Abstract:
Water quality of many rivers in the developing countries is under serious threat of
degradation and Pakistan is no exception to this. The river water may be polluted by the
effluents stemming from industrial, municipal, agricultural or mining activities. The most
affected rivers are those flowing through the urban areas and subjected to anthropogenic
activities. The river Chenab, traversing near the industrial cities and municipalities, is
largely used for constant disposal of untreated effluents in the Punjab province of
Pakistan. Consequently water quality of the river degrades particularly in the low flow
months.
This study was conducted to monitor, assess and model the water quality (WQ) of
river Chenab over a length of 292 km from its entrance in Pakistan at Marala. The
monitoring program was conducted during low flow months (October to March) of years
2006-7 and 2007-8. Water samples were collected from seven locations along the river
and all the contributing drains as well. These samples were analyzed for a variety of
physical, chemical and biological quality parameters.
The data collected from monitoring as well as from secondary sources were
utilized in three phases of analysis. In the first phase water quality indices (WQIs) were
calculated using CWQI 1.0 model developed by Canadian Council of Ministers of the
Environment (CCME). Three intended uses of river water i.e. drinking, aquatic life and
irrigation were incorporated for WQI calculations at selected points along the river. In the
second phase, mathematical model (MIKE 11 model developed by Danish Hydraulic
Institute (DHI), Denmark) was formulated to simulate a conservative WQ parameter
(salinity of river water). Two non-conservative WQ parameters (dissolved oxygen (DO)
and biochemical oxygen demand (BOD)) were modeled in third phase of the analysis
using MIKE 11 model.
The results of WQI revealed that the lower river reach (185 to 233 km) was more
polluted than the upper 185 km segment. In this river reach, overall WQI ranking were
poor for drinking and marginal for both irrigation and aquatic life. The WQIs for all three
uses were ranked poor at sampling point located at 233 km below Marala headworks. The
calibrated model for salinity simulated the most saline condition in the river during the
months with minimum flow (i.e. November and December). The results also depicted
high salinity in the downstream river reach receiving polluted effluents from two major
drains (Faqirian Sillanwali and Chakbandi drain). Finally the model was calibrated and
validated for DO and BOD. The results of simulations indicated DO depletion and high
BOD levels in the downstream river reaches particularly from 200 to 270 km.
Different scenarios were also tested to predict the river water salinity by varying
discharge of the drains. The salinity of river water was found highly sensitive to the
amount of effluents added by the surface drains. The study of management scenarios for
BOD suggested that the maximum water quality improvement can be achieved if there is
no diversion of flow from the river coupled with 60 percent reduction in BOD of the
drain effluents through treatment.