Virginia Institute of Marine Science, William & Mary, Gloucester Point, Virginia, United States of America.
PLoS One. 2022 May 31;17(5):e0267880. doi: 10.1371/journal.pone.0267880. eCollection 2022.
Non-native species can become deleterious or potentially beneficial as components of novel ecosystems. The non-native red macroalga Gracilaria vermiculophylla may provide nursery habitat where eelgrass Zostera marina has been extirpated in Chesapeake Bay. A mensurative experiment was conducted monthly May-October 2013 and 2014 in the York River, Chesapeake Bay, to evaluate hypotheses that Gracilaria (1) can compensate for the loss of seagrass nurseries by colonizing habitats where seagrass has been eliminated by environmental stress, and (2) is utilized by juvenile blue crabs (Callinectes sapidus) as nursery habitat. We quantified Gracilaria presence, percent cover, and biomass as a function of region (upriver, midriver, and downriver) and seagrass presence or absence using stratified random sampling, 20-m transects, and 0.0625-m2 quadrats. Gracilaria volume was measured and converted to dry weight. Effects of the factors and covariates temperature, salinity, dissolved oxygen, month, and year were analyzed using generalized linear models. Juvenile blue crab density was quantified in summer 2013 using suction sampling in Gracilaria and seagrass. A model with the collective effect of region and seagrass presence or absence (downriver seagrass, downriver unvegetated bottom, midriver unvegetated bottom) best predicted Gracilaria abundance. Gracilaria presence, percent cover, and biomass were highest in downriver seagrass, followed by downriver unvegetated bottom, and then midriver unvegetated bottom, where seagrass has been extirpated, supporting hypothesis (1). Gracilaria did not occur upriver, likely due to a lack of recruitment. Seagrass and Gracilaria housed similar densities of juvenile blue crabs, supporting hypothesis (2). We estimated that a single 40-ha cove system with Gracilaria could house 200,000 juvenile crabs as would a single 2.4-ha seagrass bed. Consequently, the numerous midriver and downriver cove systems in the York River could support millions of young juvenile blue crabs and thereby compensate for the loss of seagrass in the river and in other areas of Chesapeake Bay. At present, Gracilaria has no widespread negative impacts on seagrass in the York River or most regions of Chesapeake Bay, likely because percent cover and biomass are not excessively high at present. We posit that Gracilaria has become an important alternative nursery habitat for the blue crab in Chesapeake Bay and can potentially mitigate impacts of climate change on seagrass nursery habitats.
外来物种可能会成为有害的或潜在有益的,成为新生态系统的组成部分。外来的红色大型海藻石莼可能会在切萨皮克湾的海草草场被消灭的地方提供育苗栖息地。2013 年 5 月至 10 月和 2014 年,在切萨皮克湾的约克河进行了一项测量实验,以评估以下假设:(1)石莼可以通过在被环境压力破坏的海草栖息地中定殖来弥补海草苗圃的损失,(2)它被幼年蓝蟹(Callinectes sapidus)用作苗圃栖息地。我们使用分层随机抽样、20 米的横断和 0.0625 平方米的四分位数,以区域(上游、中游和下游)和海草的存在或不存在为函数,量化了石莼的存在、覆盖率和生物量。用体积测量石莼并将其转换为干重。使用广义线性模型分析了温度、盐度、溶解氧、月份和年份等因素和协变量的影响。2013 年夏季,在石莼和海草中使用吸力采样来量化幼年蓝蟹的密度。一个由区域和海草存在或不存在(下游海草、下游无植被底部、中游无植被底部)共同作用的模型可以最好地预测石莼的丰度。石莼的存在、覆盖率和生物量在下游海草中最高,其次是下游无植被底部,然后是中游无植被底部,在那里已经消灭了海草,这支持了假设(1)。石莼在河流上游没有出现,可能是由于缺乏繁殖。海草和石莼的幼年蓝蟹密度相似,这支持了假设(2)。我们估计,一个拥有 40 公顷石莼的单个海湾系统可以容纳 20 万只幼年蟹,而一个拥有 2.4 公顷海草床的系统也可以容纳 20 万只幼年蟹。因此,约克河的许多中游和下游海湾系统可以容纳数百万只幼年蓝蟹,从而弥补河流和切萨皮克湾其他地区海草的损失。目前,石莼对约克河或切萨皮克湾大部分地区的海草没有广泛的负面影响,这可能是因为目前的覆盖率和生物量并不是过高。我们假设,石莼已成为切萨皮克湾蓝蟹的一个重要替代育苗栖息地,并可能减轻气候变化对海草育苗栖息地的影响。