RIBEIRO, P. C.; http://lattes.cnpq.br/8579267075943767; RIBEIRO, Pollyana Caetano.
Resumo:
Cianobacteria bloom in aquatic water bodies are main concern to the Water
companies due to their production and liberation of neuro and hepatic toxins which can
affect human health when water is used for several activities. This phenomenon is not
restricted to clean water bodies but also happens in waste stabilization ponds, a
hipereutrophic environment and is favored by certain climatic and operational
conditions. This research was carried out to investigate the causes of excessive
cianobacteria growth in some stabilization ponds in Paraíba State - Northeast Brazil,
particularly those of Sapé, Monteiro, Sousa and Cajazeiras municipalities. The
literature emphasizes that different intervals of N/P rate allows cianobacteria bloom. In
this work N/P rate were calculated using different forms of N and P. Wastewater
Treatment Plants (WTP) final effluents were monitored from August 2000 to May 2004
with samples analysis carried out at the Laboratory of Environmental Sanitation of the
Academic Unit of Civil Engineering - CTRN - UFCG. The variables analyzed were
water temperature, pH, dissolved oxygen, electric conductivity, BOD, COD, ammonia,
nitrate, soluble orthophosphate, total phosphorous and chlorophyll "a". Municipalities
climatic data (precipitation, insolation and air temperature) were supplied by Paraíba
State Water Adminístration Agency. Data analyses were carried out using Excel® 2003
available in Microsoft Office with descriptive statistical analysis and multiple
correlations. Monitoring data showed that dry and rainy seasons influenced variation of
final effluent quality. For raw sewage samples, most values N/P < 10 occurred when
ammonia/total phosphorous were used. When ammonia/ soluble orthophosphate was
used to estimate N/P rate, most values were in the 10-16 interval. In final effluent
samples no matter which nitrogen and phosphorous forms used to calculate N/P rate,
the prevailing rate was N/P < 10. Both rates favour algae and cianobacteria intensive
growth. Intensive cianobacteria growth were evident in Sapé, Monteiro, Sousa and
Cajazeiras WTP due to certain conditions such as iong insolation period, finai effluent,
temperature above 25°C and pH around 7,5. The excessive cianobacteria proliferation
happened in those systems configurated as primary facultative pond (except Monteiro
WTP) and intermittent feeding. Attention must be given to systems with these features
in tropical climate as they can favour the excessive growth of those microorganisms
particularly in final effluent is discharged into supply water bodies.