–68 © The Author(s), 2024. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605324000206


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