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
834 S. D. Merson et al.


impact of dogs on Madagascar’s ecosystem is still being investigated. Disease transmission from cats and dogs is a significant


threat to the long-term health of endemic species. Fatal cases of Toxoplasma gondii infection have been recorded in captive fosas (Corpa et al., 2013) and lemurs (Juan-Sallés et al., 2011; Siskos et al., 2015), highlighting their vulnerability to lethal infections. Field studies of exotic carnivores in Ankarafantsika NationalPark have identified the occurrence of multiple viruses and parasites, including canine parovirus, feline calicivirus and T. gondii (Pomerantz et al., 2016), the latter prevalent in .93% of captured wild fosas. The detri- mental impact of disease on Madagascar’s wild fosa popula- tions could be significant, reflecting disease-related species population declines elsewhere (Pedersen et al., 2007).


Habitat degradation impact on fosa occupancy


PLATE 1 Wild cats Felis sp. preying on (a) a red-fronted brown lemur Eulemur rufus and (b) a speckled hognose snake Leioheterodon geayi in Andranomena Special Reserve, Madagascar (Fig. 1).


Masoala–Makira (Murphy et al., 2018a); negative associations have also been recorded between cats and the rainforest- dwelling euplerids Galidia elegans and Fossa fossana (Gerber et al., 2012a; Farris et al., 2015b). Collectively these results sug- gest that cats are probably having a negative impact on the fosa and other endemic species, at the very least through direct pre- dation and competition for prey. In concordance with previous studies in rainforest, dogs


did not have a negative association with fosa occupancy (Gerber et al., 2012a; Farris et al., 2015b). This is in contrast with the reported impact of dogs on the euplerid Galidictis fasciata (Gerber et al., 2012a) and incongruous with the damaging effects of dogs globally (Hughes & Macdonald, 2013). However, activity pattern analyses have indicated fosas display temporal activity shifts towards greater noctur- nality (Farris et al., 2015a; Merson, 2018), and/or absence from sites with higher frequency of dog detections (Gerber et al., 2012a; Farris et al., 2015b). The sociality and size of dog packs (L.J. Dollar, unpubl. data) may be a source of interference competition for fosas, but the predatory


Fosa occupancy was higher in Andranomena Special Reserve, possibly because of greater forest cover, and lower dog and human presence. However, within ourmodels fosa occupancy was not influenced by any habitat degradation parameters, with results similar to those reported for Madagascar’srainfor- ests (Gerber et al., 2012a; Farris et al., 2015b). Despite this, sur- veys have not recorded fosas in areas.5 km from the nearest contiguous forest (Kotschwar Logan et al., 2015)orinforest fragments .2.5 km from the nearest contiguous forest (Gerber et al., 2012a). This suggests that despite their resilience to habitat degradation within contiguous forest, fosas are un- able to persist far fromintact forest.ConsideringMadagascar’s highly fragmented forests (Vieilledent et al., 2018), it is likely that most forest areas are of insufficient size to support fosa populations in the long term (Hawkins & Racey, 2005). Cat occupancy was higher in the Reserve, positively asso-


ciated with higher vegetation cover and weakly associated with narrow trails. This could be attributed to their avoidance of larger carnivores (dogs, fosas) andpeople.Farris et al. (2015b) found similar positive associations with forest cover, possibly confirming theirpreference forareasofgreater preyabundance. Dogs had the highest occupancy in the Park. They had


a positive association with large trails, and civets, and a negative association with old-growth forest, and savannah, possibly explained by dogs accompanying people during forest-related activities. This was apparent in the Park, where the forest surrounding rural villages encompassed a mixture of savannah and degraded forest, with high pres- ence of people and exotic species (e.g. zebu, civet).


Long-term implications


Looking beyond the snapshot view of single-season occu- pancy models, recent multi-year studies in north-eastern Madagascar recorded occupancy of endemic and exotic


Oryx, 2020, 54(6), 828–836 © 2019 Fauna & Flora International doi:10.1017/S003060531800100X


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