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Gaza beach is the only recreational area available for the local inhabitants of Gaza, Palestine. It is heavily polluted with treated, partially treated and untreated sewage from point and non-point sources. The majority of the population is below the age of 15, an age group vulnerable to gastrointestinal diseases and that usually restricts its activities to beach sand at the swash zone. A total of 5 sampling points along the Gaza beach were selected and monitored for one year (fortnightly). Microbial sand content was evaluated for faecal coliforms (FC) and faecal streptococci (FS) as well as Salmonella, Shigella and Vibrio. Seawater samples were subjected to similar evaluation. Pseudomonas, yeast and mold count were performed for all sand samples as possible sand pollution indicators. Higher faecal indicators (both FC and FS) were obtained in sand rather than in water almost in all locations. The frequency of Salmonella and Vibrio isolation was also higher in sand than in water despite the fact that only 10 grams of sand were used while one liter of seawater was collected. Statistically significant correlations were found between faecal coliform and streptococci on one side of the beach and Salmonella and Vibrio on the other side. Similar correlation was also detected between Pseudomonas levels and the isolation of Salmonella from sand samples.
The anthropogenic effect on faecal and chemical pollution at Bahir Dar Gulf of Lake Tana, Ethiopia was investigated in the period of October 2006 to February 2007. Faecal and physicochemical pollution levels were significantly increased and clearly discernible in the Bahir Dar Gulf locations as compared to presumptively anthropogenic uninfluenced reference locations near the outlet of the Blue Nile River of Lake Tana. One directly sewage influenced lake site at Bahir Dar Gulf was found to be excessively faecally polluted. The total pooled data set from the study for faecal coliforms, Escherichia coli and Clostridium perfringens spores ranged from not detectable (n.d.) to log 6.2 CFU, n.d. to log 6.1 CFU and n.d. to log 1.7 CFU per 100 ml, respectively. A high variation was also observable for the physicochemical parameters including the spectral absorption coefficient at 254 nm, ammonia, nitrite, nitrate, total dissolved solids, total suspended solids and pH values. Although the data have to be considered preliminary, it strongly points to the need for systematic water quality monitoring of Lake Tana and its potential impact sources. This is all the more important as the lake is the largest freshwater body in the country serving a multipurpose role and being identified as a growth corridor of the country.
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