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PeerJ
2022 Oct 06;10:e12971. doi: 10.7717/peerj.12971.
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Sea urchin harvest inside marine protected areas: an opportunity to investigate the effects of exploitation where trophic upgrading is achieved.
Ceccherelli G
,
Addis P
,
Atzori F
,
Cadoni N
,
Casu M
,
Coppa S
,
De Luca M
,
de Lucia GA
,
Farina S
,
Fois N
,
Frau F
,
Gazale V
,
Grech D
,
Guala I
,
Mariani M
,
Marras MS
,
Navone A
,
Pansini A
,
Panzalis P
,
Pinna F
,
Ruiu A
,
Scarpa F
,
Piazzi L
.
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BACKGROUND: Marine protected areas (MPAs) usually have both positive effects of protection for the fisheries' target species and indirect negative effects for sea urchins. Moreover, often in MPAs sea urchin human harvest is restricted, but allowed. This study is aimed at estimating the effect of human harvest of the sea urchin Paracentrotus lividus within MPAs, where fish exploitation is restricted and its density is already controlled by a higher natural predation risk. The prediction we formulated was that the lowest densities of commercial sea urchins would be found where human harvest is allowed and where the harvest is restricted, compared to where the harvest is forbidden.
METHODS: At this aim, a collaborative database gained across five MPAs in Sardinia (Western Mediterranean, Italy) and areas outside was gathered collecting sea urchin abundance and size data in a total of 106 sites at different degrees of sea urchin exploitation: no, restricted and unrestricted harvest sites (NH, RH and UH, respectively). Furthermore, as estimates made in past monitoring efforts (since 2005) were available for 75 of the sampled sites, for each of the different levels of exploitation, the rate of variation in the total sea urchin density was also estimated.
RESULTS: Results have highlighted that the lowest sea urchin total and commercial density was found in RH sites, likely for the cumulative effects of human harvest and natural predation. The overall rate of change in sea urchin density over time indicates that only NH conditions promoted the increase of sea urchin abundance and that current local management of the MPAs has driven towards an important regression of populations, by allowing the harvest. Overall, results suggest that complex mechanisms, including synergistic effects between natural biotic interactions and human pressures, may occur on sea urchin populations and the assessment of MPA effects on P. lividus populations would be crucial to guide management decisions on regulating harvest permits. Overall, the need to ban sea urchin harvest in the MPAs to avoid extreme reductions is encouraged, as inside the MPAs sea urchin populations are likely under natural predation pressures for the trophic upgrading.
Figure 1. Maps of Sardinia and the studied MPAs. CI, Capo Caccia-Isola Piana; AS, Isola dellâAsinara; SN, Penisola del Sinis-Isola di Mal di Ventre; TV, Tavolara Punta Coda Cavallo; CC, Capo Carbonara.Zonation of each MPA is showed: A zone in red, B zone in grey and C zone in light grey.
Figure 2. Paracentrotus lividus. (A) total and (B) commercial density (mean and the confidence interval) at the NH (no harvest), RH (restricted harvest) and UH (unrestricted harvest) sites (replicated sites n = 33, 37, and 36, respectively).
Figure 3. Paracentrotus lividus. Response (mean ± SE) of total density (black) and commercial density (white) to no harvest (NH) and restricted harvest (RH) conditions.Response was quantified by the natural logarithm of the ratio between the values of each response variable (sea urchin total and commercial density) at NH and RH conditions versus UH conditions.
Figure 4. Paracentrotus lividus. Temporal variability in total abundance (individuals/m2) at NH, no harvest; RH, restricted harvest and UH, unrestricted harvest conditions from 2005 to 2019.The number of sites from which each mean (and SE) was calculated is indicated at the bottom of the plot.
Figure 5. Paracentrotus lividus. Rate of variation (mean±SE across 15 years) in total abundance (individuals/m2yr) at NH (no harvest), RH (restricted harvest) and UH (unrestricted harvest) conditions (replicated sites n = 27, 28, and 13, res.
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