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5.9 Integrated Water Conservation - Bhilai Steel Plant, India
Introduction
Bhilai and its adjoining areas in the Durg and Raipur Districts of
Madhya Pradesh State in India experience severe water shortages. For
example, in 1988, the Bhilai area, in the vicinity of the steel plant,
received only 636 mm of rainfall, compared to the long-term average
rainfall of 1 300 mm. As a result, the reservoirs of the Mahanadi
Reservoir Project and Tandula Complex, which supply water to Raipur and
Durg Towns and village nistari tanks for irrigation, industries and
drinking purposes, were reduced in volume to 22.3% of their full supply
capacity, or to a live storage of 391 million m3. In comparison, the
annual consumption of water at the Bhilai Steel Plant during the previous
financial year (1987-88) was 297 million m3. Given the available storage
in the reservoirs in 1988, it became essential to reduce the consumption
of water until the next monsoon.
Technical Description
As a first step in preparing a comprehensive strategy for managing water
resources at the Bhilai Steel Plant, an inventory was prepared identifying
areas in the plant where reuse and recycling could be achieved, and an
audit conducted of water uses to identify areas in the plant where water
consumption could be reduced. In terms of these studies, a number of rain
water outlets in the plant, carrying substantial quantities of effluent,
which had a potential to be recycled, into the Marida-I Reservoir, were
intercepted and diverted to various pump houses so that their recycling
was possible. Similarly, the ash slurry from Power Plants-I and -II was
conveyed to an Ash Pond (No. 2 ) for settlement of solids and recycling of
the clarified water. Approximately 1 000 m3/hr was conserved in this
manner and returned into the pressure mains for reuse in the Rolling Mills
area of the plant. Likewise, the Horizontal Secondary Settling Tanks
(HSST) and the overflow channels were found to be poorly maintained,
resulting in substantial spillages, which were eliminated by cleaning the
return channels so as to ensure that the settled water is contained within
the rain water outlet system for later recovery. Additional reenforced
concrete pipes were laid to interconnect the rain water outlets to avoid
any effluent spills. In addition to the effluent recycling from selected
outlets, seepage from the Marida-I Reservoir was also intercepted and
routed via the pump house into the recycling system, and water discharges
from the Plate Mill, previously routed to a subsoil soakaway, were
diverted as make up water to the circulating water pump house at the Plate
Mill and to the CAS-III Pump House. The water supply to the townships was
also checked and the supply hours were reduced to an half hour in the
morning and an half hour in the evening. Such a practice did not cause any
serious inconvenience in the townships but helped conserve 1 000 m3/hr of
water.
In addition to the recycling schemes, other actions designed to reduce
water consumption were also taken, including stopping the water supply to
any Mill that was taken out of production for whatever reason; stopping
overflows from the suction pumps in the pump houses and cooling towers;
improving maintenance of, and stopping leaks in, industrial water supply
lines; isolating damaged lines to stop wastage; minimizing the use of
water by the Horticulture Department for gardening; and, using posters and
public announcements to raise awareness of the need for water conservation
amongst staff and township residents.
Extent of Use
All the major schemes were completed within five months. There was no
major resistance to the water conservation measures from the staff of the
plant or from the residents of the townships towards water conservation
efforts.
Operation and Maintenance
The major operation and maintenance aspects considered were "good
housekeeping" at the facility, constant monitoring and preventive
maintenance to minimize losses through leakages, improving operations and
supervision of the pumping stations, and monitoring of concentrations of
potential pollutants in the effluents and the quality of the Maroda-I
Reservoir.
Level of Involvement
The public sector was completely responsible for the implementation of
the recycling and conservation programme at the steel plant. However,
community involvement was important in conserving water in the residential
townships.
Costs
The capital costs incurred for water conservation at this facility
included procurement and installation costs associated with the upgrading
of pumping facilities prior to implementation of the recycling programme.
In addition, costs were incurred for pump operation, for cleaning and
maintenance of the effluent and water pipes, and for descaling and the
removal of sludge from pipes. The actual cost figures are not available.
Effectiveness of the Technology
Due to the implementation of the water conservation strategies, the
industrial make up water consumption was reduced from 16 740 m3/hr to 3
000 m3/hr at the additional cost of pumps, interconnecting pipes, cleaning
and pump operation. Table 35 shows that the industrial water consumption
per tonne of steel produced has been reduced from 52.2 m3 to 9.3 m3 , a
substantial reduction in water use.
Advantages
The advantages of implementing water conservation measures include a
lower water supply costdue to a five- to tenfold decrease in water
consumption, the ability to continue operations despite reduced water
resource availability, the conservation of 14 000 m3/hr of water, an
heightened awareness of the need for water conservation amongst the plant
staff as well as the residents of the township, and a priority being given
to water conservation by the senior management.
Disadvantages
Amongst the disadvantages were an increase in hardness, and suspended
and dissolved solids and chloride concentrations in the plant effluent
which required increased monitoring to meet pollution control and process
water quality standards and an increased frequency of backwashing ion
exchange columns, and which led to a marginally greater degree of
impairment of water quality (particularly, increased turbidity) in the
Maroda-I Reservoir. To mitigate the latter impact, sodium metaphosphate
has been added to the Maroda-I Reservoir to inhibit turbidity and
discourage scaling in the pipelines by forming a film within the pipes. A
further disadvantage of this technology was that, as the water
conservation measures use pumping as the principal means of circulating
the recycled waters, the water conservation system incurred higher energy
costs.
TABLE 42. Reduction in Water Consumption at the
Bhilai Steel Plant.
| Period |
Total water consumption m3/hr |
% Savings |
Industrial water consumption per tonne of crude steel |
| April to August 1988 (average) |
25 550 |
- |
52.2 |
| September 1988 |
21 245 |
16.8 |
48.3 |
| October 1988 |
19 852 |
22.3 |
36.9 |
| November 1988 |
13 863 |
45.7 |
18.8 |
| December 1988 |
11 448 |
55.2 |
12.2 |
| January 1989 |
9 165 |
64.1 |
5.2 |
| February 1989 |
12 278 |
51.9 |
10.3 |
| March 1989 |
10 771 |
57.8 |
4.8 |
| April 1989 |
12 777 |
50.0 |
9.5 |
| May 1989 |
13 728 |
46.3 |
12.3 |
| June 1989 |
11 453 |
55.2 |
10.3 |
Further Development of the Technology
Water conservation efforts within public sector enterprises such as
Bhilai Steel clearly demonstrate that significant opportunities exist for
the conservation of large quantities of water, in this case 14 000 m3/hr,
using relatively simple methods such as better maintenance, reuse of
process water, and recycling. However, it is also important to
concomitantly explore water reduction, through technological
modifications, for example, in addition to focussing on reuse. Such a
strategy, in the longer term, could reduce the relatively high operating
costs of the recycling-based scheme to a great extent.
Information Sources
Tambe, G.N. 1990. Journal of Indian Water Works Association,
Jan-March, pp. 33-36.
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