According to the estimated ecological footprint (EF) of fishery production (EFf), Algiers fishing is in the status of ecological surplus, as the demand for fisheries production averages 15,338.49 gha compared to more than 108 thousand gha of biologically productive fishing area. In addition to this overall output, this metric indicates each species’ primary production requirement (PPR), which could help to restructure the fishing effort based on the stock’s condition. For the energy component, the fuel consumption and greenhouse gas (GHG) emissions expressed in metric tons of CO2 were used to estimate the required area for carbon sequestration, valued roughly at 500 gha. The latter is a reference state and remains approximate because it was derived from unofficial data provided by the fishers.
1. EF to Restructure Fishing
Algerian fishing is mainly coastal, dominated by pelagic fishes. The ecological footprint (EF) of fishery production (EFf) analysis indicates that the demand for fisheries resources is substantially lower than the biological capacity of the available fishing grounds in the region of interest (fishing grounds biocapacity). According to the ecological footprint (EF) concept rationale, the fishing area would be in a state of an “ecological reserve”. This assumption can neither confirm nor reject the ecological deficit state attributed to Algeria
[1] because this study was carried out on a small scale (ports of Algiers) and only considered local production statistics. Moreover, the Global Footprint Network (GFN) calculation uses international, synthetic data on fisheries and aqua farming production and trade. The EF of production based on primary production requirement (PPR) is even more interesting, as it serves as a lens to estimate the biomass demand of each species. For example, Crustaceans and Mollusks have the lowest PPR records due to their trophic levels, implying that increasing their catches would have negligible effects on the overall EFf. However, such a strategy should consider the species’ stock status.
Furthermore, it is worth noting that in Algeria, both overfishing and sustainable fishing have been reported for different locations and species. Indeed, the stocks of horse mackerel, bogues, red mullet, and axillary seabream do not appear to suffer from overexploitation in the port of Algiers
[2], or round sardinella in Ghazaouet
[3]. In other locations, the status of these populations’ stock has been described as unsustainable, particularly, the horse mackerel stock at the port of Bou Ismail
[4], or overexploited for the red mullet, the Axillary seabream, and the Common sardine at the ports of Beni-Saf
[5] and Ghazaouet
[3]. However, the same authors recommend that these findings be investigated cautiously due to the sampling strategy and data collection system, which is regarded as weak and possibly biased
[6][4]. In this case, the EF model could be an effective organizational tool for data collection. However, concerning the uncertainties and the complexity of the component assessed, it is evident that EF results should be supplemented by other studies, such as biological and stock dynamics analyses
[2][7][8], as well as environmental parameters and climate monitoring, which is assumed to be lacking at the level of fisheries management structures
[9].
2. Energy Use Inventory
According to this research, the catch of one ton of fisheries products requires an average of 22 L of diesel each year. More than a thousand metric tons of CO2 are released from this combustion, requiring about five hundred global hectares of sequestration land. This metric has been derived from data supplied by fishers and serves as a baseline since no previous research has been undertaken in this sector. However, detailed data on the number of days at sea, departure and arrival times, distance traveled, and actual fuel consumption would improve the quality of the results.
The effectiveness of the component-based EF remains in its standardized structure, which might support entities attempting to track their energy use and contribute to the establishment of greenhouse gases (GHG) inventories by activity type. Furthermore, the simple EF design makes it straightforward facilitates its usage by fishers, and allows them to engage in the management of fishing in a participatory framework. Indeed, according to national experts, multidisciplinarity is a crucial prerequisite for the fishing sector’s long-term growth
[10]. In the context of the present study, the estimate of the CO
2 sequestration land is approximate and probably not representative of the activity. A more detailed approach based on an accurate number of trips per type of métier conducted in the fishing ports of Tipaza (Algeria) has provided representative results, outlining the correlation between production and fuel consumption by vessel types
[11]. The latter highlighted that sardine vessels use the least fuel quantity per estimated production, compared to trawlers and small-scale vessels representing 67% and 23%, respectively, of the CO
2 emissions associated with fishing
[11].
3. Available Fishing Grounds
This situation of “ecological reserve” available and potentially exploitable meets the hypothesis of other authors in Algeria who stipulate the possibility of investigating further areas, notably zones of more than 500 m of depth
[12][13]. Nonetheless, managers and decision-makers should not arbitrarily expand fishing efforts based on this conclusion. Indeed, prior initiatives to increase the national production resulted in a temporary growth that faded due to intense competition for the same marketed resource and the same space explored by all users
[14].
This entry is adapted from the peer-reviewed paper 10.3390/su14031418