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STRIVE - Environmental Protection Agency

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3.3.3 Relationships between Chlorophyll-a,<br />

Temperature and Secchi Depth<br />

Chlorophyll-a concentrations greater than 5 µg.l-1 were<br />

generally reached when temperatures were near 18ºC<br />

(Fig. 3.6). Higher chlorophyll-a levels were associated<br />

with low Secchi depths, in particular between weeks<br />

5 and 10. The low chlorophyll-a concentrations<br />

observed at the beginning of the study coincided with<br />

high water clarity, whereas the lakes sampled near the<br />

end of the summer showed both low phytoplankton<br />

biomass and weak light penetration, suggesting the<br />

presence of humic substances or perhaps heavy<br />

loads of suspended matter in the water column<br />

concomitant to bad weather and rainfall.<br />

N. Touzet (2008-FS-EH-3-S5)<br />

Figure 3.6. Scatter plots between chlorophyll-a and temperature (a), and between chlorophyll-a and Secchi<br />

depth (b) in the lakes sampled during summer 2009.<br />

3.3.4 Trophic Status of Lakes and Associated<br />

Land Cover Type<br />

Contingency analysis was carried out to determine<br />

the presence of significant relationships between<br />

the nature of land cover and the trophic state of the<br />

25<br />

waterbodies sampled in the study area (Fig. 3.7).<br />

The analysis was performed using four trophic state<br />

classes (ultra-oligotrophic, oligotrophic, mesotrophic<br />

and eutrophic) and the three geographical zonation<br />

groups defined following examination of the indices<br />

data. When feasible, publicly available water body<br />

categorisation, previously carried out by the Irish<br />

EPA, was used for the lakes sampled (EPA Ireland,<br />

2008b). The trophic state of the remaining lakes was<br />

estimated using the chlorophyll-a concentrations<br />

and Secchi depth values determined in this study<br />

according to the eutrophication classification levels<br />

defined in OECD (1982). The contingency analysis<br />

showed a significant relationship between trophic<br />

status and the zonation groups (X = 17.35, p < 0.05,<br />

df = 6). A further significant relationship was found in<br />

relation to spatial distribution between trophic status<br />

and the clusters of river catchment (excluding lakes<br />

from clusters C and F) (X = 20.22, p < 0.05, df = 9,<br />

n = 46).

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