Ecol Appl. 2014 Mar;24(2):300-14. doi: 10.1890/13-0524.1.
Eutrophication, defined as the accumulation of organic matter typically in response to anthropogenically enhanced nutrient inputs, often takes the form of macroalgal blooms in shallow estuaries and causes a cascade of adverse ecosystem effects. Confidence in the use of macroalgae as an indicator of eutrophication in estuaries is limited by the lack of quantitative data on thresholds of adverse effects. Field experiments can provide "benchmarks" of no effect or adverse effects that can be used to validate thresholds derived statistically from field data. To determine a benchmark of adverse effects of macroalgal abundance on macrobenthic faunal communities in intertidal flats, experiments were conducted in two sites in Bodega Harbor (BOD) and two sites in Upper Newport Bay (UNB), California, USA. At each site, 24 cages maintained six treatments of macroalgae for eight weeks, with mat depths of 0, 1.0, 1.5, 2.5, 3.5, and 5.0 cm composed mostly of bloom-forming green macroalgae in the genus Ulva. Every two weeks, cores of sediment (10 cm deep) were collected, and macrofauna were quantified. Mats 1 cm deep, equivalent to a biomass of 110-120 g dry mass (dm)/m2 or 840-930 g wet mass/m2, resulted in the reduction of macrofaunal abundance by at least 67% and species richness by at least 19% within two weeks at three of four sites. Loss was attributed to the decline of key functional groups. Surface-deposit feeders were eliminated from one site at BOD within four weeks and at one site in UNB within six weeks, while 1-cm mats negatively affected suspension feeders and herbivores in the second site at BOD. In contrast, the other site at UNB was not affected by macroalgal treatment, likely due to an initial community composed of a high proportion of subsurface-deposit feeders tolerant of stressful environments. Macroalgal abundances as low as 110-120 g dm/m2 had significant and rapid negative effects on macrobenthic invertebrates, providing a clear benchmark of adverse effects of macroalgal blooms on macrofaunal abundance and community structure, two indicators of ecosystem health. This information can inform the establishment of appropriate metrics for macroalgal abundance in eutrophic estuaries.
富营养化是指由于人为增强的营养物质输入而导致有机物的积累,通常表现为浅河口的大型藻类大量繁殖,并引发一系列不良的生态系统效应。人们对大型藻类作为河口富营养化指示物的信心受到限制,因为缺乏关于不利影响阈值的定量数据。野外实验可以提供无影响或不利影响的“基准”,可用于验证从野外数据统计得出的阈值。为了确定大型藻类丰度对潮间带底栖动物群落的不利影响的基准,在美国加利福尼亚州的博德加港(BOD)和上纽波特湾(UNB)的两个地点进行了实验。在每个地点,24 个笼子维持着六种大型藻类处理,持续八周,藻垫深度分别为 0、1.0、1.5、2.5、3.5 和 5.0 cm,主要由绿藻属的富营养化形成的大型藻类组成。每两周,采集 10 厘米深的沉积物岩芯,并对底栖动物进行定量分析。在四个地点中的三个地点,1 厘米深的藻垫(相当于 110-120 克干重(dm)/平方米或 840-930 克湿重/m2)导致底栖动物数量在两周内减少至少 67%,物种丰富度减少至少 19%。损失归因于关键功能群的减少。在四个星期内,BOD 的一个地点的表面沉积食性动物被消灭,在 UNB 的一个地点的六个星期内被消灭,而 1 厘米厚的藻垫在 BOD 的第二个地点对悬浮食性动物和草食性动物产生负面影响。相比之下,UNB 的另一个地点不受大型藻类处理的影响,这可能是由于初始群落由高比例耐受恶劣环境的地下沉积食性动物组成。大型藻类丰度低至 110-120 g dm/m2 对底栖无脊椎动物产生了显著而迅速的负面影响,为大型藻类大量繁殖对大型底栖动物丰度和群落结构的不利影响提供了明确的基准,这两个指标是生态系统健康的标志。这些信息可以为富营养化河口的大型藻类丰度建立适当的指标提供信息。