Efficient sampling methodologies for lake littoral invertebrates in compliance with the European Water Framework Directive

Lake shores are characterised by a high natural variability, which is increasingly threatened by a multitude of anthropogenic disturbances including morphological alterations to the littoral zone. The European Water Framework Directive (EU WFD) calls for the assessment of lake ecological status by monitoring biological quality elements including benthic macroinvertebrates. To identify cost- and time-efficient sampling strategies for routine lake monitoring, we sampled littoral invertebrates in 32 lakes located in different geographical regions in Europe. We compared the efficiency of two sampling methodologies, defined as habitat-specific and pooled composite sampling protocols. Benthic samples were collected from unmodified and morphologically altered shorelines. Variability within macroinvertebrate communities did not differ significantly between sampling protocols across alteration types, lake types and geographical regions. Community composition showed no significant differences between field composite samples and artificially generated composite samples, and correlation coefficients between macroinvertebrate metrics calculated with both methods and a predefined morphological stressor index were similar. We conclude that proportional composite sampling represents a time- and cost-efficient method for routine lake monitoring as requested under the EU WFD, and may be applied across various European geographical regions

Numerical simulation of dissolved oxygen in coastal lagoons Case study: El Gouna, Egypt

Preservation of water quality in coastal areas has become an urgent challenge especially upon considering the increasing anthropogenic impacts, the expansion of urban areas and the predicted climate change in the upcoming decades. Dissolved oxygen (DO) may be considered the most important parameter to study the quality of water, in which the preservation of a reasonable rate of DO is essential for a healthy aquatic life. Herein, the water quality considering dissolved oxygen in coastal lagoons located in El Gouna, Egypt, is investigated using the TELEMAC-2D WAQTEL module. The simulation focused on the effects of the increasing water temperature on the quantity of DO, as lower levels of DO are expected in case of high temperatures. Studying the DO values and the sensitivity analysis of the affecting parameters helps to prevent and control anoxic problems in shallow areas, which occur if the DO concentration is less than 0.5 mg/l

Water Framework Directive Intercalibration Technical Report: Central Baltic Lake Benthic invertebrate ecological assessment methods

One of the key actions identified by the Water Framework Directive (WFD; 2000/60/EC) is to develop ecological assessment tools and carry out a European intercalibration (IC) exercise. The aim of the Intercalibration is to ensure that the values assigned by each Member State to the good ecological class boundaries are consistent with the Directive’s generic description of these boundaries and comparable to the boundaries proposed by other MS. In total, 83 lake assessment methods were submitted for the 2nd phase of the WFD intercalibration (2008-2012) and 62 intercalibrated and included in the EC Decision on Intercalibration (EC 2013). The intercalibration was carried out in the 13 Lake Geographical Intercalibration Groups according to the ecoregion and biological quality element. In this report we describe how the intercalibration exercise has been carried out in the Central Baltic Lake Benthic invertebrate group.JRC.H.1-Water Resource

Morphological alterations of lake shores in Europe: A multimetric ecological assessment approach using benthic macroinvertebrates

Besides pollution, lakes are affected by human alterations of lake-shore morphology. However, ecological effects of such alterations have rarely been studied systematically. Hence, we developed tools to assess the ecological effects of anthropogenic morphological alterations on European lake-shores based on pressure-specific response patterns of littoral macroinvertebrate community composition. Littoral invertebrates were sampled from 51 lakes in seven European countries. Sampling covered a range of natural to heavily morphologically degraded sites including natural shorelines, recreational beaches, ripraps and retaining walls. Biological data were supplemented by standardized morphological data that were collected via a Lake Habitat Survey (LHS) protocol and subsequently used to develop a morphological stressor index. Two biotic multimetric indices were developed based on habitat-specific samples (Littoral Invertebrate Multimetric based on HAbitat samples, LIMHA) and composite samples (Littoral Invertebrate Multimetric based on COmposite samples, LIMCO) through correlations with the morphological stressor index. Similarity analyses showed strong spatial differences in macroinvertebrate community composition between four main geographical regions, i.e. Western, Northern, Central and Southern Europe. The morphological stressor index as well as LIMCO and LIMHA have been developed for each geographical region specifically, thereby optimizing correlations of LIMCO and LIMHA with the respective morphological stressor index. The metric composition of LIMCO and LIMHA and their correlation coefficients with the morphological stressor index are comparable to existing national and regional methods that assess morphological lakeshore degradation via macroinvertebrate communities. Hence, LIMCO and LIMHA indices constitute a new stressor-specific assessment tool that enables comparable lake morphology assessment across Europe, as it has been developed involving a uniform methodology followed by regionalized optimization. These tools fulfil the standards of the EU Water Framework Directive and thus may complement existing assessment approaches used in lake monitoring focusing solely on lake eutrophication so far. (c) 2013 Elsevier Ltd. All rights reserved

Micropollutants

More than half of the human population currently lives in urban areas and according to the United Nations, cities will be the living space of an additional 2.5 billion people by the year 2050 (UN, 2015b). The proportion and speed of this urban growth increase the pressure on water resources, and this is often seen negatively. However, this challenge can also be a chance to substantially improve the quality of life in urban areas, if we consider how we want to live tomorrow and actively shape our future. As a group of interdisciplinary young scientists authoring the current science policy report, we agreed that we want to live in cities where sustainable, integrated watershed management guarantees public health and environmental safety. This requires sanitation and rainwater management, solutions for dealing with contaminants, such as micropollutants, as well as information flows and public involvement in water management. Integrated watershed management as part of urban planning takes into account interdisciplinary relationships and connects different sectors, for example city administration, health providers and water managers. It also ensures access to sustainable, adaptable, effective and resilient rain and wastewater management, which includes the specific needs of vulnerable groups. Such a rain and wastewater management considers water reuse as a possibility to increase the available water supply. A growing number and increasing concentration of micropollutants in the aquatic environment are a health risk. It is important to understand their fate and effects and to develop appropriate management strategies. In such decision-making processes, all aspects of water management should be included and local stakeholders involved. Moreover, comprehensive and optimized information flows improve the understanding of water-related problems and must be used to help communities to set priorities, take action and assume responsibilities. Education, capacity building and community engagement are particularly important for creating ownership, identification with water resources and environmental consciousness. Further research is needed in these areas to better understand challenges and chances of water management in growing urban areas and to develop scientifically based solutions. This scientific knowledge will build the basis for policy-making and implementation of actions in urban water management. In this way, we believe a better and more desirable urban environment can be achieved for future generations