A study was carried out during the period from September 2001 to August 2002 in Jimma zone, western Ethiopia to evaluate the husbandry and health of captive African civets (Vivera civetica). Wild civets were found in the wild in all 13 of the districts in the zone, although traditional civet-keeping was practiced in only five. Civet management practices were determined via the use of a questionnaire survey of 15 farms; containing a total of 107 civets. Health was assessed by routine clinical examination, and examination of faecal and blood smears of 55 civets selected at random. All civets were male and over one year of age, with a mean weight of 12.5 ± 0.79 kg. Fifteen percent were in poor body condition, and only 13% had a good body condition score. An average of 7.13 civets were kept on each farm. Farmers obtained wild civets by either trapping them themselves, purchasing them from dealers or a combination of both. The civets were housed separately in wooden cages, with an average size of 1.0 × 0.5 × 1.0 m (length × breadth × height) and kept in a communal thatched room. They were fed boiled meat, milk (fresh or powdered), eggs, butter, corn soup and fruit juice. Although an assessment of the behavioural parameters of welfare were outwith the scope of this study, trapping methods, adaptation processes, housing condition, restraint and the techniques for musk extraction from the anal glands were stressful and injurious, and have important welfare implications. Approximately 20 g of musk was expressed from a single civet every 9-15 days. The civets often sustained injuries while being restrained during musk harvesting; 14% had swelling and bruising, 6.5% fractures and 11.2% had eye lesions. Cestodes were the most prevalent gastrointestinal parasites, followed by ancylostomes, ascarides and Tricuris spp. Skin lesions were identified in 19.6% of civets examined and an assortment of fleas and ticks including Haemophysalis leachi, Rhipicephalus and Amblyoma spp were found on the body. Trypanosoma congolense and Babesia felis were identified in blood smears taken from four animals. This study shows there is an urgent need to invest in research into improving the welfare, husbandry and health of civets, as well as providing educational programmes for those who farm these animals.

The role of wild meat for subsistence or as a luxury good is debated. We investigated the role of wild meat in food security in Madagascar, where consumption is poorly understood in urban areas and at regional scales. Using semi-structured interviews (n = 1339 heads-of-households, 21 towns), we aimed to: (1) quantify the amount and purpose of, (2) understand the drivers of, and (3) examine changes in wild meat consumption. Few respondents preferred wild meat (8 ± 3%) but most had eaten it at least once in their lifetime (78 ± 7%). Consumption occurred across ethnic groups, in urban and rural settings. More food insecure areas reported higher rates of wild meat consumption in the 6–8 months prior to interviews. Consumption was best explained by individual preferences and taboos. Less than 1% of respondents had increased consumption during their lifetimes. Wild meat prices showed no change from 2005–2013. Most consumption involved wild pigs and smaller-sized animals, though they were consumed less in the years following the 2009 coup. These data illustrate the differences between urban and rural communities, the occasions in which wild meat is used a source of food security, and provide evidence that some taxa are not hunted sustainably in Madagascar.

Rigorous population studies on many small carnivores are lacking in India. Presence-absence models with habitat covariates were applied to estimate seasonal occupancy and abundance of nine small-carnivore species from camera-trap data in Mudumalai Tiger Reserve (2010 and 2011). We deployed 25 camera-trap stations in the deciduous forest, 21 in the semi-evergreen forest and 26 in the dry thorn forest. In total, 7380 trap-nights yielded 448 photographs of small carnivores: jungle cat (n = 72), leopard cat (n = 6), rusty-spotted cat (n = 11), small Indian civet (n = 89), common palm civet (n = 37), brown palm civet (n = 20), stripe-necked mongoose (n = 66), ruddy mongoose (n = 96) and Indian grey mongoose (n = 51). In the dry season, rusty-spotted cat was the rarest carnivore with an average abundance (λmean) of 0.24 ± 0.26, while ruddy mongoose was the most abundant (λmean = 0.90 ± 0.40). In the wet season, leopard cat was the rarest species (λmean = 0.048 ± 0.041) while grey mongoose was the most abundant (λmean = 0.68 ± 0.35). Abundance of jungle cat, common palm civet, ruddy mongoose and grey mongoose increased in the dry thorn forest whereas in the dry season abundance of small Indian civet decreased in this forest type. Abundance of leopard cat and small Indian civet was not influenced by habitat in the wet season. Deciduous forest was positively associated with abundance of rusty-spotted cat. Deciduous and semi-evergreen forests had a positive effect on abundance of stripe-necked mongoose while the latter was a positive predictor of abundance and occupancy for brown palm civet. Improved modelling approaches can account for the spatio-temporal variation in habitat use of small carnivores occupying specialized niches in heterogeneous tropical forests of southern India.