Textile Finishing Industry as an Important Source of Organic Pollutants

The textile finishing industry is, among all industries in Europe, the greatest consumer of high quality fresh water per kg of treated material and with the natures of their production processes significantly contributing to pollution. Wastewater from the textile industry is also a significant environmental pollution source of persistent organic pollutants. Not only textile wastewater but also textile products often contain chemicals such as formaldehyde, azo-dyes, dioxins, pesticides and heavy metals, that might pose a risk to humans and the environment. Some of these chemicals found in finished products are there as residues from the production of dyes and auxiliary chemicals (the synthesis of dyes involves a large variety of chemicals with complex synthesis paths, during which toxic, carcinogenic and persistent organic compounds can be formed, such as dioxins, and traces can be found in commercial dyes), others are added to give certain characteristics to the products (colour, flame retardancy, anti wrinkling properties etc.) (Križanec & Majcen Le Marechal, 2006), or are already present in the raw textile material. The mentioned compounds have been found in wastewater after home washing, in organic solvent after dry-cleaning and also in the atmosphere after incineration. Possible sources of organic pollutants are also wastewater treatment methods and the incineration of textile materials. The formation of dioxins can occur via dyeing and textile finishing processes with conditions favourable for their generation (high temperature, alkaline conditions, ultraviolet (UV) radiation, and other radical initiators). Textile dyes are designed to be resistant to microbial, chemical, thermal and photolytic degradation. After the dyeing process, a lot of non-bonded dyes are released into the wastewater, which can also be treated by Advanced Oxidation Processes (AOPs) in order to destroy the dye molecule and to decolourise the wastewater and reduce organic pollution. It is well-known that under the experimental conditions of such methods, which can be very useful because of the short-time of treatment, hazardous compounds can be formed due to very powerful oxidizing agents such as hydroxyl radicals (OH). In line with the improvement of people’s living standard and the growing awareness and need to preserve the environment several regulations were introduced also in the textile industry in order to control the use of chemicals in textile processes. Under REACH regulation (REACH regulation controlled the quality of fabric, apparels, and shoes

[1]  Anil Baral,et al.  Chromium-based regulations and greening in metal finishing industries in the USA , 2002 .

[2]  Graham Brookes,et al.  GM crops: global socio-economic and environmental impacts 1996- 2007 , 2008 .

[3]  Willy Verstraete,et al.  Treatment and Reuse of Wastewater from the Textile Wet-Processing Industry : Review of Emerging Technologies , 1998 .

[4]  E. Somers International Agency for Research on Cancer. , 1985, CMAJ : Canadian Medical Association journal = journal de l'Association medicale canadienne.

[5]  Mark A. Brown,et al.  Predicting azo dye toxicity , 1993 .

[6]  H. Chu,et al.  Reuse of activated sludge biomass: I. Removal of basic dyes from wastewater by biomass , 2002 .

[7]  Ibrahim M. Banat,et al.  Microbial decolorization of textile-dye-containing effluents A review , 1996 .

[8]  A. L. Marechal,et al.  Dioxins and Dioxin-Like Persistent Organic Pollutants in Textiles and Chemicals in the Textile Sector , 2006 .

[9]  E. Abad,et al.  Dioxin mass balance in a municipal waste incinerator. , 2000, Chemosphere.

[10]  S. Parsons,et al.  Advanced Oxidation Processes for Water and Wastewater Treatment , 2015 .

[11]  K. Golka,et al.  Carcinogenicity of azo colorants: influence of solubility and bioavailability. , 2004, Toxicology letters.

[12]  S. Vajnhandl,et al.  Case study of the sonochemical decolouration of textile azo dye Reactive Black 5. , 2007, Journal of hazardous materials.

[13]  J. Volmajer Valh,et al.  Water in the Textile Industry , 2011 .

[14]  D. Mattioli,et al.  Water minimization and reuse in the textile industry. , 2001 .

[15]  W. Baumann,et al.  Textile Chemicals: Environmental Data and Facts , 2004 .

[16]  R. Irusta,et al.  Decolouration of textile dyes in wastewaters by photocatalysis with TiO2 , 2005 .

[17]  Y. Slokar,et al.  Methods of decoloration of textile wastewaters , 1998 .

[18]  H. Zollinger Color chemistry: Syntheses, properties, and applications of organic dyes and pigments , 1987 .

[19]  G. Prasad,et al.  Removal of chrome dye from aqueous solutions by mixed adsorbents fly ash and coal , 1990 .

[20]  Steven E. Naranjo,et al.  Impacts of Bt crops on non-target invertebrates and insecticide use patterns , 2009 .

[21]  B. Mccarthy Biotechnology and coloration , 2008 .

[22]  M. Pelzing,et al.  An optimized method for the determination of perfluorooctanoic acid, perfluorooctane sulfonate and other perfluorochemicals in different matrices using liquid chromatography/ion-trap mass spectrometry. , 2011, Journal of chromatography. B, Analytical technologies in the biomedical and life sciences.

[23]  Trevor Coward,et al.  Nova Science Publishers , 2013 .

[24]  A. L. Marechal,et al.  Comparison of H2O2/UV, H2O2/O3 and H2O2/Fe2+ processes for the decolorisation of vinylsulphone reactive dyes , 2003 .

[25]  Santiago Villaverde,et al.  Combined anaerobic-aerobic treatment of azo dyes--a short review of bioreactor studies. , 2005, Water research.

[26]  D. Sponza,et al.  Fate and toxicity of azo dye metabolites under batch long-term anaerobic incubations , 2007 .

[27]  Keisuke Hanaki,et al.  Treatise on water science , 2011 .