Vigiak Olga, Udias Angel, Pistocchi Alberto, Zanni Michela, Aloe Alberto, Grizzetti Bruna
European Commission, Joint Research Centre (JRC), via E Fermi 2749, 21020 Ispra, VA, Italy.
ARHS Developments Italia S.r.l., Via F.lli Gabba 1/A, 20121 Milano, Italy.
Ecol Indic. 2021 Jul;126:107684. doi: 10.1016/j.ecolind.2021.107684.
Understanding how anthropogenic pressures affect river ecological status is pivotal to designing effective management strategies. Knowledge on river aquatic habitats status in Europe has increased tremendously since the introduction of the European Union Water Framework Directive, yet heterogeneities in mandatory monitoring and reporting still limit identification of patterns at continental scale. Concurrently, several model and data-based indicators of anthropogenic pressures to freshwater that cover the continent consistently have been developed. The objective of this work was to create European maps of the probability of occurrence of river conditions, namely failure to achieve good ecological status, or to be affected by specific pervasive impacts. To this end, we applied logistic regression methods to model the river conditions as functions of continental-scale water pressure indicators. The prediction capacity of the models varied with river condition: the probability to fail achieving good ecological status, and occurrence of nutrient and organic pollution were rather well predicted; conversely, chemical (other than nutrient and organic) pollution and alteration of habitats due to hydrological or morphological changes were poorly predicted. The most important indicators explaining river conditions were the shares of agricultural and artificial land, mean annual net abstractions, share of pollution loads from point sources, and the share of upstream river length uninterrupted by barriers. The probability of failing to achieve good ecological status was estimated to be high (>60%) for 36% of the considered river network of about 1.6 M km. Occurrence of impact of nutrient pollution was estimated high (>60%) in 26% of river length and that of organic pollution 20%. The maps are built upon information reported at country level pursuant EU legal obligations, as well as indicators generated from European scale models and data: both sources are affected by epistemic uncertainty. In particular, reported information depend on data collection scoping and schemes, as well as national knowledge and interpretation of river system pressures. In turn, water pressure indicators are affected by heterogeneous biases due to incomplete or incorrect inputs and uncertainty of models adopted. Lack of effective reach- and site-scale indicators may hamper detection of locally relevant impacts, for example in explaining alteration of habitats due to morphological changes. The probability maps provide a continental snapshot of current river conditions, and offer an alternative source of information on river aquatic habitats, which may help filling in knowledge gaps. Foremost, the analysis demonstrates the need for developing more effective continental-scale indicators for hydromorphological alterations and chemical pollution.
了解人为压力如何影响河流生态状况对于制定有效的管理策略至关重要。自欧盟水框架指令出台以来,欧洲河流生境状况的相关知识有了大幅增加,但强制性监测和报告中的异质性仍然限制了在大陆尺度上对模式的识别。与此同时,已经开发出了一些基于模型和数据的、能持续覆盖整个大陆的淡水人为压力指标。这项工作的目的是创建欧洲河流状况发生概率的地图,即未能达到良好生态状况或受到特定普遍影响的概率地图。为此,我们应用逻辑回归方法将河流状况建模为大陆尺度水压指标的函数。模型的预测能力因河流状况而异:未能达到良好生态状况的概率以及营养物和有机污染的发生情况预测得较好;相反,化学(除营养物和有机物质外)污染以及水文或形态变化导致的生境改变预测得较差。解释河流状况的最重要指标是农业用地和人工用地的比例、年平均净取水量、点源污染负荷的比例以及上游无屏障河流长度的比例。在约160万公里的河流网络中,估计有36%的河流未能达到良好生态状况的概率较高(>60%)。营养物污染影响的发生率在26%的河流长度中估计较高(>60%),有机污染的发生率为20%。这些地图基于各国根据欧盟法律义务报告的信息以及从欧洲尺度模型和数据生成的指标构建:这两种来源都受到认知不确定性的影响。特别是,报告的信息取决于数据收集范围和方案,以及各国对河流系统压力的了解和解释。反过来,水压指标也受到由于输入不完整或不正确以及所采用模型的不确定性而导致的异质性偏差的影响。缺乏有效的河段和站点尺度指标可能会妨碍对局部相关影响的检测,例如在解释形态变化导致的生境改变方面。概率地图提供了当前河流状况的大陆概况,并提供了有关河流水生生境的另一种信息来源,这可能有助于填补知识空白。最重要的是,分析表明需要为水文形态变化和化学污染开发更有效的大陆尺度指标。