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Table L7: 271 Some South African Industrial water consumption data Including wastewater quality Information (continued). Industry Details Laundries Laundries in South Africa consume approximately 3,0 x 10 6 m 3 of water annually, of which 95% Is discharged as wastewater. The weighted mean SWI was 15,1 £ per kg of laundry washed. A wide range, namely, B,O - 5B,4 £ per kg was evident. Laundries with a rinse-water recycle procedure had a SWI of approximately 9 £ per kg, while firms without a rinse-water recycle facility hada SWI of some 30 £ per kg. A target SWI of B £ per kg and 20 £ per kg was suggested for rinse-water recycling and non rinse-water recycling firms respectively. The weighted mean SPL was B,B g COD per kg; 19,B g total dissolved solids per kg; 2,6 g suspended solids per kg, and 0,7 g ortho-phosphate (as PI per kg. A target SPL corresponding to these industry means was recommended for total dissolved solids and ortho-phosphate (as PI, while no target SPL values were suggested for COD and suspended solids, which depend on the type of material to be washed Metal finishing industry Metal finishing covers a wide variety of techniques, where electroplating, anodizing and phosphating processes were found to be the most water intensive categories of the industry as a whole. The SWI varied between 0,03 • 1,25 m 3 of water per "effective" m 2 of surface treated. A target SWI of 0,1 m 3 of water per effective m 2 of surface treated for firms with a monthly production in excess of 10 000 m 2 , and 0,2 m 3 of water per effective m 2 of surface treated (for firms with a monthly production of less than 10 000 m 2 1, was recommended. The SPL (based on total dissolved solids), was highly variable depending on the process concerned. Much of the pollution from metal finishing industries is caused by the dumping of process Solutions (which should be examined in the first instance to reduce water pollution) Soyrce: After Steffen, Robertson and Kirsten Inc., 1991. National industrial water and waste-water survey, WRC Report No. 145/1/91, Water Research Commission, Pretoria, 26 p. + app. See also: (i) Anonymous, 1989. Water supply guidelines for township development schemes in Johannesburg, Water and Gas Department, Johannesburg Corporation, Johannesburg, 21 p. + app. (Some brief water consumption data specific to the Johannesburg area, in terms of overall industrial consumption, are presented in the document).
1111.11." (ii) (iii) (iv) (v) (vi) 272 Funke. J.W.• 1969. Industrial water and effluent management: some aspects on conservation of water and effects of effluent disposal on the environment. Summerschool on Water Pollution and Water Reuse. Ref. No. W2/1I19/2. January 1969. University of Pretoria. Pretoria. 32 p. (The publication provides older water consumption data reflecting earlier production techniques for industries listed in the above table. as well as for the gold. steel and electricity generation industries. Consumptive use of water (total intake minus total return flow) data are also presented in the report). Similar (older) data can be found in Van Duuren. F.A. and Funke. J.W.• 1970. Optimization of water use by means of water quality and volume requirements. Water Year 1970. Convention on Water for the Future. (Department of Water Affairs). 16 - 20 November 1970, Pretoria. 8 p. According to the Commission of Enquiry into Water Matters which reported in 1970. the volume of water consumed per electricity unit sent out (at that time) from power stations. varied from 0.006 m 3 per kWh in old power stations to 0.004 m 3 per kWh in modern stations (Anonymous. 1986)*. More recent innovations have reduced water consumption even further. Anonymous (1986) noted that the water consumption at the ISCOR Pretoria works was 5 m 3 per tonne of steel produced. Funke. J.W.• 1990. The water requirements and pollution potential of South African gold and uranium mines. WRC Report No. KV 9/90. Water Research Commission. Pretoria. 172 p. Murray. K.A.• 1987. Wastewater Treatment and Pollution Control. Water Research Commission. Pretoria. 367 p. (The publication provides useful information on the mining; cellulose fibre; iron and steel; tanning; textile; brewing; wine/brandy. and sugar industries in terms of water consumption and water quality). Stander. G.J.• 1954. Waterbewaring en doeltreffende beplanning vir die maksimum-eksploitasie van Suid-Afrika se natuurlike hulpbronne. Tydskrif vir Wetenskap en Kuns. VOl 14(2). Nuwe Reeks. p. 162 177. (The paper is an historical overview of water consumption in South Africa. with reference to selected industrial and agricultural activities. A brief summary can be found in: Stander. G.J.• 1955. Water en watergebruik in Suid-Afrika. Tydskrif vir Wetenskap en Kuns. VOl 15(2). Nuwe Reeks. p. 220 - 224). Stander. G.J.• 1970. The potential of water reclamation in South Africa. Water Year 1970. Convention on Water for the Future. (Department of Water Affairs]. 16 - 20 November 1970. Pretoria. 6 p. (The paper contains older. although relevant. water reuse data). * See Anonymous. 1986. Management of the Water Resources of the Republic of South Africa, Department of Water Affairs. Pretoria. various pages.
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Table L7:<br />
271<br />
Some South African Industrial water consumption data Including wastewater quality Information (continued).<br />
Industry Details<br />
Laundries Laundries in South Africa consume approximately 3,0 x 10 6 m 3 <strong>of</strong> water annually, <strong>of</strong> which 95% Is discharged<br />
as wastewater. The weighted mean SWI was 15,1 £ per kg <strong>of</strong> laundry washed. A wide range, namely, B,O -<br />
5B,4 £ per kg was evident. Laundries with a rinse-water recycle procedure had a SWI <strong>of</strong> approximately 9 £ per<br />
kg, while firms without a rinse-water recycle facility hada SWI <strong>of</strong> some 30 £ per kg. A target SWI <strong>of</strong> B £ per<br />
kg and 20 £ per kg was suggested for rinse-water recycling and non rinse-water recycling firms respectively.<br />
The weighted mean SPL was B,B g COD per kg; 19,B g total dissolved solids per kg; 2,6 g suspended solids per<br />
kg, and 0,7 g ortho-phosphate (as PI per kg. A target SPL corresponding to these industry means was<br />
recommended for total dissolved solids and ortho-phosphate (as PI, while no target SPL values were suggested<br />
for COD and suspended solids, which depend on the type <strong>of</strong> material to be washed<br />
Metal finishing industry Metal finishing covers a wide variety <strong>of</strong> techniques, where electroplating, anodizing and phosphating processes<br />
were found to be the most water intensive categories <strong>of</strong> the industry as a whole. The SWI varied between<br />
0,03 • 1,25 m 3 <strong>of</strong> water per "effective" m 2 <strong>of</strong> surface treated. A target SWI <strong>of</strong> 0,1 m 3 <strong>of</strong> water per effective<br />
m 2 <strong>of</strong> surface treated for firms with a monthly production in excess <strong>of</strong> 10 000 m 2 , and 0,2 m 3 <strong>of</strong> water per<br />
effective m 2 <strong>of</strong> surface treated (for firms with a monthly production <strong>of</strong> less than 10 000 m 2 1, was<br />
recommended. The SPL (based on total dissolved solids), was highly variable depending on the process<br />
concerned. Much <strong>of</strong> the pollution from metal finishing industries is caused by the dumping <strong>of</strong> process Solutions<br />
(which should be examined in the first instance to reduce water pollution)<br />
Soyrce: After Steffen, Robertson and Kirsten Inc., 1991. National industrial water and waste-water survey, WRC Report No.<br />
145/1/91, Water Research Commission, Pretoria, 26 p. + app.<br />
See also: (i) Anonymous, 1989. Water supply guidelines for township development schemes in Johannesburg, Water and Gas<br />
Department, Johannesburg Corporation, Johannesburg, 21 p. + app. (Some brief water consumption data specific<br />
to the Johannesburg area, in terms <strong>of</strong> overall industrial consumption, are presented in the document).