Urresti-Estala Begoña, Gavilán Pablo Jiménez, Pérez Iñaki Vadillo, Cantos Francisco Carrasco
Facultad de Ciencias, Grupo de Geodinámica Externa, Universidad de Málaga, Campus de Teatinos s/n, 29071, Málaga, Spain.
Environ Sci Pollut Res Int. 2016 Aug;23(16):15990-6005. doi: 10.1007/s11356-016-6662-9. Epub 2016 May 4.
One of the key aspects introduced by the European Water Framework Directive 2000/60/EC (WFD) and developed by Groundwater Directive 2006/118/EC was the need to analyse pollution trends in groundwater bodies in order to meet the environmental objectives set in Article 4 WFD. According to this Directive, the main goal of "good status" should be achieved by the year 2015, and having reached this horizon, now is a suitable time to assess the changes that have taken place with the progressive implementation of the WFD. An extensive database is available for the Guadalhorce River basin, and this was used not only to identify in groundwater but also to draw real conclusions with respect to the degree of success in meeting the targets established for this main deadline (2015) The geographic and climate context of the Guadalhorce basin has facilitated the development of a variety of economic activities, but the one affecting the largest surface area is agriculture (which is practised on over 50 % of the river basin). The main environmental impacts identified in the basin aquifers arise from the widespread use of fertilisers and manures, together with the input of sewage from population centres. In consequence, some of the groundwater bodies located in the basin have historically had very high nitrate concentrations, often exceeding 200 mg/L. In addition, return flows, the use of fertilisers and other pressures promote the entry of other pollutants into the groundwater, as well as the salinisation of the main aquifers in the basin. In order to assess the hydrochemical changes that have taken place since the entry into force of the WFD, we performed a detailed trends analysis, based on data from the official sampling networks. In some cases, over 35 years of water quality data are available, but these statistics also present significant limitations, due to some deficiencies in the design or management; thus, data are missing for many years, the results are subject to seasonality effects, there are gaps in the historical records obtained by the monitoring networks and other shortcomings. The results obtained were analysed with the non-parametric Mann-Kendall test and revealed a general upward trend of pollutants in the areas affected by major pressures. In this analysis, we evaluated not only the increase or decrease in pollutants but also the different processes detected and the sources of pollution within the basin area. Our evaluation shows that robust measures should be taken in order to prevent further major degradation of groundwater quality and to enable "good quality" status to be achieved in future extensions of the WFD.
欧洲水框架指令2000/60/EC(WFD)引入并由地下水指令2006/118/EC进一步发展的关键方面之一,是需要分析地下水体中的污染趋势,以实现WFD第4条规定的环境目标。根据该指令,应在2015年前实现“良好状态”的主要目标,达到这一期限后,现在是评估随着WFD的逐步实施所发生变化的适当时机。瓜达尔霍河盆地有一个广泛的数据库,该数据库不仅用于识别地下水中的情况,还用于就实现这一主要期限(2015年)所设定目标的成功程度得出实际结论。瓜达尔霍盆地的地理和气候环境促进了各种经济活动的发展,但影响面积最大的是农业(在流域面积的50%以上从事农业活动)。该流域含水层中确定的主要环境影响来自化肥和粪肥的广泛使用,以及人口中心污水的排放。因此,该流域内的一些地下水体历史上硝酸盐浓度一直很高,经常超过200毫克/升。此外,回流、化肥的使用和其他压力促使其他污染物进入地下水,以及该流域主要含水层的盐碱化。为了评估自WFD生效以来发生的水化学变化,我们根据官方采样网络的数据进行了详细的趋势分析。在某些情况下,有超过35年的水质数据,但由于设计或管理方面的一些缺陷,这些统计数据也存在重大局限性;因此,多年数据缺失,结果受季节性影响,监测网络获得的历史记录存在空白以及其他缺点。使用非参数曼-肯德尔检验对所得结果进行分析,结果显示在受到主要压力影响的地区,污染物总体呈上升趋势。在该分析中,我们不仅评估了污染物的增加或减少,还评估了检测到的不同过程以及流域内的污染源。我们的评估表明,应采取有力措施,以防止地下水质量进一步严重恶化,并在WFD未来的扩展中实现“良好质量”状态。