Marine Spatial Ecology Lab & ARC Centre of Excellence for Coral Reef Science, School of Biological Sciences, The University of Queensland, St. Lucia, Queensland, Australia.
Darling Marine Center, School of Marine Sciences, University of Maine, Walpole, Maine, USA.
Conserv Biol. 2021 Oct;35(5):1473-1483. doi: 10.1111/cobi.13738. Epub 2021 Apr 28.
By 2004, Belize was exhibiting classic fishing down of the food web. Groupers (Serranidae) and snappers (Lutjanidae) were scarce and fisheries turned to parrotfishes (Scarinae), leading to a 41% decline in their biomass. Several policies were enacted in 2009-2010, including a moratorium on fishing parrotfish and a new marine park with no-take areas. Using a 20-year time series on reef fish and benthos, we evaluated the impact of these policies approximately 10 years after their implementation. Establishment of the Southwater Caye Marine Reserve led to a recovery of snapper at 2 out of 3 sites, but there was no evidence of recovery outside the reserve. Snapper populations in an older reserve continued to increase, implying that at least 9 years is required for their recovery. Despite concerns over the feasibility of banning parrotfish harvest once it has become a dominant fin fishery, parrotfishes returned and exceeded biomass levels prior to the fishery. The majority of these changes involved an increase in parrotfish density; species composition and adult body size generally exhibited little change. Recovery occurred equally well in reserves and areas open to other forms of fishing, implying strong compliance. Temporal trends in parrotfish grazing intensity were strongly negatively associated with the cover of macroalgae, which by 2018 had fallen to the lowest levels observed since measurements began in 1998. Coral populations remained resilient and continued to exhibit periods of net recovery after disturbance. We found that a moratorium on parrotfish harvesting is feasible and appears to help constrain macroalgae, which can otherwise impede coral resilience.
到 2004 年,伯利兹已经出现了典型的渔业捕捞食物链降级现象。石斑鱼( Serranidae )和笛鲷( Lutjanidae )数量稀少,渔业转而捕捞鹦嘴鱼( Scarinae ),导致其生物量减少了 41%。2009-2010 年出台了几项政策,包括禁止捕捞鹦嘴鱼的禁令和一个没有捕捞区的新海洋公园。利用 20 年的珊瑚礁鱼类和底栖生物时间序列数据,我们评估了这些政策在实施大约 10 年后的影响。Southwater Caye 海洋保护区的建立导致了 3 个地点中有 2 个地点的笛鲷数量恢复,但保护区外没有恢复的迹象。一个较老保护区内的笛鲷种群继续增加,这意味着至少需要 9 年才能恢复。尽管人们担心一旦鹦嘴鱼成为主要的鱼类捕捞对象,禁止捕捞鹦嘴鱼的可行性,但鹦嘴鱼还是回来了,并超过了渔业前的生物量水平。这些变化中的大部分涉及到鹦嘴鱼密度的增加;物种组成和成年体型普遍变化不大。保护区和其他形式的捕鱼区都同样很好地恢复了,这意味着遵守情况很强。鹦嘴鱼摄食强度的时间趋势与大型藻类的覆盖率呈强烈负相关,到 2018 年,大型藻类的覆盖率已经降至 1998 年开始测量以来的最低水平。珊瑚种群仍然具有弹性,并在受到干扰后继续表现出净恢复的时期。我们发现,禁止捕捞鹦嘴鱼是可行的,似乎有助于限制大型藻类的生长,否则大型藻类会阻碍珊瑚的恢复。