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Lakes and Watercourses

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TABLE 32.<br />

DEVIATION from reference value, potentially toxin-producing cyanobacteria<br />

Class Description No. of potentially toxic genera/<br />

reference value<br />

1 No or insignificant deviation < 1<br />

3 Significant deviation 1 – 1.5<br />

5 Large to very large deviation ≥ 1.5<br />

TABLE 33.<br />

DEVIATION from reference value, Gonyostomum semen<br />

Class Description Recorded volume/reference value<br />

1 No or insignificant deviation ≤ 1.0<br />

2 Slight deviation 1.0 – 10<br />

3 Significant deviation 10 – 25<br />

4 Large deviation 25 – 50<br />

5 Very large deviation > 50<br />

of 15 µg/l. The reference values have then been based on correlations<br />

with the total biomass of planktonic algae. The biomass in August has<br />

been determined by calculating the relationship with the seasonal mean<br />

from the Environmental Monitoring Programme database. The volume<br />

of diatoms in April/May is based on the maximum figure in the database<br />

for mesotrophic lakes having a nutrient status of 15 µg/l (tot-P). Two<br />

reference lakes form the basis for assessment of forest lakes. Maximum<br />

figures from a number of published studies have been used for mountain<br />

lakes, since the Environmental Monitoring Programme database was<br />

inadequate.<br />

Reference values for potentially toxic genera have been set using the<br />

Environmental Monitoring Programme database. Essentially, the<br />

reference value for Gonyostomum semen is considered to be an absence of<br />

viable communities. The reference value has been set using lakes where<br />

there is an influx of humic water capable of carrying limited quantities of<br />

Gonyostomum, which will temporarily survive in a given habitat.<br />

56

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