5 Scientific and management recommendations

48 The coastal waters have many uses. Almost the entire fisheries industry of Tanzania for example, is artisanal and is based within the inshore waters. The coastal waters are also important for recreation activities, for tourism development, aquaculture and for transport. Many of these activities require good water quality. The picture that emerges from the various studies show that in general the coastal waters in many parts of Tanzania are in a pristine condition. The exception is coastal areas bordering major tows and cities that are recipients of untreated municipal and industrial wastes and those receiving agricultural wastes. These include the main coastal towns of Dar es Salaam, Tanga, Mtwara and Zanzibar. In Zanzibar, faecal coliform and total coliform levels of up to 70100 ml and numerous thousands per ml of seawater respectively have been reported in the waters fronting the Zanzibar Municipality Mohammed, 1997. Nutrient levels are also higher than normal for tropical seawaters indicating anthropogenic inputs. Concentrations of nitrate of up to 7.8 µ-at Nl and phosphate levels of 4.0 µ-at Nl have been reported Anderson, 1994. Likewise,it has been reported that there is a proliferation of macroalgae in Tanga coastal waters due to excess nutrient loadings from discharges from a fertiliser factory and from the municipality Munisi, 1999. Coastal pollution in Tanga is also caused by discharge of effluents from sisal decorticating plants in the area. Up to twenty plants discharge their wastes onto the coast via the Pangani, Sigi, MruaziMnyuzi and Mkurumzi Rivers Shilungushela, 1993. In Dar es Salaam, domestic waste is the most serious source of pollution. The west generated by 15 of the city residents who are connected to the sewer system is discharged into the sea untreated. As a result, the coastal waters off the city especially the harbour area is heavily polluted. Discharges untreated sewage in Dar es Salaam has resulted in high faecal and total coliform levels in the same areas. The situation is made worse by a broken sewer pipe which discharges untreated sewage on sandy-mud flats near the harbour which is said to threaten invertebrates and fish Bryceson, 1981, Bryceson et al, 1990. It has also been reported that chlorinated organic compounds are at alarming levels in the harbour areas as are heavy metals, Pb, Zn and Cu Machiwa, 1992. The harbour area also suffers from oil pollution from the refinery at Kigamboni, and industrial wastes from Keko, Chang’ombe, Kurasini, Mtoni and Temeke. These discharge heavy metal, pesticide, organic, and paint wastes into the nearby area Bryceson, 1992. Msimbazi River and Creek are also among the most polluted water bodies in Dar es Salaam. The river and creek receives large quantities of untreated domestic wastes from the city’s residents in addition to industrial wastes from various industries. The river and creek receive such pollutants as dyes and paint wastes and strong alkalis from textile factories, oil and tars, from vehicle depots and power stations, organic wastes from breweries and meat plants. Other industrial and agricultural chemicals that pollute the river and creek include heavy metals, PCBs, cyanides, pesticides, and detergents Bryceson, et al, 1992. Other coastal areas of Tanzania outside the major cities and townships though free from domestic wastes do suffer from input of agricultural wastes, including pesticides and fertilisers, via rivers and streams. Most major rivers in the country drain agricultural lands and deposit their waste loads on the coast. Unfortunately, this area of concern has not received sufficient attention in the literature. Riverdischarges on coastal areas also carry with them industrial wastes. An example cited in the literature is Kilombero River, which transport wastes from the Mufindi Pulp and Paper Mill from the hinterland to the coast Bryceson et al 1990. The coastal waters of Tanzania are also subjected to input of heavy loads of sediment especially in areas where major rivers enter the sea. Even though such inputs can be a result of natural events such as storm events and rains in upland areas, poor agricultural practices have been known to play a leading role in water quality degradation due to sedimentation Bryceson, 1981. A direct consequence of this is the smothering of corals and other organisms as well the reduction of aesthetic value of the water thus making it less attractive for such activities as tourism as well as for general recreational activities.

2. 5 Scientific and management recommendations

49 There is no specific scientific recommendation given in the literature reviewed for this report. However, recommendations for management purposes have been given in a number of papers and reports. An important recommendation given in various reports is the need for the treatment of municipal waste before it is disposed of into the sea. In view of this recommendation, some reports have recommended the installation of primary waste treatment facilities to facilitate initial waste treatment before discharge. Many reports have strongly recommended the promotion of local awareness of the dangers of pollution and thehealth risk associated with the problem. Specifically, Chaggu 1993, in her study at Majumbasita area, has recommended that that there should be formulated guidelines on the design and construction of wells and pit latrines with the view to reduce pollution in the area. She also recommended that people should be discouraged from using shallow hand-dug wells and that a monitoring program to study the fluctuation of ground water levels and quality should be initiated. The study further recommended thatthe public should be advised on the health risks associated with using water from shallow wells. In order to alleviate the pollution problem in the coastal waters of Zanzibar, Walvoord 1993 recommended that leaks in sewage disposal pipes should be repaired and that faecal coliform concentrations in the water be reduced below health risk levels. Walvoord further recommended that the public is made aware of the risk of swimming in sewage contaminated waters. Similar recommendations as above were given by Anderson 1994 and Mohammed et al 1993. Anderson recommended the rehabilitation of the Zanzibar sewerage system to reduce further pollution of Zanzibar coastal water. Mohammed et al 1993 recommended that the construction of discharge pipes should be such that it observes current patterns in the area of concern so that sewage is flushed out to the open sea. Another useful recommendation was given by Powell 1997, who studied ocean sewage pollution and composting toilets in Zanzibar. In that study it was recommended that the use of composting toilets be promoted in order to reduce the volume of sewage discharged into the sea and hence contamination risks. It should be noted, however, that not a single city or town in Tanzania has a sewage treatment facility and most of these citiestowns discharge their waste untreated into the environment. Dar es Salaam has a few stabilisation ponds. For the long-term sustainability of the coastal zone it is important to develop better facilities including treatment plants. 2.6 Information gaps 2.6.1