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FORUM FOR  ENVIRONMENTAL
MANAGEMENT AND RESEARCH - NEPAL

 

 

WATER POLLUTION

Drinking Water situation in Nepal
Source % of People Served
Piped water 31.5
Well water 7.1
Hand pump 31.9
Spring water (Kuwa) 18.9
River/stream 7.2
Others 3.4
Population with Access to Safe water
42 %

Source: MOH, 1996 and xMHPP. 1996

Water Pollution

Water pollution through natural processes is insignificant in Nepal. Domestic sewage and industrial effluents are the major contributors of water pollution. Haphazard urbanisation and inadequate sewerage facilities have accelerated the discharge of domestic liquid wastes without any treatment. Almost all the urban areas have no wastewater treatment facilities. The cumulative effects of wastewater discharge have a striking negative impact, particularly, in the rivers flowing through the Kathmandu Valley. The holy river Bagmati is biologically dead due to discharge of such domestic and industrial wasters, particularly in the stretch flowing through urban areas.

Biological contamination is generally noticed in the supplied drinking water as well. Frequent incidence of water-borne diseases indicates the deterioration of the drinking water quality in both urban and rural areas.

Although the contribution of the manufacturing industries to the gross domestic product (GDP) is estimated to be around 10 per cent, most of them discharge the effluents and solid wastes without any treatment. According to the latest Census (1996//97) of industries, the number of establishments and persons engaged in all VDCs were about 1,594 and 92,344 as against 1,963 and 1,04,364 in all Municipalities. Compared to the previous 1991/92 Census, carpet and rugs, garments, bricks, distilleries and printing establishments have decreased in numbers during 1996/97 Census.

With a concentration of 56.76 per cent of total manufacturing establishments, the Central Development Region (CDR) is found to be the most busy region in manufacturing activities. The region shares 70.54 per cent of the total employees, and 73.04 per cent of total wages and salaries. It has also shared 76.04 per cent of the total value added with 66.84 per cent of input and 70.5 per cent of the total output.

In contrast to the CDR, the Far-Western Development Region (FWDR) shares only 3.74 per cent of the total number of manufacturing establishments.

Localised industrial pollution is also on the rise. Wastewater is directly discharged on to the terrestrial and aquatic systems without any treatment. The wastewater generally contains a high load of oxygen demanding wastes, disease causing agents, synthetic organic compounds, plant nutrients, inorganic chemical and minerals, and sediments (Devkota and Neupane, 1994). Total industrial wastes have been estimated at 0.076 million tons of TSP, 8.557 million cubic meter of wastewater, 5.7 thousand tons of BOD, 9.6 thousand tons of TSS and 22 thousand tons of solid wastes. Industrial TSP release in the Kathmandu Valley exceeds the total load discharged in all other development regions. A recent sample survey of 36 industries throughout the Kingdom revealed that the population equivalent (PE) of industrial effluent ranges from 416 to 9,540 (Devkota, 1997; Table 2.8.3). It is generally accepted that local human PE is about 50 gram per day.

Table 2.8.3 Characteristics of Industrial Wastewater
Maximum observed values
Sector/source Sample size pH Conductivity (ms/cm) Salinity Temp   TDS BOD COD TSS O/G PE
  (. /.) (0C)   (mg/l) (mg/l) (mg/l) (mg/l) (mg/l)  
Iron and steel galvanizing
Pickling waste 3 1.54 2.39 1.1 44.4 2850   n.a 96 30 n.a.  
Soap manufacturing                        
Combine final outlet 3 14 153 220 43.8 174800   8220 33500 17400 90 822
Pulp and paper 2                     1713
Black liquor   10.4 39 25.2 32.9 31350   32450 13600 15200 2200  
White liquor   9.34 1290* 1.9 35.7 9000   1824 9833 2044 50  
Vegetable oil/ghee                        
Neutralization wash 4 9.08 4.1 4.1 48.8 10850   4717 5320 5350 580 2000
Textile
Combine final outlet 4 6.36 2210* 0.1 33.4 2210   732 5750 140 9.8 4392
Brewing
Combine final outlet 2 8.04 521* 0.1 29.4 278   514 725 90 n.a 1542
Distillery Spent wash 1 4.4 18.13 10.9 84.5 18550   13040 54000 11230 n.a 9540
Beverage/soft drink                        
Combine final outlet 3 9.05 2.7 1.3 33.2 1236   196 300 66 1.4 720
Food processing                        
Combine final outlet 3 4.91 863* 0.2 36.7 350   2372 3800 1200 12.4 1423
Leather tanning
Combine final outlet 3 13.58 3 1.4 29 9900   1035 6500 8267 1230 1035
Carpet dyeing 4                     1142
Light spent dye bath   4.71 2.62 1.4 84.2 1072   648 860 280 4.2  
Dark spent dye bath   4.82 5.08 2.8 82.1 3595   2208 2300 400 5.8  
Carpet washing 4                     416
Sulfuric acid + bleaching 1.02 21.6 13.1 27.1 1200   184 456 672 4  
Caustic soda wash 14 10.4 6 28.6 4531   230 540 320 8.7  
Sulfuric acid wash 1.07 19.87 12 28.1 4115   210 620 294 5.5  
Detergent wash 2.53 2.85 1.4 28.1 316   207 330 132 4.3  

Source: Devkota, 1997 Note : TDS: total dissolved solid; BOD: biological oxygen demand; COD: chemical oxygen demand; . TSS: total suspended solid; O/G: oil and grease; PE: population equivalent. * unit in ms/cm

Although urbanisation and industrial development is at an infancy stage, water pollution is rapidly increasing in most of the areas of the country, both in urban and rural areas. Water quality is degraded through the discharge of untreated domestic wastewater and industrial effluents. Continued efforts are required to minimise pollution load through the enforcement of pragmatic standards for specific types of industries, provision of incentives for use of cleaner technologies, and effluent treatment facilities. Industries should also be promoted to comply with the environmental regulatory measures. Industrial operators should also be encouraged to minimise the waste load through good house keeping practices, appropriate water management, stocking of required raw materials, optimum use of chemicals, and adoption of recovery and reuse process and complying with discharge standards

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