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Macroalgae and phytoplankton as indicators of ... - Naturstyrelsen

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Flensborg Fjord on the ranked scale, the response to nitrogen input is<br />

about 2-3 times larger than for open co<strong>as</strong>tal sites. The largest response to<br />

nitrogen input is observed for inner Odense Fjord, Nissum Fjord <strong>and</strong><br />

R<strong>and</strong>ers Fjord, sites strongly affected by riverine inputs. Overall the<br />

ranking <strong>of</strong> the sites by their slopes corresponds well to the expected influence<br />

from l<strong>and</strong>-b<strong>as</strong>ed nitrogen discharges.<br />

Figure 2.6 Estimated site-specific slopes in TN-nitrogen input relations <strong>and</strong> 95% confidence intervals for the estimate. Estimates<br />

have been sorted by incre<strong>as</strong>ing slopes.<br />

For the 39 different water bodies, reference conditions <strong>and</strong> boundary values<br />

between ecological status cl<strong>as</strong>ses were predicted from the regression<br />

model using fixed intercepts <strong>and</strong> site-specific slopes (Table 2.3). The uncertainty<br />

<strong>of</strong> these estimates includes a variance contribution from both<br />

the slope <strong>and</strong> the estimated common intercept <strong>of</strong> 15.46 µmol l -1 (±0.88).<br />

For the TN concentrations used in the macroalgae calculations the procedure<br />

is similar with the exception that TN annual means represent an<br />

entire year (July-June). Given this, we found values (Table 2.4) that were<br />

slightly lower than those used for chlorophyll due to generally lower TN<br />

levels in July-December compared to January-June.<br />

15

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