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Environmental Aspects in Textile Industry: Ecological Hazards and Remedial Measures

A study on environmental impact of textile industry and its remedies

Among many pollution-creating industries, textile has a larger share in terms of its impact with regard to noise, air, and effluent. It is, therefore, felt worthwhile to study the environmental hazards associated with various operations of textiles. In this paper, pollution arising out of noise and air is discussed. Areas of concern and their appropriate rectifying procedures are also taken into account.

Ecological degradation happens in natural fiber right from cultivation to finishing of the ultimate product. Prominent parameters and the possible package of corrective measures are highlighted. Synthetic fiber industry is not an exception to environmental pollution and therefore various pollution-creating activities are pointed out. Management of various textile wastes is also mentioned in this paper.

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Categorization of Textile Waste

The textile industry covers a wide range of manufacturing processes and technologies to design the required shape of the final product. But during the course of various process flows, there is an obvious generation of wastes, which are classified into four categories namely, hard to treat wastes, dispersible wastes, hazardous or toxic wastes and high volume wastes [14].

Hard to Treat Waste

These include colour, metals, phenols, certain surfactants, toxic organic compounds, pesticides, as well as phosphates. Major sources are:

  • Colour and metals – dyeing operation
  • Phosphates            – dyeing operation
  • Surfactants            – non-biodegradable organic materials

Dispersible Waste

A prominent source of dispersible wastes in textile wet processing is the following: Print paste, lint, coating operation, solvent, waste stream from continuous dyeing, printing, finishing etc.

High Volume Waste

High volume wastes are sometimes a problem for the textile processing units. These include water from preparation and dyeing stages, alkaline wastes from the preparation, salt, cutting room waste, knitting oils and warp sizes. These wastes sometimes can be reduced by recycling or reuse as well as by process and equipment modifications.

Hazardous or Toxic Wastes

The impact on the environment of such kind of wastes is significant. They include metal, chlorinated solvents, non-degradable surfactants and other non-biodegradable or volatile organic materials. These wastes originate often from non-process operations, such as machine cleaning.

Waste-Management

The textile industry encompasses a range of unit operation covering a variety of natural and synthetic fibres to produce fabrics. Various parameters such as turbidity, acidity, alkalinity, total dissolved solids, BOD, metal content, toxic substances etc. are benchmarked so as to ensure that the effluent water before being released into city sewage, stream, river or sea is not harmful to human, animal or plant life. With the concept to bring the parameters of effluent water to acceptable standards, the effluent is treated. The appropriateness of their choice and sequence is critical for the success of the treatment plant.

Treatment of Textile Waste

Three types of process are normally used for the treatment and recycling of effluent from the textile industry. These are physicochemical, biological and membrane process.

Figure 1. Flowchart of typical water recycle plant
Figure 1. Flowchart of typical water recycle plant

Physico-chemical processes remove suspended and colloidal impurities, to coagulate and flocculate reactively, disperse and vat dyes and to facilitate their removal by sedimentation. The removal is a function of entrapment within a voluminous precipitate consisting primarily of the coagulant itself. Result of the addition of chemicals is the net increase in the dissolved constituents in the wastewater. Coagulants usually added include alum, lime etc. [15]. These processes offer a good pre-treatment to the downstream biological and membrane processes.

Biological processes used to remove dissolved organics from effluent and thus to reduce chemical and biochemical oxygen demands of the effluent. This is achieved biologically wherein bacteria are used to convert the colloidal and dissolved carbonaceous organic matter into various gases and into cell tissue.

Because the cell tissue has a specific gravity slightly greater than that of water, removal from the treated effluent is facilitated under gravity.  Biologically treated effluent contains dissolved salts and residual impurities that have passed through the previous processes. These are removed in the membrane process such as reverse osmosis, which is suitable for removing high salt concentrations so that the treated effluent can be re-used again in the processing. A typical flow chart of the water recycle plant for the textile industry is shown in Figure 1.

Conclusions

Consumer awareness of the environmental issue is on the rise. It is the need of the day to substitute hazardous chemicals by environmentally benign methods. Buyers are eco-conscious on product, processes and disposal. Thus, the textile industry cannot ignore the environmental impact of its activities.

The best approach is to manufacture eco-friendly products and to modify certain areas of textile processing in such a way so as to avoid toxicity as efficiently as possible. At the same time, we must not forget in using better-engineered machines with less noise and following an effective and improvised system of air purification and circulation. Better handling of textile waste and their efficient disposal will surely be an appropriate step to maintain the ecological balance on earth.


References:

  1. Lal, R. A., Proc. NCUTE Extension Programme on Environmental Problems in Chemical Processing of Textile, KCT Coimbatore, India, (2001).
  2. Shastree, N. K., Environmental Resource Management, Noise Pollution: Standards and Control, Anmol Publication Pvt. Ltd., New Delhi, 1997.
  3. Prabhaka, V. K., Environmental Noise Pollution, Nature of Noise, Anmol Publications Pvt. Ltd., New Delhi, 2001.
  4. Ertem, M., Ilcin, E. and Meric, F., Tr. J. of Medical Sciences, 28, 561(1998).
  5. Subramanian, S. and Phalgumani, G. R., Proc. A Bilateral Symposium on Eco-Friendly Textile processing, IIT Delhi, India, (1995).
  6. Wagle, N. P., Proc. NCUTE Programme on Eco-Friendly Textile Wet Processing, S.S.M. College of Engineering Komarapalayam, India, (2001).
  7. Bechtold, T., Burtscher, E. and Gmeiner, D., Melliand Textilber, 72, 22 (1991).
  8. Bechtold, T., Burtscher, E., Kuhnel, G. and Bobleter, O., J Soc Dyers Colour, 113, 135 (1997).
  9. Anon, International Dyer, 189, 18 (2004).
  10. Taub, A., Textilveredlung, 4, 17 (2004).
  11. Clark, M., American Dyestuff Reporter, 83, 19 (1994).
  12. Reinhardt, R. M., American Dyestuff Reporter, 83, 80 (1994).
  13. Mukherjee, A. K., Proc. A bilateral symposium on Eco-friendly Textile Processing, IIT Delhi, India, (1995).
  14. Das, S. and Ghosh, A., Proc. National Conference on Environmentally Conscious Design and Manufacturing – Issues and Challenges, KCT Coimbatore, India, (2004).
  15. Metcaff and Eddy, Waste Water Engineering, Treatment, Disposal and Reuse, 3rd Edition, Mc-Graw-Hill International Edition, Singapore, 1997.
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