Abstract

The representativeness of aquatic ecosystem monitoring and the precision of the assessment results are of high importance when implementing the EU’s Water Framework Directive that aims to secure a good status of waterbodies in Europe. However, adapting monitoring designs to answer the objectives and allocating the sampling resources effectively are seldom practiced. Here, we present a practical solution how the sampling effort could be re-allocated without decreasing the precision and confidence of status class assignment. For demonstrating this, we used a large data set of 272 intensively monitored Finnish lake, coastal, and river waterbodies utilizing an existing framework for quantifying the uncertainties in the status class estimation. We estimated the temporal and spatial variance components, as well as the effect of sampling allocation to the precision and confidence of chlorophyll-a and total phosphorus. Our results suggest that almost 70% of the lake and coastal waterbodies, and 27% of the river waterbodies, were classified without sufficient confidence in these variables. On the other hand, many of the waterbodies produced unnecessary precise metric means. Thus, reallocation of sampling effort is needed. Our results show that, even though the studied variables are among the most monitored status metrics, the unexplained variation is still high. Combining multiple data sets and using fixed covariates would improve the modeling performance. Our study highlights that ongoing monitoring programs should be evaluated more systematically, and the information from the statistical uncertainty analysis should be brought concretely to the decision-making process.

Highlights

  • Environmental monitoring is the cornerstone of evidencebased environmental management

  • The need for representative environmental monitoring programs has been encountered in European member states in the implementation of the Water Framework Directive (WFD; EC 2000)

  • The RSE% varied from the median of 6% for waterbodies in the Gulf of Finland inner archipelago (Ss, nWB = 3) to 19% for the Bothnian Bay outer coastal waters (Pu, nWB = 5) and to 32% for a one waterbody in the Bothnian Sea outer coastal waters (Seu)

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Summary

Introduction

Environmental monitoring is the cornerstone of evidencebased environmental management. For many existing water quality monitoring programs, sampling takes place at fixed sampling locations and is carried out at regular intervals This approach is generally justified by the need for standard time series, but it can produce data that is either too excessive or insufficient in time or space in the light of the assessment and management objectives (Levine et al 2014). A falsely assessed good status may result in no allocation of water protection resources, which may have other consequences to society. To address this sort of misclassification, WFD requires the member states to determine the precision and the confidence of the classification (Anonymous 2003b, Annex I). The most dominant errors, sources of variation, in the status class indicators have to be identified and quantified

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