sed in a generic sense and refers to members of the genera Oreochromis, Sarotherodon and Tilapia. Within Asia, it is believed that the first movement of a tilapia species was in 1930, where Oreochromis mossambicus (Peters) was introduced to Indonesia from South Eastern Africa. This presumably constituted the founder stock of the species that was distributed throughout the region (Mair, 2002). The introduction of cichlid fishes to Asia have been reported in detail by Welcomme (1984, 1988), De Silva (1989) and Welcomme and Vidthayanon (1999).
Tilapias are cultured globally, with production currently exceeding 1.5 million tonnes valued around US$ 1.8 billion in 2002. According to the Food and Agriculture Organization of the United Nations (FAO) aquaculture statistics, in 2002 tilapias had the third largest production among groups of fish (after carps and salmon and trout) in the world. The global aquaculture production of tilapias has been increasing steadily over the past years, with an average percent rate of growth (APR) of 13.2 for the period 1970 - 2002 (Figure 1). For total aquaculture production for the same period, the corresponding rate is 8.9 percent. It should be noted that, in reporting aquaculture production data to FAO, many countries do not report all production to the species- or genus-level. Thus, the data contain a large (almost 20 percent of the total) category of miscellaneous freshwater fish, which is not included in the analysis of tilapia production. It is reasonable to assume that some of these miscellaneous fish are, in fact, also tilapias so that the reported totals are underestimated.
While tilapias contribute to increased food fish production for sale, they are also a major source of animal protein for poorer sectors of many Asian communities (Lin, 1977). Tilapias are also gaining increasing acceptance among consumers in developing and developed countries as well as in sophisticated markets (Ferdouse, 2001; Vannuccini, 2001). In addition, they contribute significantly to inland capture fisheries production in many tropical Asian countries, particularly in the lacustrine waters of Indonesia (Sarinita, 1999), Lao People's Democratic Republic (Bernacsek, 1997; Mattson et al., 2001), Philippines (Guerrero, 1999), Sri Lanka (Fernando and Indrasena, 1969; De Silva, 1988), Thailand (Moreau and De Silva, 1991; Bernacsek, 1997) and Viet Nam (Phan and De Silva, 2000). Total production, capture and culture, of tilapias in the Association of South-East Asian Nations (ASEAN) countries and China was 1 166 737 in 2002 (Bartley et al. in press). However, there is a concern, which is being increasingly expressed, that the introduction of tilapias, accidental or deliberate, into Asia has had detrimental effects on the indigenous fauna and flora. Indeed, it has been suggested that the introduction of tilapias was responsible for the collapse of some traditional fisheries, even to the extent of endangering local species (Gindelberger, 1981; Aypa, 1993).
Available information about tilapias in Asia primarily comes from: (a) aquaculture and inland capture production; (b) biology in natural and quasi-natural waters; and (c) culture of selected species. Despite much speculation, the environmental and socioeconomic impacts of tilapia introductions have rarely been examined or evaluated. In this document, the authors examine the production trends of tilapias in Asia, for both aquaculture and capture fisheries, and to evaluate the socio-economic impacts of the introductions. In addition, the document evaluates the perceived negative influences of tilapias on biodiversity and the environment in Asia.
Capture fishery production of tilapias by region 1970-2002