Abstract
Benthic invertebrates are the most commonly used organisms used to assess ecological status as required by the EU Water Framework Directive (WFD). For WFD-compliant assessments, benthic invertebrate communities are sampled, identified and counted. Taxa × abundance matrices are used to calculate indices and the resulting scores are compared to reference values to determine the ecological status class. DNA-based tools, such as DNA metabarcoding, provide a new and precise method for species identification but cannot deliver robust abundance data. To evaluate the applicability of DNA-based tools to ecological status assessment, we evaluated whether the results derived from presence/absence data are comparable to those derived from abundance data. We analysed benthic invertebrate community data obtained from 13,312 WFD assessments of German streams. Broken down to 30 official stream types, we compared assessment results based on abundance and presence/absence data for the assessment modules "organic pollution" (i.e., the saprobic index) and "general degradation" (a multimetric index) as well as their underlying metrics. In 76.6% of cases, the ecological status class did not change after transforming abundance data to presence/absence data. In 12% of cases, the status class was reduced by one (e.g., from good to moderate), and in 11.2% of cases, the class increased by one. In only 0.2% of cases, the status shifted by two classes. Systematic stream type-specific deviations were found and differences between abundance and presence/absence data were most prominent for stream types where abundance information contributed directly to one or several metrics of the general degradation module. For a single stream type, these deviations led to a systematic shift in status from 'good' to 'moderate' (n = 201; with only n = 3 increasing). The systematic decrease in scores was observed, even when considering simulated confidence intervals for abundance data. Our analysis suggests that presence/absence data can yield similar assessment results to those for abundance-based data, despite type-specific deviations. For most metrics, it should be possible to intercalibrate the two data types without substantial efforts. Thus, benthic invertebrate taxon lists generated by standardised DNA-based methods should be further considered as a complementary approach.
Highlights
Status assessment of freshwater ecosystems is frequently performed with biological indicators
Ecological status class (ESC) estimates inferred from presence/absence data and abundance data were congruent in 76.6% of all cases (10,191 of 13,312 comparisons; Fig 2, Table 1)
Different ecological status class (ESC) were observed in 23.4% of all cases; 12% of presence/absence ESCs were one class lower than originally inferred and 11.2% of presence/absence ESCs were one class higher
Summary
Status assessment of freshwater ecosystems is frequently performed with biological indicators. They are of particular importance in Europe, where the Water Framework Directive (Directive 2000/60/EC; WFD) requires EU member states to achieve ‘good ecological status’ for all water bodies by 2027, defined as a ‘slight deviation from undisturbed conditions.’. Ecological status is determined based on biological quality elements (BQEs), i.e., organism groups that reflect aquatic ecosystem integrity by responding to various pressures rather than the intensity of a single pressure. The assessment procedure typically involves the standardised sampling of the BQE community, enumeration of taxa and estimating taxon abundance. Based on the resulting taxa lists, metrics are calculated and compared to reference values derived from undisturbed reference sites or through a modelling approach [2]. The resulting score is translated into an ecological status class (ESC) of high, good, moderate, poor, or bad
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