The exotic pet trade is a prominent driver of species decline in Southeast Asia (Tingley et al., 2017). Wildlife trapping has been made easier on the ground via the development of road networks that have opened up land to hunters (Sodhi et al., 2010), and increased internet accessibility has proliferated the sale of exotic pets in both local and global markets (Siriwat and Nijman, 2018). Domestic consumer demand for wild pets has been exacerbated by the rise of Southeast Asia’s middle classes and their subsequent purchasing power (Setyowati, Widayanti and Supriyanti, 2021), alongside the rising popularity of social media and WhatsApp (Hui, 2010) where exotic pet keeping is promoted and facilitated (Izzo, 2010). Subsequently, social media has provided researchers avenues for monitoring consumer trends in wildlife pet keeping. However, whilst the online pet trade in vulnerable or endangered endemic species such as otters, owls, and newts in southeast Asia have received enhanced attention in recent years (see for example Rowley et al., 2016; Harrington, Macdonald and D’Cruze, 2019; Siriwat, Nekaris and Nijman, 2020), trade in non-IUCN-listed endemic species has received less attention despite known population declines.
Common palm civets (Paradoxurus hermaphroditus) and Masked palm civets (Paguma larvata) are endemic species whose trade as pets in Indonesia is increasing. Both species are listed as ‘Least Concern’ on the IUCN Red List of Threatened Species. However, wild Paradoxurus and Paguma populations are decreasing (Duckworth et al., 2015, 2016) and harvesting quotas for civet species are routinely exceeded (Shepherd, 2008; Roberts, 2017; Lewis-Whelan et al., 2023a, Nijman, et al. 2024). Civets remain a common species openly sold in southeast Asia’s wildlife markets (Shepherd, 2008, 2012; Nijman et al., 2014, 2024; Morcatty et al., 2022) where they are sold into civet coffee and tourism industries and as exotic pets (Hooper, 2022a; Trinh Thi et al., 2022; Lewis-Whelan et al., 2023b).
In 2014, Nijman and colleagues documented the formation of Indonesian “Civet Lover” clubs, social clubs comprised of young Indonesian civet pet keeping enthusiasts. Wildlife traders signposted prospective civet owners to Civet Lover clubs for civet pet keeping advice, and the internet was noted as an instrumental platform for Civet Lover social networking. By 2017, 235 Indonesian Civet Lover Facebook groups were recorded with an average 4,031 members in each (Roberts, 2017). By 2020, civet “home breeding” (the selective breeding of civets to produce unique morphological offspring) was recorded (Hooper, 2022b). Increasing sharply on social media from 2016 onwards (Hooper, 2024), home breeding facilities were documented as entrepreneurial and non-regulated, occurring in the homes, backyards, and garages of urban and suburban settings. Species recorded included P. hermaphroditus, P. larvata, Viverricula indica, and Arctogalidia trivirgata (Hooper, 2022b). Lack of adequate trade regulation/enforcement and the low value conservation statuses of civets has enabled civet home breeding to thrive. However, lack of accurate baseline data on wild population numbers and trade estimates makes civet conservation status assessments difficult (Duckworth et al., 2015, 2016; Lewis-Whelan et al., 2023b).
Ongoing debate regarding the taxonomic classifications within the Viverridae family also hinder conservation monitoring as wild population genetics are poorly understood. Research by Veron et al. (2015) proposed that P. hermaphroditus should be recognized as separate species: P. hermaphroditus (Indian and Indochinese regions), Paradoxurus musangus (mainland Southeast Asia, Sumatra, Java and other small Indonesian islands) and Paradoxurus philippinensis (Mentawai Islands, Borneo and the Philippines). A further two subspecies within both P. musangus and P. philippinensis, were hypothesised along with at least two or three subspecies within P. hermaphroditus. Similarly, there are marked morphological differences between P. larvata from Indonesia compared to Vietnam, Laos, and China, including pelage and body size (Hunter, 2019), yet no genetic assessments have been conducted.
Monitoring the online trade in civet pets provides the opportunity to assess the scale of wild civet trade and the potential genealogical implications of captive breeding on species integrity. Given the challenges associated with wild data collection for nocturnal and cryptic species, social media can provide a gateway for researchers to assess the conservation impacts of emerging human-wildlife interactions. This paper serves as an initial account of the breeding rates and morphological changes occurring for Viverrid species within Indonesia’s burgeoning civet “home breeding” practices. The results presented here are from a subset of data taken from a larger online investigation of civet pet keeping practices in Indonesia (undertaken from 2019 until 2023). This paper addresses the following questions: What are the rates of civet breeding for a typical home-breed facility? Which species and from which geographic locations are civets utilised for home breeding? What are the implications of home breeding for the civet conservation?