Abstract
Leather processing is an important industrial activity. Globally about 2.0 billon sqmt of leather is produced annually. Conventional cleansing operations carried out prior to tanning generate large amounts of waste. Among them dehairing and fibre opening process (reliming) generate large amount of effluent containing hazardous substances and alkaline sludge, resulting in high negative impact on the environment. In this study, both these pre-tanning process steps have been combined using a cocktail of carbohydrases along with optimum quantity of chemicals to minimize the environmental concerns. Carbohydrate and proteoglycan removal were chosen as the parameters of study for efficacy of unhairing and fibre opening. The morphology features of skins were analysed using scanning electron microscopy and histology. Pollution load of the enzyme aided process effluent was determined and compared with conventional process. Findings of the study indicate complete elimination of reliming process step is possible when both unhairing and fibre opening is carried out simultaneously using carbohydrases as an adjunct. Reduction in use of harmful sulphide and lime up to 40% apart from substantial saving in time and water input is the major outcome of the present work.
Similar content being viewed by others
References
Dey PM, Pridham JB (1972) Biochemistry of α-galactosidase. Adv Enzymol 36:911–930
Dubolis M, Gillis KA, Hamilton JK, Rebers PA, Smith F (1956) Colorimetric method for determination of sugars and related substances. Anal Chem 28:350–356
Durga J, Ranjithkumar A, Ramesh R, Rose C, Muralidharan C (2015) Rapid fiber opening process for skins: an approach for fail-safe chemical free process. J Am Leather Chem Assoc 110:07–12
Durga J, Ranjithkumar A, Ramesh R, Girivasan KTP, Rose C, Muralidharan C (2016) Replacement of lime with carbohydrases—a successful cleaner process for leather making. J Clean Prod 112:1122–1127
Eaton AD, Clesceri LS, Greenberg AE (1995) Standard methods of the examination of water and waste water. The American Public Health Association (APHA), Washington
Harish B, KhandelwalS MoreV, Kalal KM, Seeta Laxman R (2015) Eco-friendly enzymatic dehairing of skins and hides by C. brefeldianus protease. Clean Technol Environ Policy 17:393–405
IUP 2 (2000) Sampling. J Soc Leather Technol Chem 84:303
IUP 6 (2000) Measurement of tensile strength and percentage elongation. J Soc Leather Technol Chem 84:317–321
IUP 8 (2000) Measurement of tear load—double edge tear. J Soc Leather Technol Chem 84:327–329
Jian S, Wenyi T, Wuyong C (2011) Kinetic of enzymatic unhairing by protease in leather industry. J Clean Prod 19:325–331
Kandasamy N, Velmurugan P, Sundarvel A, Jonnalagadda RR, Bangaru C, Palanisamy T (2012) Eco-benign enzymatic dehairing of goat skins utilizing a protease from Pseudomonas fluorescens species isolated from fish visceral waste. J Clean Prod 25:27–33
Ludvik J (1996) Cleaner tanning technologies, UNIDO report, pp 18–25
Ludvik J (2000) The Scope of decrease of pollution load in leather processing (US/RAS/92/120/11-51). United Nation Industrial Development Organsiation-Regional programme for pollution control in the Tanning industry in south-East Asia, 2000-08-09
Mantle M, Allen A (1978) Periodic acid/Schiff assay for glycoproteins and Mucin. Bio Chem Soc Trans 6:607–609
Miller J (1972) Experiments in molecular genetics. Cold Spring Harbor Laboratory, NY, pp 352–355
Rose C, Suguna L, Samivelu N, Rathinasamy V, Ramalingam S, Iyappan K, Parvathaleswara T, Ramasami T (2007) Process for lime and sulfide free unhairing of skins or hides using animal/or plant enzymes. US Patent 7,198,647
Sandhya C, Sumantha A, Szakacs G, Pandey A (2005) Comparative evaluation of neutral protease production by Aspergillusoryzae in submerged and solid-state fermentation. ProcBiochem 40:2689–2694
Schlosser L, Keller W, Hein A, Heidemann E (1986) Utilisation of a Lactobacillus culture in the beamhouse. J Soc Leather Technol Chem 70:163–168
Seggiani M, Puccini M, Vitolo S, Chiappe C, Pomeli CS, Castiello D (2014) Eco-friendly titanium tanning for the manufacture of bovine upper leathers: pilot scale studies. Clean Technol Environ Policy 16:1795–1803
Senthilvelan T, Kanagaraj J, Mandal AB (2012) Application of enzymes for dehairing of skins: cleaner leather processing. Clean Technol Environ Policy 14:889–897
Sivasubramanian S, Manohar BM, Rajaram A, Puvanakrishnan R (2008) Ecofriendly lime and sulfide free enzymatic dehairing of skins and hides using a bacterial alkaline protease. Chemosphere 70:1015–1024
Thangam EB, Nagarajan T, Suseela RG, Chandrababu NK (2001) Application of alkaline protease isolated from Alcaligenesfaecalis for enzymatic unhairing in tanneries. J Ind Leather 37:215–222
Vijayaraghavan R, Vedaraman N, Muralidharan C, Mandal AB, MacFarlane DR (2015) Aqueous ionic liquid solutions as alternatives for sulphide-free leather processing. Green Chem 17:1001–1007
Acknowledgements
The authors gratefully acknowledge the Council of Scientific and Industrial Research (CSIR), New Delhi, for funding this research. Authors thank “Science and Technology Revolution in Leather with a Green Touch” (STRAIT)—1190.
Author information
Authors and Affiliations
Corresponding author
Electronic supplementary material
Below is the link to the electronic supplementary material.
Appendices
Appendix 1
The pelts were washed with 200% water for 10 min. Subsequently, the pelts were delimed by adding 100% water and 1% (w/w) ammonium chloride for 45 min in a drum. Deliming was ascertained by checking the cross section of the delimed pelts for colourlessness due to phenolphthalein indicator. After deliming, bating process were carried out in the same bath for 30 min by the addition of bating enzyme. The pelts were washed with 100% water for 10 min. Pickling was carried out. 1% sulphuric acid (w/w) was added in 4 feeds at 10-min interval and tumbled in a drum for 60 min to obtain pickled skin at pH of 2.8. The pickled skins were tanned using 8% (w/w) basic chromium sulphate (BCS) in 50% pickle water for 90 min. Then 50% (w/w) water was added and the drum was run further for 30 min. To the running drum, 1% (v/w) sodium formate (mixed with 10% w/v water) was added. After 30 min, 1% (w/w) sodium bicarbonate (mixed with 10% w/v water) was added in 3 feeds at 10-min interval and continued the tumbling for 60 more min to bring the pH to 3.8.
Appendix 2
Post-tanning operations comprise of rechroming of semi-finished wet blue leather, neutralization, dyeing, fat liquoring and finishing. The wet blue leathers obtained by the procedure under Appendix 1 to were shaved to 1.0 mm thickness. All the samples were washed in 100% (w/v) water in a drum for 10 min. After draining, the wet blue leathers were treated with 1.0% (w/w) neutralizing syntan with 100% water for 20 min. Sodium formate 0.5% (w/w) and sodium bicarbonate were then added to the drum in 3 feeds at 10-min interval, while the drum was in running mode. After ensuring the pH of the cross sections at 5.0, the leather samples were washing twice with 200% (w/v) water for 10 min. The neutralized skins were washed with water followed by treatment with resin syntan (3% w/w) and allowed to run in the drum for 20 min. After this, dying (2% w/w acid dye) and fat liquoring (4% w/w synthetic fat liquor) were carried out by drumming for 30 min. Subsequently melamine- and naphthalene-based retanning syntans 4% (w/w) was added and run for 40 min followed by the addition of synthetic fat liquor 4% (w/w), polymeric fat liquor 3% (w/w) and natural fat liquor oil 4% (w/w) and further running the drum for 40 min. Finally the auxiliaries were fixed using 2% (v/w) formic acid diluted with 20% (v/w) water and added at 3 feeds at every 10-min interval and the drum was further run for 30 min and piled overnight. The leathers were set, conditioned, again set with reversible setting machine and hooked for drying. After drying, leather was staked and buffed using 400-grit emery paper.
Rights and permissions
About this article
Cite this article
Durga, J., Ramesh, R., Rose, C. et al. Role of carbohydrases in minimizing use of harmful substances: leather as a case study. Clean Techn Environ Policy 19, 1567–1575 (2017). https://doi.org/10.1007/s10098-016-1321-x
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10098-016-1321-x