Water conservation in textile industry
by: Muhammad Ayaz
Shaikh, Assistant Professor, College of Textile Engineering,
SFDAC.The textile Industry is in no way
different than other chemical industries, which causes pollution
of one or the other type. The textile industry consumes large
amount of water in its varied processing operations. In the
mechanical processes of spinning and weaving, water consumed is
very small as compared to textile wet processing operations,
where water is used extensively. Almost all dyes, specialty
chemicals, and finishing chemicals are applied to textile
substrates from water baths. In addition, most fabric
preparation steps, including desizing, scouring, bleaching, and
mercerizing use aqueous systems. According to USEPA a unit
producing 20,000 Ib / day of fabric consume 36000 liters of
water.
In textile wet processing, water is used mainly for two
purposes. Firstly, as a solvent for processing chemicals and
secondly, as a washing and rinsing medium. Apart from this, some
water is consumed in ion exchange, boiler, cooling water, steam
drying and cleaning.
Textile Industry is being forced to consider water
conservation for many reasons. The primary reasons being the
increased competition for clean water due to declining water
tables, reduced sources of clean waters, and increased demands
from both industry and residential growth, all resulting in
higher costs for this natural resource. Water and effluent costs
may in the more common cases, account for as much as 5% of the
production costs.
Water usage
Water usage at textile mills can generate millions of gallons
of dye wastewater daily. The unnecessary usage of water adds
substantially to the cost of finished textile products through
increased charges for fresh water and for sewer discharge.
The quantity of water required for textile processing is
large and varies from mill to mill depending on fabric produce,
process, equipment type and dyestuff. The longer the processing
sequences, the higher will be the quantity of water required.
Bulk of the water is utilized in washing at the end of each
process. The processing of yarns also requires large volumes of
water. The water usage of different purposes in a typical cotton
textile mill and synthetic textile processing mill and the total
water consumed during wet process is given in table 1 and table
2 respectively.


Wide variation is observed in consumption mainly due to the
use of old and new technologies and difference in the processing
steps followed types of machines used.

Every textile processor should have knowledge of the quantity
of water used for processing. The volume of water required for
each process is tabulated as under:

Washing efficiency
Washing process is characterized by its washing efficiency
that is the amount of the compound that is removed divided by
the total amount that could have been removed. Washing
efficiency is not directly dependent on the amount of water used
but is a function of:

- Temperature
- Speed of fabric in the washing range
- The properties of the fabric
- The properties of the washing range
Temperature
The temperature is important in washing because the
temperature influences;
- The viscosity of water. At a lower viscosity water can
better penetrate through the fabric and washing will become
more effective.
- The affinity of compounds. At a higher temperature the
affinity decreases and results in a better washing away of the
unwanted components.
- Migration of the components from the inner fibre to the
water around the fiber. This migration is important for the
total time the washing process will take.
Speed of fabric in the washing range
The speed of fabric in the washing range determines the
amount of water that is hanged in the fabric by passing a roller
in the washing compartment. That is the liquor that was in the
fabric before passing the roller with a high concentration of
the unwanted components that is replaced by the washing liquor
with a low concentration of the unwanted components.
The properties of the fabric
The properties of fabric influence the washing effectiveness
by the amount of water that can be pressed through the fabric
during washing. The openness of the fabric as well as the
openness of yarn determines the length of the way the unwanted
component has to migrate to the fluid that can be exchanged in
the washing process. In the washing process generally only very
little water from the pores between the fibres is exchanged when
the yarns are strongly twisted this will be practically zero. As
migration is a very slow process it will take much longer for
all the components to be washed out. The same holds more or less
for thicker yarns and heavy weight fabrics.
The properties of the washing range
The effectiveness of the washing range is determined by the
number of washing tanks, the number of compartments in each
tank, the diameter of the roller and the way the fabric is led
through the washing range. The washing effectiveness can be
improved by placing rollers on top of the top-rollers. This
squeeze off the excess water in the fabric and a better exchange
of washing liquid will be realized. Also at high speed these top
rollers will prevent water to be taken with the fabric to the
next compartment.
Water conservation and reuse
Water is expensive to buy, treat, and dispose. If the
industry does not have water conservation program, its pouring
money downs the drain. Now, water conservation and reuse are
rapidly becoming a necessity for textile industry. Water
conservation and reuse can have tremendous benefits through
decreased costs of purchased water and reduces costs for
treatment of wastewaters. Prevention of discharge violations as
a result of overload systems can be a significant inducement for
water conservation and reuse. By implementing water conservation
and reuse programs, the decision to expand the treatment
facilities can be placed on hold, and the available funds can
then be used for expansion or improvements to process equipment.
The first step in developing a water conservation and reuse
program is to conduct a site survey to determine where and how
water being used. It would be extremely helpful to develop a
spreadsheet and/ or diagram of the water usage with specific
details as shown below:
- Location and quantity of water usage.
- Temperature requirements.
- Water quality requirements, i.e. pH, hardness and
limitations on solid content, must meet clean water standards,
etc.
- Any special process requirements.
Water conservation measures
Water conservation measures lead to:
- Reduction in processing cost.
- Reduction in wastewater treatment cost.
- Reduction in thermal energy consumption.
- Reduction in electrical energy consumption.
- Reduction in pollutants load.
Water conservation significantly reduces effluent volume. A
water conservation program can cut water consumption by up to 30
percent or more, and the cost savings can pay for the required
materials in a very short time. Since the average plant has a
large number of washers, the savings can add up to thousands of
rupees per year. Other reasons for large effluent volume is the
choice of inefficient washing equipment, excessively long
washing circles and use of fresh water at all points of water
use.
The equipment used in a water conservation program is
relatively inexpensive, consisting in most cases of valves,
piping, small pumps, and tanks only. The operating costs for
these systems are generally very low. Routine maintenance and,
in some cases, electricity for the pumps, would be the major
cost components.
The payback period for a water conservation system will vary
with the quantity of water saved, sewer fees, and costs for raw
water and wastewater treatment. In addition to the direct cost
savings, a water conservation program can reduce the capital
costs of any required end-of-pipe wastewater treatment system.
Personnel from textile industry need to be aware of water
conservation potential so they can help their organization
realize the benefits.
Water conservation methods for
textile mills
Numerous methods have been developed to conserve water at
textile mills. Some of the techniques applicable to a wide
variety of mills are discussed.
Good Housekeeping
A reduction in water use of 10 to 30 percent can be
accomplished by taking strict house keeping measures. A walk
through audit can uncover water waste in the form of:
- Hoses left running.
- Broken or missing valves.
- Excessive water use in washing operations.
- Leaks from pipes, valves, and pumps.
- Cooling water or wash boxes left running when machinery is
shut down.
- Defective toilets and water coolers.
Good house keeping measures often carried out without
significant investments, but leading to substantial cost savings
and the saving of water, chemicals and energy. Good house
keeping measures are essential for a company, which is critical
about its own behaviors. Implementing the following can make
significant reductions in water use
- Minimizing leaks and spills.
- Plugging leakages and checks on running taps.
- Installation of water meters or level controllers on major
water carrying lines.
- Turn off water when machines are not operating.
- Identifying unnecessary washing of both fabric and
equipment.
- Training employees on the importance of water
conservation.
Water reuse
Water reuse measures reduce hydraulic loadings to treatment
systems by using the same water in more than one process. Water
reuse resulting from advanced wastewater treatment (recycle) is
not considered an in-plant control, because it does not reduce
hydraulic or pollutant loadings on the treatment plant.
Reuse of certain process water elsewhere in mill operations
and reuse of uncontaminated cooling water in operations
requiring hot water result in significant wastewater discharge
reductions. Examples of process water reuse include:
1. Reuse of water jet weaving wastewater
The jet weaving wastewater can be reused within the jet
looms. Alternatively, it can be reused in the desizing or
scouring process, provided that in-line filters remove fabric
impurities and oils.
2. Reuse of bleach bath
Cotton and cotton blend preparation are performed using
continuous or batch processes and usually are the largest water
consumers in a mill. Continuous processes are much easier to
adapt to wastewater recycling/reuse because the waste stream is
continuous, shows fairly constant characteristics, and usually
is easy to segregate from other waste streams.
Waste stream reuse in a typical bleach unit for
polyester/cotton blend and 100 percent cotton fabrics would
include recycling j-box and kier drain waste water to
saturators, recycling continuous scour wash water to batch
scouring, recycling washer water to equipment and facility
cleaning, reusing scour rinses for desizing, reusing mercerizes
wash water or bleach wash water for scouring.
Preparation chemicals, however, must be selected in such a
way that reuse does not create quality problems such as
spotting.
Batch scouring and bleaching are less easy to adapt to
recycling of waste streams because streams occur intermittently
and are not easily segregated. With appropriate holding tanks,
however, bleach bath reuse can be practiced in a similar manner
to dye bath reuse and several pieces of equipment are now
available that has necessary holding tanks.
3. Reuse of final rinse water from dyeing for dye bath
make-up
The rinse water from the final rinse in a batch dyeing
operation is fairly clean and can be used directly for further
rinsing or to make up subsequent dye baths. Several woven fabric
and carpet mills use this rinse water for dye bath make-up.
4. Reuse of soaper wastewater
The coloured wastewater from the soaping operation can be
reused at the back grey washer, which does not require water of
a very high quality. Alternatively, the wastewater can be used
for cleaning floors and equipment in the print and color shop.
5. Reuse of dye liquors
The feasibility of dye liquor reuse depends on the dye used
and the shade required on the fabric or yarn as well as the type
of process involved. It has already been applied whilst disperse
dyeing polyester, reactive dyeing cotton, acid dyeing nylon and
basic dyeing acrylic, on a wide variety of machines. However,
commission dyeing where the shades required are much more varied
and unpredictable would make the reuse of dye liquor difficult.
But, given the right conditions dye liquor could be reused up to
10 times before the level of impurities limits further use.
6. Reuse of cooling water
Cooling water that does not come in contact with fabric or
process chemicals can be collected and reused directly. Examples
include condenser-cooling water, water from water-cooled
bearings, heat-exchanger water, and water recovered from cooling
rolls, yarn dryers, pressure dyeing machines, and air
compressors. This water can be pumped to hot water storage tanks
for reuse in operations such as dyeing, bleaching, rinsing and
cleaning where heated water is required or used as feeding water
for a boiler.
7. Reusing wash water
The most popular and successful strategy applied for reusing
wash water is counter-current washing.

The counter-current washing method is relatively
straightforward and inexpensive. For both water and energy
savings, counter-current washing is employed frequently on
continuous preparation and dye ranges. Clean water enters at the
final wash box and flows counter to the movement of the fabric
through the wash boxes. With this method the least contaminated
water from the final wash is reused for the next-to-last wash
and so on until the water reaches the first wash stage, where it
is finally discharged. Direct counter-current washing is now
generally built into the process flow sheet of new textile
mills. It is also easy to implement in existing mills where
there is a synchronous processing operation.
Use of automatic shut-off valves
An automatic shut-off valve set to time, level, or
temperature controls the flow of water into a process unit. One
plant estimated that a reduction in water use of up to 20
percent could be achieved with thermally controlled shut-off
valves.
Use of flow control valves
A flow or pressure-reduction valve can significantly reduce
the quantity of water used in a wash or clean-up step. These
valves are particularly useful in cleaning areas where operators
are not always aware of the need for water conservation.
Flocculation of clean water of
pigment printing
A rotary screen printer uses as much water as a continuous
washing range. All this water is used to wash the belt, to rinse
the pipes and pumps and to clean the screens and squeegees. The
water does not come in contact with the fabric. When only
pigments are used for printing, it is relatively easy to
coagulate the pigments and let them settle. The result is the
clean water, which can be used for cleaning purposes.
Use single stage of processing
Knitted fabric process combined bleaching/scouring and dyeing
giving considerable saving in water. The scouring and bleaching
process takes place for 10-20 minutes and without draining the
bath the dyeing is carried out without any loss of depth of
colour value. In some cases the finishing process can also be
carried out along with the dyeing process.
Use of low material to liquor ratio
systems
Different types of dyeing machinery use different amounts of
water. Low liquor ratio dyeing machines conserve water as well
as chemicals and also achieve higher fixation efficiency but the
washing efficiency of some types of low liquor ratio dyeing
machines, such as jigs, is inherently poor; therefore, a
correlation between liquor ratio and total water use is not
always exact. Typical liquor ratios for various types of dyeing
machines are given below:

Water conservation measures in
dyeing equipment
Washing and rinsing are both important for reducing impurity
levels in the fabric to pre-determined levels. Water and
wastewater treatment prices are increasing, the optimization of
water use pays dividends. One possible option is to reduce rinse
water use for lighter shades. Here are some successful water
reduction projects in batch and continuous operations.
Winch Dyeing: Dropping the dye bath and avoiding overflow
rinsing could reduce water consumption reduced by 25%.
High and Low: Replacing the overflow with Pressure jet
dyeing batch wise rinsing can cut water consumption by
approximately 50%.
Beam Dyeing: About 60% of water preventing overflows during
soaking and rinsing may reduce consumption. Automatic controls
proved to be quite economical with a payback period of about
four months.
Jig Dyeing: A wide range of reductions ranging from 15% to
79% is possible by switching from the practice of overflow to
stepwise rinsing. Rinsing using a spray technique is also
effective.
Cheese Dyeing: A reduction of around 70% is possible
following intermittent rinsing.
Continuous Operation: A 20%-30% saving was realized by
introducing automatic water stops. Counter-current washing
proved to be the most effective method. Horizontal washing
equipment delivered the same performance as two vertical washing
machines, using the same amount of water.
References
- Bergenthal, J.F. “Wastewater recycle and reuse potential
for indirect discharge textile finishing mills”: Volume
1-Technical Report. U.S. Environmental Protection Agency.
- Waste reduction fact sheet, “Water conservation for
textile mills industrial pollution prevention program”. May
1993, NC division of pollution prevention and environmental
assistance.
- NIIR Board, The complete technology book on “Textile
processing with effluents treatment”, Asia pacific business
press Inc. I.S.B.N: 81-7833-050-4.
- Dr. Brent Smith, James Rucker, “Water and textile wet
processing, Part 1”, NCSU, Raleigh, NC.
- Edward Menezes, “Development in water treatment methods”,
Pakistan Textile Journal, September 2003.
- Brown & Caldwell, “Industrial water conservation
references of textile manufacturers and dyers”, California
department of water resources.
- Environmental pollution control: “Textile processing
industry”, Cincinnati, OH: U.S. Environmental Protection
Agency.
- Anton Luiken, Janet Mensink, Lecture at the APTPMA seminar
on “Environmental aspects of textile wet processing”, 2000.
- Jeffery D. Denit, Anne M. Gorsuch, Richard E. Williams,
“Effluent limitations guidelines and standards for the textile
mills point source category”, U.S. Environmental Protection
Agency Washington, D.C.
- Manual, “Better environmental management practices in
textile processing sector”, World Wide Fund for Nature-
Pakistan (WWF-P).
- Report 5, “Waste minimisation and best practice”, The
British Textile Technology Group, Ref: S5471, November 1999.
- Ms. Ilse Hendrickx, Gregory D. Boardman, “Pollution
prevention studies in the textile Wet processing industry”,
1995. Department of environmental quality office of pollution
prevention.
|