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STRIVE - Environmental Protection Agency

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

Figure 3.35. Succession of spherical cyanobacteria inferred from denaturent gradient gel electrophoresis<br />

(DGGE) analysis in Lough Corrib and Ballyquirke Lough (a) together with the grouping of samples based on<br />

hierarchical clustering (b).<br />

Figure 3.36. Segregation of the denaturent gradient gel electrophoresis (DGGE) bands for spherical<br />

cyanobacteria (a) according to their maximum intensity and frequency of occurrence in both Lough Corrib<br />

and Lough Ballyquirke. Segregation of stations in the two lakes based on their spherical cyanobacteria<br />

richness and abundance (b).<br />

with those from August significantly greater than those<br />

from June and July (ANOVA, F = 13.02, p < 0.01).<br />

Individual bands from groups B, C and D were<br />

successfully excised from the gels and re-amplified<br />

prior to purification and sequencing. The occurrence<br />

of the indicator bands was assessed in relation to<br />

47<br />

environmental descriptors using Fisher’s exact test<br />

(Table 3.9). In particular, bands 15, 22, 28, 46, 49 and<br />

52 for spherical cyanobacteria showed, for each lake,<br />

significant correlations with the descriptors pertaining<br />

to the time of the summer, surface chlorophyll-a<br />

levels, light penetration and inorganic nitrogen levels.

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