Changes in the trophic structure of the southern Benguela before and after the onset of industrial fishing

• Published in: African journal of marine science Vol. 30; no. 2; pp. 351 - 382
• Main Authors: Watermeyer, KE, Shannon, LJ, Griffiths, CL
• Format: Journal Article
• Language: English
• Published: Taylor & Francis Group 01.09.2008
• Subjects: ECOPATH; ECOSYSTEM MODEL; FISHING IMPACTS; FOODWEB; Marine; Sardinops; Scomber; SOUTHERN BENGUELA; TROPHIC FLOWS; ASE, South Atlantic, Benguela Current
• ISSN: 1814-232X; 1814-2338
• DOI: 10.2989/AJMS.2008.30.2.11.561

Despite a human presence in the Benguela region for at least one million years, exploitation of marine resources by European seafarers only began in earnest in the 1400s. Ecopath with Ecosim was used to construct and compare mass-balanced foodweb models of the southern Benguela ecosystem, representing the following eras of human influence: aboriginal (10 000 BP-1651), pre-industrial (1652-1909), industrial (1910-1974) and post-industrial (1975-present). Biomass at higher trophic levels (TLs) decreased over the periods examined, whereas that of sardine and anchovy increased in the early 2000s, reflected by the decline in weighted TL of the community (excluding plankton). Fishing became an important predatory impact, taking over consumption of small pelagics and horse mackerel from declined natural predators such as hake. Harvesting of apex predators such as seals and seabirds during the pre-industrial era meant that the mean TL of the catch declined markedly between the pre-industrial (1900) and industrial (1960) models. Biomass removals by fishing have increased substantially over time. Total biomass, consumption, respiration, production and throughput decreased from the pristine model to 1960 and then increased again in the 2000s, probably influenced by the abnormally high small pelagic biomass in the early 2000s. Three additional alternate scenarios were examined for each of the retrospective models, in particular to explore the effects of removing large fish and forage fish from the system. Although biomasses and consumption of various groups in these scenarios differed from base models, indicators such as TL of the community and piscivore groups, and the diversity indices, were not altered much, suggesting that outputs from such retrospective models in the form of derived, relative indicators, may be more robust than comparisons of absolute flows, although the latter provide supplementary inferences. Although South African fisheries have certainly impacted ecosystem structure since their commencement, these effects are in addition to natural (specifically environmental) forcing that has always been influencing the system. Fishing stress at the ecosystem level and the collapse of small pelagic stocks may lead to a shift toward a bottom-up trophic control mechanism becoming the dominant driver of ecosystem dynamics, increasing the impact of environmental events including climate change. It is thus possible that pristine systems were not as severely affected by environmental anomalies as are modern systems.