Department of Biology and Marine Biology, University of North Carolina Wilmington, Wilmington, North Carolina, 28403, USA.
Department of Biology, California State University, Northridge, California, 91330, USA.
Ecol Appl. 2020 Apr;30(3):e02070. doi: 10.1002/eap.2070. Epub 2020 Feb 3.
Marine protected areas (MPAs) are increasingly implemented as a conservation tool worldwide. In many cases, they are managed adaptively: the abundance of target species is monitored, and observations are compared to some model-based expectation for the trajectory of population recovery to ensure that the MPA is achieving its goals. Most previous analyses of the transient (short-term) response of populations to the cessation of fishing inside MPAs have dealt only with gonochore (fixed-sex) species. However, many important fishery species are protogynous hermaphrodites (female-to-male sex-changing). Because size-selective harvest will predominantly target males in these species, harvesting not only reduces abundance but also skews the sex ratio toward females. Thus the response to MPA implementation will involve changes in both survival and sex ratio, and ultimately reproductive output. We used an age-structured model of a generic sex-changing fish population to compare transient population dynamics after MPA implementation to those of an otherwise similar gonochore population and examine how different features of sex-changing life history affect those dynamics. We examined both demographically open (most larval recruitment comes from outside the MPA) and demographically closed (most larval recruitment is locally produced) dynamics. Under both scenarios, population recovery of protogynous species takes longer when fishing was more intense pre-MPA (as in gonochores), but also depends heavily on the mating function, the degree to which the sex ratio affects reproduction. If few males are needed and reproduction is not affected by a highly female-biased sex ratio, then population recovery is much faster; if males are a limiting resource, then increases in abundance after MPA implementation are much slower than for gonochores. Unfortunately, the mating function is largely unknown for fishes. In general, we expect that most protogynous species with haremic mating systems will be in the first category (few males needed), though there is at least one example of a fish species (though not a sex-changing species) for which males are limiting. Thus a better understanding of the importance of male fish to population dynamics is needed for the adaptive management of MPAs.
海洋保护区(MPAs)作为一种全球范围内的保护工具,越来越多地得到了应用。在许多情况下,它们都是以自适应管理的方式进行管理:目标物种的数量是被监测的,观测结果与基于模型的种群恢复轨迹的预期进行比较,以确保 MPA 实现其目标。以前对海洋保护区内停止捕捞对种群的短期(短期)响应的大多数分析仅涉及雌雄同体(固定性别)物种。然而,许多重要的渔业物种是雌雄同体的雌雄同体(雌性到雄性性别转换)。由于选择性捕捞将主要针对这些物种的雄性,捕捞不仅会降低数量,还会使性别比例向雌性倾斜。因此,对 MPA 实施的反应将涉及到生存和性别比例的变化,最终是生殖产出的变化。我们使用了一种通用雌雄同体鱼类种群的年龄结构模型,比较了 MPA 实施后的短期种群动态与类似的雌雄同体种群的动态,并研究了雌雄同体生活史的不同特征如何影响这些动态。我们研究了两种情况:一种是在 MPA 之外有大量的幼鱼补充(大多数幼鱼来自 MPA 之外),另一种是在 MPA 之内有大量的幼鱼补充(大多数幼鱼是在 MPA 内产生的)。在这两种情况下,当 MPA 前的捕捞强度更大时(如在雌雄同体中),雄性向雌性转变的物种的种群恢复时间更长,但也严重依赖于交配功能,即性别比例对繁殖的影响程度。如果需要的雄性数量较少,并且繁殖不受高度偏向雌性的性别比例的影响,那么种群恢复就会更快;如果雄性是一种限制资源,那么 MPA 实施后种群数量的增加就会比雌雄同体慢得多。不幸的是,鱼类的交配功能在很大程度上是未知的。一般来说,我们预计大多数具有后宫交配系统的雌雄同体物种将属于第一类(需要的雄性数量较少),尽管至少有一个鱼类物种(尽管不是雌雄同体物种)的雄性是限制因素。因此,需要更好地了解雄性鱼类对种群动态的重要性,以便对 MPA 进行适应性管理。