Lakes and Watercourses

Lakes and Watercourses Lakes and Watercourses

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used to estimate the distribution of benthic vegetation, for example, since double the Secchi depth is regarded as a rough measure of compensation depth, ie, the depth at which photosynthesis does not occur. Only current conditions scales are given for the above parameters. Assessment of deviation from reference values is hindered by the absence of background data more than is the case with other quality parameters. Assessment of current conditions TABLE 12. CURRENT CONDITIONS: water colour Class Description Abs f 400/5 Colour figure (mgPt/l) 1 Clear, or hardly discoloured water ≤ 0.02 ≤ 10 2 Slightly discoloured water 0.02 – 0.05 10 – 25 3 Moderately discoloured water 0.05 – 0.12 25 – 60 4 Substantially discoloured water 0.12 – 0.2 60 – 100 5 Heavily discoloured water > 0.2 > 100 In lakes, classification of water colour is based on seasonal mean values (May – October) over one year, based on monthly readings taken in surface water (0.5 m) or in samples taken from several depths. Assessment of watercourses should be based on samples taken 12 times over one year. The assessment scale is intended to group water colour levels typical of Swedish lakes and watercourses and is not related to biological or microbial effects. Photometer readings of the absorbency of filtered water (0.45 µm membrane filter) in a 5 cm cuvette at a wavelength of 420 nm give greater accuracy than readings of water colour using a colour comparator, particular at low colour levels. Photometer readings are therefore preferable. The table shows a multiplication factor of 500, used to convert absorbency units (abs f 420/5 ) to a colour value. This factor involves an element of uncertainty. 33

TABLE 13. CURRENT CONDITIONS: turbidity Class Description FNU units 1 No or insignificant turbidity ≤ 0.5 2 Slightly turbid 0.5 – 1.0 3 Moderately turbid 1.0 – 2.5 4 Substantially turbid 2.5 – 7.0 5 Highly turbid > 7.0 In lakes, turbidity is classified using seasonal mean values (May – October) over one year, based on monthly readings taken in surface water (0.5 m) or in samples taken at several depths. Assessment of watercourses should be based on samples taken 12 times over one year. The assessment scale classifies group concentration levels typical of Swedish lakes and watercourses and is not related to biological or microbial effects. Turbidity readings using different methods yield somewhat different results. The previous Swedish standard expressed turbidity as FTU (formazine turbidity units). The present Swedish and ISO standard states readings in the form of FNU (formazine nephelometric units). Other methods involve readings expressed as NTU (nephelometric turbidity units) or JTU (Jackson turbidity units). For practical purposes, 1 FTU = 1 FNU = 1 NTU ≈ JTU. TABLE 14. CURRENT CONDITIONS: Secchi depth in lakes Class Description Depth (m) 1 Very great Secchi depth ≥ 8 2 Great Secchi depth 5 – 8 3 Moderate Secchi depth 2.5 – 5 4 Little Secchi depth 1 – 2.5 5 Very little Secchi depth < 1 34

used to estimate the distribution of benthic vegetation, for example, since<br />

double the Secchi depth is regarded as a rough measure of compensation<br />

depth, ie, the depth at which photosynthesis does not occur.<br />

Only current conditions scales are given for the above parameters.<br />

Assessment of deviation from reference values is hindered by the absence<br />

of background data more than is the case with other quality parameters.<br />

Assessment of current conditions<br />

TABLE 12.<br />

CURRENT CONDITIONS: water colour<br />

Class Description Abs f 400/5<br />

Colour figure<br />

(mgPt/l)<br />

1 Clear, or hardly discoloured water ≤ 0.02 ≤ 10<br />

2 Slightly discoloured water 0.02 – 0.05 10 – 25<br />

3 Moderately discoloured water 0.05 – 0.12 25 – 60<br />

4 Substantially discoloured water 0.12 – 0.2 60 – 100<br />

5 Heavily discoloured water > 0.2 > 100<br />

In lakes, classification of water colour is based on seasonal mean values<br />

(May – October) over one year, based on monthly readings taken in<br />

surface water (0.5 m) or in samples taken from several depths.<br />

Assessment of watercourses should be based on samples taken 12 times<br />

over one year. The assessment scale is intended to group water colour<br />

levels typical of Swedish lakes <strong>and</strong> watercourses <strong>and</strong> is not related to<br />

biological or microbial effects.<br />

Photometer readings of the absorbency of filtered water (0.45 µm<br />

membrane filter) in a 5 cm cuvette at a wavelength of 420 nm give<br />

greater accuracy than readings of water colour using a colour comparator,<br />

particular at low colour levels. Photometer readings are therefore<br />

preferable. The table shows a multiplication factor of 500, used to<br />

convert absorbency units (abs f 420/5 ) to a colour value. This factor<br />

involves an element of uncertainty.<br />

33

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