纽芬兰岛两个天然湖泊和一个施肥湖泊中选定底栖无脊椎动物类群的密度、生物量和产量

K. Clarke, R. Knoechel
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引用次数: 0

摘要

大多数关于底栖生物群落实验扰动的研究在进行不同处理之间的比较时,采用简单的数值丰度估计(Rosenberg& Resh 1993, Benke 1994)。虽然在许多情况下是有效的,但数量丰度受到繁殖和死亡之间平衡的影响,而每一个都可能独立地对扰动作出反应。简单的数值估计也不能反映个体大小的差异,这可能是由于生长速度的提高而造成的。次级产量估计考虑到繁殖、生长和死亡(Benke 1994),因此可能是生态系统变化的更有力的指标,并使我们更好地了解变化发生的原因。第二次产量估计很少报告,可能是因为它们需要大样本量和劳力密集的重量测定。因此,在中生态营养物富集实验中,底栖生物群落产量通常被忽略,而在全湖营养物富集实验中,底栖生物产量估计几乎不存在。当底栖生物产量的估计已经报告了关于实验性营养添加的结果是相互矛盾的。Peterson et al.(1993)观察到初始生长率增加,但在冻土带河流系统中,由于“自上而下”的过程(捕食),总次生产量没有增加。Aagaard(1982)在一次全湖富集实验中报道了2种中游物种的密度增加,但这些增加和产量估计都在单按年变化所预期的范围内,因此,由于养分富集的影响尚不清楚。我们的研究有两个主要目标。首先,记录了纽芬兰3个小湖泊中底栖大型无脊椎动物的生物量和主要分类群的产量,并将这些信息与文献中发现的其他估计相结合。据我们所知,这是第一次尝试计算纽芬兰这些栖息地的二次产量估计,尽管它们对高价值鲑鱼物种的总体产量很常见且很重要(Dempson et al. 1996)。我们的第二个目标是记录整个湖的营养富集及其对底栖生物次生生产的影响之间的关系。这一目标的工作假设是,营养丰富的生态系统中营养负荷的增加会增加初级生产力,这反过来又会增加底栖动物的生产力。底栖生物的反应可以表现为数量的增加(Clarke et al. 1997)和/或增长率的增加(更大的尺寸),这两者都应反映在种群生产估算中。
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Density, biomass, and production of selected benthic invertebrate taxa in two natural lakes and one fertilized lake in insular Newfoundland
Most studies of experimental perturbation of the benthiccommunity employ simple estimates of numerical abundancewhen making comparisons among treatments (Rosenberg& Resh 1993, Benke 1994). Although valid in manyinstances, numerical abundance is influenced by the balancebetween reproduction and death, each of which may respondindependently to the perturbation. Simple numerical esti-mates also cannot reflect differences in individual size thatmay result from growth rate enhancement. Secondary pro-duction estimates take reproduction, growth, and death intoaccount (Benke 1994) and thus may be more powerful indi-cators of ecosystem change and give us a better understand-ing of why changes are occurring. Secondary production esti-mates are infrequently reported, probably because theyrequire large sample sizes and labour-intensive weight deter-minations.Thus, benthic community production has usually beenneglected in mesocosm nutrient enrichment experiments andbenthic production estimates are almost non-existent inwhole-lake nutrient enrichment experiments. When benthicproduction estimates have been reported with respect toexperimental nutrient additions the results have been con-flicting. Peterson et al.(1993) observed initial growth rateincreases, but total secondary production did not increase dueto “top-down” processes (predation) in a tundra river system.Aagaard (1982) reported density increases for 2 chirono-mid species during a whole-lake enrichment experiment, butthese increases and the production estimates were reported asbeing within the limits expected by annual variation alone,and thus the effect due to the nutrient enrichment was notclear.Our study had 2 main objectives. First, to document thebenthic macroinvertbrate biomass and production of thedominate taxa in 3 small Newfoundland lakes and to put thisinformation in context with respect to other estimates foundin the literature. To our knowledge this is the first attempt atcalculating secondary production estimates for these habitatsin Newfoundland despite them being common and importantto the overall production of highly valued salmonid species(Dempson et al. 1996).Our second objective was to document the relationshipbetween whole-lake nutrient enrichment and its effect onbenthic secondary production. The working hypothesis forthis objective was that the increase in nutrient load to theenriched ecosystem would increase primary productivity,which in turn would increase the productivity of the benthos.Benthic responses could be manifested as numericalincreases (Clarke et al. 1997) and/or growth rate increases(larger size), both of which should be reflected in populationproduction estimates.
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