Evans Chris D, Cooper David M, Juggins Steve, Jenkins Alan, Norris Dave
Centre for Ecology and Hydrology, Deiniol Road, Bangor, LL57 2UP, UK.
Sci Total Environ. 2006 Jul 15;365(1-3):167-85. doi: 10.1016/j.scitotenv.2006.02.037. Epub 2006 Mar 31.
Freshwater sensitivity to acidification varies according to geology, soils and land-use, and consequently it remains difficult to quantify the current extent of acidification, or its biological impacts, based on limited spot samples. The problem is particularly acute for river systems, where the transition from acid to circum-neutral conditions can occur within short distances. This paper links an established point-based long-term acidification model (MAGIC) with a landscape-based mixing model (PEARLS) to simulate spatial and temporal variations in acidification for a 256 km(2) catchment in North Wales. Empirical relationships are used to predict changes in the probability of occurrence of an indicator invertebrate species, Baetis rhodani, across the catchment as a function of changing chemical status. Results suggest that, at present, 27% of the river network has a mean acid neutralising capacity (ANC) below a biologically-relevant threshold of 20 microeq l(-1). At high flows, this proportion increases to 45%. The model suggests that only around 16% of the stream network had a mean ANC < 20 microeq l(-1) in 1850, but that this increased to 42% at the sulphur deposition peak around 1970. By 2050 recovery is predicted, but with some persistence of acid conditions in the most sensitive, peaty headwaters. Stream chemical suitability for Baetis rhodani is also expected to increase in formerly acidified areas, but for overall abundance to remain below that simulated in 1850. The approach of linking plot-scale process-based models to catchment mixing models provides a potential means of predicting the past and future spatial extent of acidification within large, heterogeneous river networks and regions. Further development of ecological response models to include other chemical predictor variables and the effects of acid episodes would allow more realistic simulation of the temporal and spatial dynamics of ecosystem recovery from acidification.
淡水对酸化的敏感性因地质、土壤和土地利用情况而异,因此,基于有限的定点样本,目前仍难以量化酸化的当前程度及其生物影响。对于河流系统而言,这个问题尤为严重,因为在短距离内就可能出现从酸性条件到接近中性条件的转变。本文将已建立的基于点的长期酸化模型(MAGIC)与基于景观的混合模型(PEARLS)相链接,以模拟北威尔士一个256平方公里集水区酸化的时空变化。利用经验关系预测指示无脊椎动物物种——红纹沼石蛾在整个集水区出现概率的变化,该变化是化学状态变化的函数。结果表明,目前,27%的河网平均酸中和能力(ANC)低于20微当量/升这一与生物相关的阈值。在高流量时,这一比例增至45%。该模型表明,在1850年,只有约16%的河网平均ANC < 20微当量/升,但在1970年左右硫沉降峰值时,这一比例增至42%。预计到2050年情况会有所恢复,但在最敏感的泥炭质源头地区,酸性条件仍会持续存在一段时间。预计在以前酸化的地区,河流对红纹沼石蛾的化学适宜性也会提高,但总体丰度仍将低于1850年模拟的水平。将基于地块尺度过程的模型与集水区混合模型相链接的方法,为预测大型异质河网和区域内酸化的过去和未来空间范围提供了一种潜在手段。进一步开发生态响应模型,纳入其他化学预测变量和酸事件的影响,将能更真实地模拟生态系统从酸化中恢复的时空动态。