Strong effects of occasional drying on subsequent water clarity and cyanobacterial blooms in cool tropical reservoirs

In semi‐arid regions, the construction of small reservoirs is important in alleviating water shortage, although many have poor water quality with high turbidity and dense blooms of algae and cyanobacteria, and there are large differences in the ecology of such reservoirs. We took advantage of two ex...

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Published in:Freshwater biology Vol. 59; no. 4; pp. 870 - 884
Main Authors: Teferi, Mekonen, Declerck, Steven A. J, De Bie, Tom, Lemmens, Pieter, Gebrekidan, Abraha, Asmelash, Tsehaye, Dejenie, Tadesse, Gebrehiwot, Kindeya, Bauer, Hans, Deckers, Jozef A, Snoeks, Jos, De Meester, Luc
Format: Journal Article
Language:English
Published: Oxford Blackwell Science 01-04-2014
Blackwell Publishing Ltd
Blackwell
Wiley Subscription Services, Inc
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Summary:In semi‐arid regions, the construction of small reservoirs is important in alleviating water shortage, although many have poor water quality with high turbidity and dense blooms of algae and cyanobacteria, and there are large differences in the ecology of such reservoirs. We took advantage of two exceptionally dry years in northern Ethiopia to study the effect of a dry period and the associated fish kills on reservoir ecology and water quality. We studied 13 reservoirs, seven of which dried up in 2009. Four of the latter dried up again in 2010. We monitored the ecology of these reservoirs from 2009 to 2011, hypothesising that the pattern of reservoir drying would explain ecological differences among them. Reservoirs that refilled after drying had a significantly lower fish biomass, lower biomass of phytoplankton (expressed as chlorophyll‐a) and cyanobacteria (Microcystis), clearer water, greater macrophyte cover and lower nutrient concentrations than reservoirs that did not dry. Although the differences in water quality were most striking in the wet season after a drying event, there were persistent effects on reservoir ecology. The three categories of reservoirs we distinguished, based on their behaviour in 2009 and 2010, also showed differences in 2004, a year during which none of the reservoirs dried out. While drying evidently results in better water quality, we could not disentangle the effects of drying per se from that of reductions in fish biomass. The total combined effect was highly significant in all 3 years, whereas the separate effects of drying and loss of fish were only significant in 2004. Our results suggest that differences in water quality and ecology among reservoirs depend on their propensity to dry out. Drying might be used as a restoration measure to reduce potentially harmful cyanobacterial blooms in reservoirs.
Bibliography:http://dx.doi.org/10.1111/fwb.12312
ark:/67375/WNG-2DPH6G4F-W
Table S1. ANOVA results for the effect of reservoir categories (reservoirs that did not dry out in 2009 nor in 2010; reservoirs that dried out only in 2009; reservoirs that dried out in both 2009 and 2010) on the morphometric and regional characteristics of the studied reservoirs. Table S2. Results of the redundancy analysis: amount of variation in ecological variables explained by reservoir drying for the sampling campaigns of 2009, 2010 and 2011, and for the data collected in 2004 by Dejenie et al. (). Figure S1. Map of Ethiopia and the location of the 13 reservoirs in Tigray region, northern Ethiopia. Figure S2. Morphometric and regional characteristics of the 13 reservoirs in relation to drying (black: no drying in 2009 nor 2010; light grey: drying only in 2009; dark grey: drying in both 2009 and 2010).
istex:ED07B1DB97E0CEC4E751B22C4E437040D3413FE0
Flemish Institutional University Cooperation (IUC)
ArticleID:FWB12312
ObjectType-Article-1
SourceType-Scholarly Journals-1
ObjectType-Feature-2
content type line 23
ISSN:0046-5070
1365-2427
DOI:10.1111/fwb.12312