Demars Benoît O L, Edwards Anthony C
The Macaulay Institute, Craigiebuckler, Aberdeen AB15 8QH, Scotland, UK.
Sci Total Environ. 2009 Jan 1;407(2):975-90. doi: 10.1016/j.scitotenv.2008.09.012. Epub 2008 Nov 1.
A brief summary of the historical developments relating to plant distribution and aquatic macrophyte-nutrient indices provided a means of assessing the general context and validity of previous assumptions. This has particular current relevance because of the prominent use of bioindicators for defining nutrient enrichment. A survey of 161 sites distributed across two broadly contrasting groups of rivers (circum-neutral versus alkaline) recorded 110 species of aquatic macrophytes and these have been statistically analyzed to (i) rank and separate the individual effects of local environmental conditions and spatial isolation on species distribution in the two contrasting groups of sites; (ii) calculate a macrophyte index based on plant cover and species indicator values (Mean Trophic Rank, MTR); and finally (iii) investigate the implications for biomonitoring. Chemical, physical and hydrological site attributes together with spatial isolation, each explained a significant and at least partially independent influence over plant species distribution. It was extremely difficult, however, to separate the single effects of different site attributes on plant distribution. While some plant species are more restricted to certain environmental conditions, many appeared indifferent to the range of those being tested. The role played by nutrients (nitrogen (N) and phosphorus (P)) were either mostly indistinguishable from other site attributes (e.g., nitrate from conductivity) or subordinate (e.g., soluble reactive phosphorus, ammonium). It is therefore very unlikely that macrophyte species composition could provide a reliable bioindicator of the surrounding nutrient (N, P) status. The calculation of the plant index illustrated this unreliability by showing that strong correlations existed with many environmental variables, not just inorganic N and P.
对与植物分布及水生大型植物 - 营养指标相关的历史发展进行简要总结,提供了一种评估先前假设的总体背景和有效性的方法。鉴于生物指标在定义营养富集方面的突出应用,这一点在当前尤为重要。一项对分布在两组形成鲜明对比的河流(中性与碱性)中的161个站点的调查记录了110种水生大型植物,并对这些数据进行了统计分析,以(i)对当地环境条件和空间隔离对两组对比站点中物种分布的个体影响进行排名和区分;(ii)基于植物覆盖度和物种指示值(平均营养等级,MTR)计算大型植物指数;最后(iii)研究对生物监测的影响。化学、物理和水文站点属性以及空间隔离,各自对植物物种分布都解释了显著且至少部分独立的影响。然而,要区分不同站点属性对植物分布的单一影响极其困难。虽然一些植物物种更局限于特定环境条件,但许多物种似乎对所测试的环境范围并不在意。营养物质(氮(N)和磷(P))所起的作用,要么大多与其他站点属性难以区分(例如,硝酸盐与电导率),要么处于次要地位(例如,可溶性活性磷、铵)。因此,大型植物物种组成极不可能提供周围营养物质(N、P)状况的可靠生物指标。植物指数的计算通过表明其与许多环境变量存在强相关性,而非仅仅与无机N和P相关,说明了这种不可靠性。