search.noResults

search.searching

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
764 A. Yanuar et al.


FIG. 1 Sungai Palin and Nanga Awen, indicating the location of the transects used to survey for orangutan nests in limited production forest and peat swamp forests, in Kapuas Hulu, west Kalimantan, Indonesia.


In both 2017 and 1991 the perpendicular distance of all


nests visible from each transect was measured with a tape. Density estimates for both sets of data were computed using the signed nest-count technique (Schaik et al., 1995). We used Distance 6.0 (Thomas et al., 2010) to estimate the effective strip width and thus determine the survey area and estimate nest density in both Sungai Palin and Nanga Awen. Distance uses a detection curve to estimate detectability (Buckland et al., 1993) as a function of the perpendicular dis- tance of nests from the centre of the transect (Cattau et al., 2014). We calculated nest density as Dn = n/L2w, where Dn is nest density, n is the number of nests counted on a tran- sect; L is transect length (in km), and w is the effective transect strip width (measured in m, converted to km), and orangutan density was calculated as Do = Dn/prt, where Do is orangutan density, p is the proportion of nest builders, r is daily nest production rate per orangutan and t is nest decay rate (Russon et al., 2001; Morrogh-Bernard et al., 2003; Johnson et al., 2005; Van Schaik et al., 2005). We used values of p = 0.85, r = 1.0 and t = 202, determined in studies (Ancrenaz et al., 2004) at sites with a similar habitat type and disturbance level to our survey area (peat-swamp forest of Lower Kinabatangan and surrounding areas in Malaysia; Ancrenaz et al., 2005). Weobserved a total of 76 orangutan nests along a total of


4.5 km of transects in Sungai Palin, and 71 nests along a total of 3.4 km of transects were observed in Nanga Awen. Mean nest densities were 222 ± SE 82.14 and 499 ± SE 162.43 per km2 in Sungai Palin and Nanga Awen, respectively (Table 1). The density estimate for Sungai Palin in 2017 is slightly lower than that for Nanga Awen in 1991 (Table 1), suggesting that orangutan density may have halved between these dates and that the orangutan population outside


protected areas remains relatively low. The building of new roads is one of the threats to the orangutan subpopulation on Sungai Palin (Local people, pers. comm., 2017). Estimated orangutan density in Sungai Palin is lower


than in the peat-swamp forest of Danau Sentarum National Park and the peat-swamp forest of the former Mega-Rice project in central Kalimantan, higher than that in the lowland and hill lowland forests of Betung Kerihun National Park, but similar to that in Sebangau National Park (Table 2). Many factors influence orangutan density in disturbed forests, including food availability, connectivity between forest remnants, and whether orangutans can sur- vive after habitat loss. The logging concession in the area of Nanga Lauk village has been inactive since at least 2003 (Local people, pers. comm., 2017), and there are no reports of local people hunting orangutans in the Nanga Lauk forest area, even though orangutans sometimes take honey from local beehives (Local people, pers. comm., 2017). Protection forests surrounding the Sungai Palin and


Nanga Awen landscape are under the jurisdiction of the district forestry agency, but are managed by the local com- munity as the Nanga Lauk Village Forest (Hutan Desa). The community is allowed to extract non-timber forest products only. This initiative to include the local community in man- aging forest land has helped to protect the orangutan, as evi- denced by the fact that logging ceased in 2003. The people of Nanga Lauk plan to expand the area of this Village Forest (Damayanti et al., 2016). More detailed surveys of the orangutan and its habitat


are required in this area, so that the orangutan population can be appropriately managed. As Sungai Palin and Nangan Awen lie between Danau Sentarum Wildlife Reserve and Betung Kerihun National Park, awareness amongst the


Oryx, 2020, 54(6), 763–766 © 2019 Fauna & Flora International doi:10.1017/S0030605319000875


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