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CHAPTER 2     11                            11







                 LABORATORY VERSUS FIELD ANALYSIS

                            OF INVERTEBRATE SAMPLES





            Laboratory analysis includes
            sieving, sub-sampling, sorting,
            and identification of animals.


            Poor weather and light will affect biological data recorded
            from field sorting. The main benefit of laboratory analysis is
            that its errors are well understood and have been quantified.
            Because of that, samples to be analysed by RIVPACS,
            particularly those used for WFD status classification, must
            be sorted and identified in the laboratory under controlled
            conditions, not in the field.

            Measures of laboratory error for laboratory-analysed
            samples based on independent audit are incorporated
            in RICT (River Invertebrate Classification Tool). Audits of
            laboratory analyses of invertebrate samples by regulatory
            agencies in Great Britain also provide estimates of bias (the
            impact of non-random error on biotic indices, see Section 13)
            and quantitative information about error. Estimates of bias are
            incorporated in WFD status classification so that they can be
            accounted for in estimates of probability of class, and results
            can be adjusted to take account of variations in analytical
            quality.

            Analysis in the field is less accurate and less precise. It is   Field analysis is most effective when it is used with data
            not suitable for WFD status classification because far more   analyses that are optimised for field data. These improve
            precision is needed to differentiate good from moderate   efficiency and limit errors by concentrating on key taxa
            status reliably than is possible with field analysis. However,   and features that are suitable for field analysis (see, for
            field analysis is ideal where high precision is not needed,   example, Chapter 5 Section 3.1.26 – Rapid Appraisal
            such as rapid screening for gross pollution. It also allows   Key for detecting farm pollution). These methods tend to
            the proportion of living and dead animals to be recorded,   be accurate but less precise than laboratory methods.
            which can be important evidence for assessing the impact of   Biotic indices used for status classification, such as WHPT
            pollution. Because of that, samples collected for investigating   (Whalley Hawkes Paisley Trigg), are not designed for use
            major pollution incidents are often analysed in the field and   with field data and they include taxa that cannot be identified
            again in the laboratory.                          reliably in the field.


















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