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Macroalgae and phytoplankton as indicators of ... - Naturstyrelsen

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The statistical analysis w<strong>as</strong> carried out on log-transformed variables (Figure<br />

4.2), <strong>and</strong> the common factor (b) w<strong>as</strong> estimated <strong>as</strong> 0.55 (±0.05). The sitespecific<br />

factors varied from 0.16 to 2.96, typically lower for co<strong>as</strong>tal sites<br />

with the exception <strong>of</strong> Dybsø Fjord <strong>and</strong> incre<strong>as</strong>ing <strong>as</strong> the estuaries/<br />

co<strong>as</strong>tal sites become more enclosed (Figure 4.3). Two sites, Nissum Fjord<br />

<strong>and</strong> Ringkøbing Fjord before change <strong>of</strong> sluice practice, had very high factors<br />

giving unrealistically high chla yields compared to TN when using<br />

Redfield ratios <strong>and</strong> a carbon:chla ratio <strong>of</strong> 50 for conversion. This indicates<br />

that additional nitrogen is introduced to these systems. In fact, both<br />

systems have been dominated by cyanobacteria (ca. 33% <strong>and</strong> 80% for<br />

Nissum Fjord <strong>and</strong> Ringkøbing Fjord, respectively) <strong>and</strong> this additional nitrogen<br />

input may have come from nitrogen fixation. Thus, the consequence<br />

<strong>of</strong> this is that chla-TN relationships <strong>as</strong> described here are not applicable<br />

to co<strong>as</strong>tal systems with a large proportion <strong>of</strong> nitrogen-fixing<br />

cyanobacteria, particularly if the proportion <strong>of</strong> cyanobacteria varies<br />

greatly from year to year.<br />

Figure 4.2 Summer chla versus winter-spring TN mean concentrations for 42 different sites. Solid line shows the estimated<br />

relationship averaged over all sites, <strong>and</strong> dotted lines show relationship with the lowest factor (Dybsø Fjord) <strong>and</strong> the highest<br />

factor (Ringkøbing Fjord before change <strong>of</strong> sluice practice).<br />

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