Western Africa is here considered to stretch from Mauritania to the northern part of Angola. The region includes a large number of coastal countries, listed here from north to south: Mauritania, Senegal, The Gambia,
Guinea-Bissau, Guinea, Sierra Leone, Liberia, Ivory Coast, Ghana, Togo, Benin, Equatorial Guinea, Nigeria,
Cameroon, Gabon, Congo, Democratic Republic of Congo (formerly Zaire) and Angola. In addition the offshore island countries of Cape Verde and Sao Tome and Principe fall within the subregion, equivalent to FAO Statistical Area 34.
Both commercial and artisanal marine fisheries operate in most West African coastal countries. Commercial fisheries operate mainly by longline, trawl and purse seine, with most nations licensing foreign fleets (primarily East Asian and European) to operate within their waters. Artisanal fisheries in the region are exceptionally diverse
and difficult to characterise, with vessel size, numbers of crew, target species and gear types all highly variable, even within one day’s fishing operation.
The countries in the northern part of the region are all net fish exporters (Table 3), owing in part to the productive upwelling system in the region. The commercial fleets of many of these countries are not well developed and have large numbers of foreign or joint venture vessels in operation (Table 3). Countries in the southern and equatorial part of this region are net fish importers and have large artisanal fisheries. Gillnets are the most commonly used gear
in the artisanal fisheries, accounting for 22-73% of the total catch.
Most of the assessed fish stocks within the region are considered either fully exploited (43%) or overexploited (53%), with the major fish species in terms of landings, sardine
Sardina pilchardus not fully exploited only from Senegal northwards (FAO 2012). This parlous state (53% overexploited) does not mean that negative impacts on seabird from fishing
will remain as they are; as fish become scarcer, effort to catch them is likely to increase, which may increase the rates of seabird interactions, further
deterioration in fish stocks, etc. More alarming is the impact of overexploitation on low trophic level species such as sardines, with indirect impacts on seabirds through competition (e.g. Cury et al. 2011) and potentially more problematic, ecosystem-wide changes to trophic dynamics, with the potential for the permanent loss of commercially important species being a real possibility (e.g. Crawford 1998).