ECOFATTING Deliverable D5 Action 1-2
Transcription
ECOFATTING Deliverable D5 Action 1-2
INESCOP STUDY ON FATLIQUORING AGENTS ENVIRONMENTAL IMPACT ACTION 1-2 DELIVERABLE 5 January 2012–March 2013 LIFE ECOFATTING PROJECT LIFE10 ENV/IT/000364 ENVIRONMENTALLY FRIENDLY NATURAL PRODUCTS INSTEAD OF CLOROPARAFFINS IN THE FATTING PHASE OF THE TANNING CYCLE Prepared by INESCOP 1 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 TABLE OF CONTENTS 1. INTRODUCTION....................................................................................................................1 2. SELECTION OF LEATHER FAT-LIQUORING PRODUCT FAMILIES ........................1 3. DEFINITION OF PARAMETERS TO BE ANALYSED ......................................................2 4. DESCRIPTION OF LABORATORY, SEMI-INDUSTRIAL AND INDUSTRIAL SCALE TRIALS. .......................................................................................................................................4 4.1. Laboratory scale trials. .................................................................................................4 4.2. Semi-industrial scale trials. ..........................................................................................6 4.3. Industrial scale trials. ...................................................................................................7 5. ENVIRONMENTAL IMPACT OF DIFFERENT FAT-LIQUORING AGENTS................8 5.1. Analysis of fat-liquoring products ................................................................................8 5.2. Characterization of fat-liquoring residual baths ...........................................................9 5.3. Characterization of fat-liquoring leathers ...................................................................13 5.3.1. Organoleptic Tests.......................................................................................13 5.3.2. Physical Resistance Tests.............................................................................14 5.3.3. Chemical Tests on leather ............................................................................16 6. CONCLUSIONS ....................................................................................................................18 7. PHOTO GALLERY...............................................................................................................19 2 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 1. INTRODUCTION This report presents the results of the assessment of fat-liquoring products of different chemical nature from the point of view of their environmental performance. For this, different types of hides have been fat-liquored employing several products by carrying out trials at laboratory, semi-industrial and industrial level. In these trials, INESCOP has carried out the following tasks: − Selection of leather fat-liquoring product families − Definition of parameters to be analysed − Description of laboratory, semi-industrial and industrial scale trials − Analysis of fat-liquoring products − Characterisation of fat-liquoring residual baths − Analysis of leather: physical tests, chemical tests and organoleptic properties The results obtained have been used as a standard against which the improvement of the environmental impact of the natural fats developed is to be compared. 2. SELECTION OF LEATHER FAT-LIQUORING PRODUCT FAMILIES Traditionally, the process of fat-liquoring tanned leathers is carried out by either coating the hide with crude oil or by mixing this with soaps during the natural drying phase. Later, with the emergence of surfactants and the ability to produce fat emulsions, fat-liquoring began to be conducted by bathing the materials inside drums or paddle vats. Fat-liquoring products are formulated from a variety of different raw materials, such as vegetable oil trioleins, alcohol and fatty acids, fish oil, paraffins, lanolin, lecithin, etc. Then, different polar groups are added by sulphation, sulphonation, phosphatisation, chlorination, etc. in order to make them emulsifiable in water and to enable them to properly penetrate leather. Thus, this makes it possible to synthesise a large variety of fat-liquoring products. Nowadays, the fat-liquoring process carried out inside drums uses mixtures of fat-liquoring products of differing chemical natures, which transfer certain specific properties to the leather. However, efforts have been made to test the different products independently in order to properly evaluate each of their individual environmental impacts. Concerning the selection of the fat-liquoring product families most commonly used in EU tanneries, the tested families of fat-liquoring products are: 1 2 3 4 5 Sulphated olein Sulphonated olein Sulphited olein Sulphited fish oil Sulphated lecithin 6 7 8 9 10 Sulphated ester Phosphoric ester Sulphochlorinated paraffin Synthetic oils Fat-liquoring polymer Table 1. Selected fat-liquoring products families 1 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Figure 1. Selected fat-liquoring products. In commercial products, greases are mixed with water or emulsifiers with an active ingredient concentration of 65-80%. For this reason, the percentage of the commercial product added is recalculated for each fat-liquoring product so as to ensure the addition of the same amount of grease to all leathers. 3. DEFINITION OF PARAMETERS TO BE ANALYSED INESCOP has defined the parameters to be analysed, as much in fat-liquoring products and the wastewater produced in the fat-liquoring stage as in the leather obtained. Table 2 shows the parameters analysed for assessing the environmental impact of fat-liquoring products: Tests on fat-liquoring products (heavy metals) As (mg/l) Cd (mg/l) Pb (mg/l) Wastewater parameters pH Conductivity at 25 º C (µS/cm) BOD5 (mg O2/l) COD (mg O2/l) Biodegradability (BOD/COD) Cr (III) (mg/l) Oils and fats (mg/l) Leather parameters Touch / Softness Colour Organoleptic Grain firmness Fullness Shrinkage temperature (ºC) Tear resistance (N) Physical Tensile strength (N/mm2) Elongation at break (%) Extractable substance by using CH2Cl2 (% m.s.) Chemical Cr (VI) Table 2. Assessment of the environmental impact of fat-liquoring products; parameters to be analysed. 2 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 The tests were monitored by means of control sheets for tests & results, which contain information about: − Test type − Type of fat-liquoring product and characteristics − Type of skin and treatment − Fat-liquoring products analysis − Leather analysis: physical tests - chemical tests and organoleptic properties − Wastewater analysis Figure 2. Control sheets for tests & results. 3 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 4. DESCRIPTION OF LABORATORY, SEMI-INDUSTRIAL AND INDUSTRIAL SCALE TRIALS. 4.1. Laboratory scale trials. The laboratory-scale leather fat-liquoring trials were conducted at INESCOP-U.T Vall d’Uixó facilities using the selected products. The trials were carried out in rotating stainless steel tanning drums measuring 300 mm in diameter and 150 mm in width respectively, featuring systems for automation, control and dosage of water and reactants. Figure 3. Laboratory-scale rotating drums at INESCOP-UT Vall d’Uixó facilities. Figure 4. Detail of laboratory-scale trials at INESCOP-UT Vall d’Uixó facilities. In each test with the calf hides, 1 sq. foot pieces of wet-blue shaved hides with a thickness of 1.5 mm were processed. These pieces of wet-blue cattle hides had been prepared for the fatliquoring operation by means of a standard process of neutralisation, retanning and dyeing. The formulations used in these tests are shown in Table 3 where it is indicated, for the different operations, the product used, the percentage by weight with respect to the wet-blue leather introduced into the tanning drum, temperature, rotating time and checks to be performed. 4 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 % by wet-blue weight Tª (ºC) Rinse with water 200 40 Acetic Acid 0’2 Degreasing surfactant 0’2 PROCESS/PRODUCTS Time (min.) pH Remarks 4’1 Check pH 4’5 Check pH 45’ 4’6 Check through section 30’ 3’8 Check pH RETANNNG 20’ Drain and wash Water 100 Synthetic Chromium 5 Sodium Formiate 1 40 30’ Drain NEUTRALISATION Water 200 40 Synthetic buffered solution 2 Sodium Formiate 1 40’ Sodium bicarbonate 1 15’ Acrylic Resin 5 60’ Drain and wash DYEING Water 50 Synthetic Phenol 5 Filler 5 Dispersing Agent 1 Powdered dye 1 Water 200 Formic Acid 0’5 25 20’ 60 Drain and wash Table 3. Description of the retanning, neautralisation, and dyeing processes. 5 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Once the hides had been retanned, neutralised and dyed, the fat-liquoring stage was performed, according to the process described in Table 4: PROCESS/PRODUCTS % by wet-blue weight Tª (ºC) 5000 45-50 Time (min.) pH Remarks FAT-LIQUORING Water 1 Fat-liquoring product 8 Formic acid (1:10 dilution) 3 90’ 20’ Check pH Wash, drain drum, take bath sample and remove leather Air dry Table 4. Description of the leather fat-liquoring process. Once this operation was completed, a sample of the waste fat-liquoring bath and a sample of each one of the obtained leathers were taken for the determination of the parameters showed in Table 2. In Annex 1, there are images of the trials being carried out in laboratory conditions and also of the resulting leather. 4.2. Semi-industrial scale trials. The semi-industrial scale leather fat-liquoring trials were conducted at INESCOP-U.T Vall d’Uixó facilities using the selected products. The trials were carried out in rotating tanning drums measuring 900 and 1,200 mm in diameter respectively and 450 mm in width, made of bolondo wood and featuring systems for automation, control and dosage of water and reactants. Figure 5. Semi-industrial scale rotating drums at INESCOP-UT Vall d’Uixó facilities. 1 In commercial products, greases are mixed with water or emulsifiers with an active ingredient concentration of 65-80%. For this reason, the percentage of the commercial product added is recalculated for each fat-liquoring product so as to ensure the addition of the same amount of grease to all leathers. 6 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 In each test with the calf hides, wet-blue shaved hides with a thickness of 1.5 mm divided into sides (half hide) were processed. The formulations used in these tests are the same as the ones employed during the laboratory trials which are shown above in Table 3, where it indicates, the product used, the percentage by weight with respect to the wet-blue leather introduced into the tanning drum, temperature, rotating time and checks to be performed during each process. Then, adhering to the process described above in Table 4, fat-liquoring was performed, on the retanned, neutralised and dyed hides. Once this operation was completed, a sample of the waste fat-liquoring bath and a sample of each one of the obtained leathers were taken for the determination of the parameters showed in Table 2. In Annex 2, there are images of the trials being carried out on a pre-industrial scale and also of the resulting leather. 4.3. Industrial scale trials. The industrial scale leather fat-liquoring trials were conducted at INESCOP-U.T. Vall d’Uixó facilities using the selected products. The trials were carried out on rotating tanning drum of 1,600 mm diameter respectively and 1,100 mm width, made of bolondo wood and featuring systems for automation, control and dosage of water and reactants The trials were carried out in this tannery in an industrial rotating tanning drums, as show in Figure 6: Figure 6. Pre-industrial scale rotating drums at INESCOP-UT Vall d’Uixó facilities. 7 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 In each test with the calf hides, wet-blue shaved hides with a thickness of 1.5 mm divided into sides (half hide) were processed. The formulations used in these trials are the same that employed at laboratory scale trials which are shown in previous Table 3, where it is indicated, for the different operations, the product used, the percentage by weight with respect to the wet-blue leather introduced into the tanning drum, temperature, rotating time and checks to be performed. Then, on the hides retanned, neutralised and dyed, the fat-liquoring stage was performed, according to the process described in previous Table 4. Once this operation was completed, a sample of the waste fat-liquoring bath and a sample of each one of the obtained leathers were taken for the determination of the parameters showed in Table 2. In Annex 3, there are images of the tests being carried out on a pre-industrial scale and also of the resulting leather. 5. ENVIRONMENTAL IMPACT OF DIFFERENT FAT-LIQUORING AGENTS In all trials carried out, the obtained leathers have good physical strength and adequate smoothness, softness, fullness and flexibility, and no significant difference between the different fatliquoring agents has been detected. The environmental evaluation of the results of the carried out tests is done through: − the analysis of fat-liquoring products − the characterization of fat-liquoring residual baths − the analysis of leather: physical tests, chemical tests and organoleptic properties 5.1. Analysis of fat-liquoring products The evaluation of the characteristics possessed by the fatliquoring products chosen to be used in the tests was carried out by determining the levels of arsenic, cadmium, and lead contained in the products, in order to prevent these substances from being present in leather in accordance with the criteria of the European Eco-label for footwear (Decision 2009/563/EC). The determination of the chemical parameters of the fatliquoring products showed its conformity to the limits established in the European Eco-label for footwear, since the findings of the analysis showed results that were less than the aforementioned limit for all of the products: Arsenic: Cadmium: Lead: < 60 ppm * < 6 ppm * < 8 ppm* * Limit of detection of the analysis technique employed 8 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 5.2. Characterisation of fat-liquoring residual baths The evaluation of the impact of the fat-liquoring on wastewater was achieved by the characterisation of the fat-liquoring waste-baths obtained in the different tests carried out, determining the most significant parameters in accordance with international standards. The table below shows the selected control parameters and the testing standards used: PARAMETER pH Conductivity COD STANDARD --UNE-EN 27888:1994. Determination of electrical conductivity. (ISO 7888:1985). UNE 77004:2002. Determination of the chemical oxygen demand (COD). BOD5 UNE-EN 1899-1:1998 Determination of biochemical oxygen demand after n days (BODn). Total Cr UNE 77061:2002 Chromium determination. Oils & Fats Standard Methods for the Examination of Water and Wastewater_SM 5520 B Table 4. Standards used in the characterization of tanning wastewater. Below, shown in graph form are the results of the analyses on fatliquoring residual baths, where the different impact of each fatliquoring product can be compared for each parameter. The graphs show the results obtained for each parameter in laboratory tests (in blue colour) on a semi-industrial scale (in pink colour) and on pre-industrial test (in white colour). In general, it can be seen that the growing mechanical effect entails a greater fixation of fatliquoring products and, therefore, a lower level of contamination in the residual baths. pH The pH value of waste water resulting from fatliquoring baths plays an important role in the process, since both the cross of leather (which depends on neutralisation) and the stability of the fatliquoring emulsion depend on pH levels. Furthermore, fatliquoring products can possess diverse ionic natures (anionic, cationic, and non-ionic), though usually they tend to be anionic. Moreover, the ionic characteristics of leather depend on pH levels, with fatliquors of an anionic nature attaching to cationic leather and vice versa. Amongst the various products that have been tested, all of them presented anionic characteristics, the only exceptions being the sulphated lecithin and sulphonated olein, both of which are non-ionic. In order to evaluate this parameter, pH levels in the residual baths were measured when the fatliquoring process had ended. Values between 3.3 and 4 were obtained, typical for this type of bath, which is used to carry out the fixation of fats through the addition of formic acid at the end of the stage in question. Figure 7 displays the values obtained during the laboratoryscale tests, and also the tests carried out on a semi-industrial and pre-industrial scale. 9 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 4,00 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 3,80 3,60 3,40 3,20 Laboratory test 3,00 1 2 3 4 5 6 7 8 9 10 pH Semi-industrial test Pre-industrial test Figure 7. Measuring the pH of the residual baths used in fatliquoring. Conductivity Regarding COD values present in the residual baths used in fatliquoring, the results obtained show a large variability in relation to the fatliquor used. As can be seen in figure 8, conductivity in the fatliquoring baths is less than 3000 µS/cm, except in the bath where sulphochlorinated paraffin was used, whose values are a lot higher than the mean. This is due to doubly ionic characteristics of this product, owing to the content of chlorine and other groups of sulphonated substances, whilst the other products only presented a sole ionic group each (a sulphated, sulphonated, sulphited or phosphatised group). 5.000 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 4.000 3.000 2.000 1.000 Laboratory test 0 1 2 3 4 5 6 7 8 9 10 Conductivity (µs/cm ) Semi-industrial test Pre-industrial test Figure 8. Measuring the conductivity of fatliquoring baths. With regard to conductivity, the environmental impact of fatliquoring agents is not very significant compared to other products and stages of the tanning process. Sulphochlorinated paraffins are the fats with the greatest impact on conductivity and Sulphonated olein, Sulphited olein and Oxidised lecithin are the fats with the lowest impact on it. 10 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Chemical Oxygen Demand (COD) Regarding COD values present in the residual baths used in fatliquoring, the results obtained show a large variability in relation to the fatliquor used. In all cases, the COD of these residual baths exceeded established limits for wastewater discharged into the sewers in Spain (< 1,500 mg/l). However, the wastewater from these baths is not discharged directly into the sewer, but it is mixed with the other water from the tannery, and as a result accounts for approximately 6% of the total volume of water discharge, and thus there is a factor of dilution with the remainder of the water used throughout the process. Figure 9 shows the values obtained in the laboratory, semi-industrial and pre-industrial tests. 20.000 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 15.000 10.000 5.000 Laboratory test 0 1 2 3 4 5 6 7 8 9 10 Semi-industrial test Pre-industrial test COD (m g/L) Figure 9. Determining COD in the residual baths used in fatliquoring. Biodegradability relationship (BOD/COD) The biodegradability of the fatliquoring residual baths is determined by analysing the relationship between BOD and COD. In terms of wastewater, effluents are classified in the following fashion: BOD/COD < 0.2 0.2 < BOD/COD < 0.7 0.7 < BOD/COD < 0.8 BOD/COD > 0.8 Non-biodegradable Slightly biodegradable Biodegradable Highly biodegradable The results obtained (as shown in figure 10) demonstrate that in general, fatliquoring baths do not, in themselves, tend to be particularly biodegradable. However, the phosphoric esters and the fatliquoring polymer are the two substances that proved to be the least biodegradable when transferred to water. 11 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 0,60 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 0,50 0,40 0,30 0,20 0,10 Laboratory test 0,00 1 2 3 4 5 6 7 8 9 10 Biodegradability Semi-industrial test Pre-industrial test Figure 10. Comparing levels of biodegradability in the fatliquoring baths. Cromium (III) The determination of this parameter is carried out in order to verify the incidence of the fatliquoring product in the release of trivalent chromium of leather. The results obtained, (as shown in Figure 11) demonstrated that, in general, fatliquoring baths do not cause the discharge of vast quantities of leather, the fatliquoring polymer being the one with the lowest capacity for the solubilisation of chromium from leather, owing to the lack of any reactive groups (sulphated, sulphonated, sulphited, phosphatised, or chlorinated groups etc.), which are present in the remainder of the products that were tested. 6,0 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 5,0 4,0 3,0 2,0 1,0 Laboratory test 0,0 1 2 3 4 5 6 7 Chrom ium (III) (m g/L) 8 9 10 Semi-industrial test Pre-industrial test Figure 11. Comparison of the content of trivalent Chromium in fatliquoring baths 12 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Oils and fats The determination of this parameter was carried out in order to test the fixation of fatliquoring products on leather. The extraction of fats from the residual baths was conducted with a mixture of two solvents (hexane and tert-butyl methyl ether, at a ratio of 80:20). The results obtained (shown in Figure 12) demonstrate that, in general, fats fix adequately to leather and fatliquoring baths do not present a high content of non-fixed oils and fats. 2.500 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 2.000 1.500 1.000 500 Laboratory test 0 1 2 3 4 5 6 7 8 9 10 Oils/Fats (m g/L) Semi-industrial test Pre-industrial test Figure 12. Analysis of levels of oils/fats in fatliquoring baths. 5.3. Characterisation of fat-liquoring leathers The characterisation of fatliquored leather was conducted from three points of consideration:: - Organoleptic tests. - Physical resistance tests. - Chemical tests. 5.3.1. Organoleptic tests The parameters considered in the organoleptic tests were: touch, colour, and firmness factors. Regarding the touch of the leathers tested, this was graded on the level of softness obtained, assigning a value of 1 for the lowest level of softness and 5 for the highest. In table 5 the results of this test are displayed, observing an adequate level of leather softness in all leather hides (3-5), except those subjected to the fatliquoring process using sulphited fish oil, which demonstrated a lower level of softness (2). 13 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 No. of Sample 1 2 3 4 5 6 7 8 9 10 Type of fat Touch (1-5) Sulphated olein Sulphonated olein Sulphited olein Sulphited fish oil Sulphated lecithin Sulphated ester Phosphoric ester Sulphochlorinated paraffin Synthetic oils (*) Fatliquoring polymer 3 5 4 2 5 4 4 3 5 4 Table 5. Touch test on fatliquored leather hides. In reference to the firmness of the leather, continuous flexing of the leather was carried out to test the degree of adhesion of the grain. Loose grain is an undesirable effect in leather, since during use as part of finished products (e.g. shoes, leather garments, etc.), wrinkles begin to form in areas where flexing movements take place. With all of the fatliquors that were tested, none produced leather with loose grain characteristics; all of the resulting leather possessed adequate levels of firmness. Finally, regarding colour, differences in final leather colour tone were observed upon the use of the various fatliquors, but no significant differences were present. 5.3.2. Physical resistance tests The quality assessment on the production of fatliquoring hides is done through physical validations in accordance with accepted standards (EN, ISO, etc.). The table below shows the selected control parameters and the testing standards used: PARAMETER STANDARD Thickness (mm) ISO 2589:2002 (IULTCS/IUP 4) Determination of thickness Tear strength (N) ISO 3377-2:2002 (IULTCS/IUP 8) Determination of tear load -- Part 2: Double edge tear Tensile strength (N/mm2) ISO 3376:2002 (IULTCS/IUP 6) Determination of tensile strength and percentage extension Elongation at break (%) ISO 3376:2002 (IULTCS/IUP 6) Determination of tensile strength and percentage extension Grain burst (mm) ISO 3379:1976 (IULTCS/IUP 9) Determination of distension and strength of grain -- Ball burst test Table 6. Standards used in the physical validations of fatliquoring hides. 14 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 The determinations of physical parameters of the leathers have shown to be compliant with the limits required for footwear manufacture. Tear resistance (N): We can see in figure 13 that all the fatliquored leathers comply with the minimum tear resistance requirements of 50 N for articles being used in the manufacture of footwear. 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 25 20 15 10 5 0 1 2 3 4 5 6 7 8 9 10 Laboratory test Semi-industrial test Te nsile strength (N/m m 2) Pre-industrial test Figure 13. Tear resistance of fatliquored leather. Tensile strength (N/mm2) In all cases, the fatliquored leather hides comply with the minimum tensile strength requirements of 15 N/mm2 for articles being used in the manufacture of footwear and in the leather goods industry (figure 14). 350 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 300 250 200 150 100 50 Laboratory test 0 1 2 3 4 5 6 7 8 9 10 Tear resistance (N) Semi-industrial test Pre-industrial test Figure 14. Tensile strength of fatliquored leather. Elongation at break (%) 15 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Through the use of this test, the elasticity of leather is evaluated, measuring the maximum elongation reached before breaking the leather. The minimum level of elongation required for the manufacture of footwear and other leather goods is 40%, this being extensively fulfilled by each of the fatliquored leathers (see Figure 15). 120 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 100 80 60 40 20 Laboratory test 0 1 2 3 4 5 6 7 8 9 10 Elongation at break (%) Semi-industrial test Pre-industrial test Figure 15. Elongation at break of the fatliquored leather. Grain burst (mm) The testing of this parameter verifies if the grain layer of the leather breaks upon being folded, which would indicate a low level of elasticity deriving from the poor fatliquoring of the leather. The minimum grain burst requirement for the manufacture of footwear is 7 mm, this value being fulfilled in all cases. 5.3.3. Chemical tests on leather The quality assessment on the production of fatliquoring hides is done through physical validations in accordance with accepted standards (EN, ISO, etc.). The table below shows the selected control parameters and the testing standards used: PARAMETER Matter soluble in dichloromethane (%) Chromium(VI) (mg/kg) STANDARD ISO 4048:2008 Leather - Chemical tests - Determination of matter soluble in dichloromethane ISO 17075:2007 Leather - Chemical tests - Determination of chromium(VI) content 16 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Matter soluble in dichloromethane This parameter enables the evaluation of the level of fatliquor fixation in the leather in a way that has a direct relationship with its physical behaviour in terms of grain burst, tear resistance, tensile strength, elongation at break, and touch, etc. The quantity of fat that is required to be fixed in the fatliquoring process, as well as the level of penetration into the leather that will take place, largely depend on the type of fat used. So, although fatliquored leather hides generally present amounts of fat accounting for between 3 and 9% of total content, certain fatliquors may result in amounts being less than 3%. On the whole, levels accounting for less than 3% tend to result in leathers that are not significantly fatliquored and their mechanical characteristics are not adequate for use in the manufacture of garments. Above 9% proves that the fatliquoring has been excessive, impeding the subsequent finishing, bonding, or vulcanisation processes taking place during the latter stages of the assembly of footwear. 8,0 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 7,0 6,0 5,0 4,0 3,0 2,0 1,0 Laboratory test 0,0 1 2 3 4 5 6 7 8 9 10 Fat (%m .s.) Semi-industrial test Pre-industrial test Figure 16. Measuring the % of fat present in the leather. According to figure 16, during the tests a level of fat fixation higher than 3% was reached in all samples except for products 8, 9, and 10. In the example shown by product 8, this product being a sulphochlorinated paraffin, two polar groups are present in its composition, so the level of leather fixation is at very high levels. Therefore, it is not entirely extracted with dichloromethane, a solvent employed in the test measuring the percentages of fat present. On the other hand, the synthetic oils and fatliquoring polymers are not fats as per se like the others, so with lesser quantities fixed onto the leather, the results of the fatliquoring process are of a higher quality and differences are not observed in the properties of the leather hides. Chromium (VI) By conducting this test, it has been possible to evaluate the influence of each fatliquoring agent on the formation of Chromium VI, derived from the Chromium III fixed to the leather during tanning. Hence, before and after the fatliquoring process, leather hides were subjected to an aggressive ageing process, prompting the appearance of hexavalent chromium. 17 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 The formation of Chromium VI is owed to the free radicals that emerge after the breakdown of the double bonds in the fats. However, the various commercial products, despite being part of the same family (e.g. sulphated olein), can present very distinctive chain lengths and degrees of instauration. During the previous ageing tests, there were no detections of cases where hexavalent chromium was present in the fatliquored leathers, complying with the requirements established by the Eco-label for footwear. However, after ageing, hexavalent chromium was determined to be present in all of the leather. As can be seen in figure 17, two ranges of chromium VI were observed: a range of between 13 and 23% was seen in products 3, 4, 5, and 7, and between 5 and 10% for products 6, 8, 9, and 10. In particular, product 2 (sulphited olein) obtained the lowest level of Chromium VI in the resulting leather. 25 1. Sulphated olein 2. Sulphonated olein 3. Sulphited olein 4. Sulphited fish oil 5. Oxidised lecithin 6. Sulphated ester 7. Phosphoric ester 8. Sulphochlorinated paraffin 9. Synthetic oil 10. Fatliquoring polymer 20 15 10 5 Laboratory test 0 1 2 3 4 5 6 Cr VI (ppm) 7 8 9 10 Semi-industrial test Pre-industrial test Figure 17. The formation of Chromium VI in fatliquored leathers after ageing. 6. CONCLUSIONS The results obtained show that none of the families of commercial fatliquoring agents that have been evaluated stand out in terms of their environmental performance. Instead several products have been highlighted as having a reduced contribution to COD, but, on the other hand, they have also shown to have a high level of conductivity or a high tendency for the formation of hexavalent chromium. Therefore, in order to allow a better comparison of the results obtained, tables 7 and 8 show the minimum, maximum and average results collected; these will be used as reference values during the evaluation of the natural fats developed by SERICHIM. 18 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Laboratory test Minimum Maximum Average pH 3,54 3,98 3,81 Conductivity (µs/cm) 1.900 5.000 2.750 COD (mg/l) 12.700 18.300 15.360 BOD (mg/l) 2.570 8.850 6.291 Biodegradability Total Cr (mg/l) 0,17 0,7 0,59 5,4 0,41 3,0 Oils & Fats (mg/l) 65 2380 991,5 Conductivity (µs/cm) 1.100 3.900 2.130 COD (mg/l) 8.200 17.100 12.000 BOD (mg/l) 1.310 5.130 3.611 Biodegradability Total Cr (mg/l) 0,11 0,4 0,48 4,0 0,31 2,2 Oils & Fats (mg/l) 27 980 348,4 Conductivity (µs/cm) 800 3.700 1.982 COD (mg/l) 7.500 16.700 11.500 BOD (mg/l) 1.130 4.192 2.844 Biodegradability Total Cr (mg/l) 0,10 0,9 0,48 3,5 0,27 2,0 Oils & Fats (mg/l) 31 684 230 Semi-industrial test Minimum Maximum Average pH 3,42 3,76 3,66 Pre-industrial test Minimum Maximum Average pH 3,37 3,71 3,56 Table 7. Minimum, maximum and average results of fatliquoiring residual baths characterization Laboratory test Tear strength (N) Minimum 132 Maximum 211 Average 155,6 Semi-industrial test Tear strength (N) Minimum 55 Maximum 314 Average 211,8 Pre-industrial-test Tear strength (N) Minimum 67 Maximum 343 Average 229,9 Tensile strength (N/mm2) 15,2 19 16,95 Elongation at break (%) 59,9 84,6 72,32 Matter soluble in Cl2CH2 (% m.s.) 1,6 8 4,42 Chromium (VI) (mg/kg) 7,8 22 14,3 Tensile strength (N/mm2) Elongation at break (%) Matter soluble in Cl2CH2 (% m.s.) Chromium (VI) (mg/kg) 15,2 67,8 0,9 6,7 18,9 103,1 4 20,4 17,39 85,92 2,67 12,97 Tensile strength (N/mm2) Elongation at break (%) Matter soluble in Cl2CH2 (% m.s.) Chromium (VI) (mg/kg) 15,4 67 0,8 4,1 20,4 93 3,5 17,8 18,08 82,5 2,37 10,7 Table 8. Minimum, maximum and average results of physical-chemical leather analisys 19 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 7. PHOTO GALLERY The images that have been collected show the tests (those carried out in the laboratory, and on a semi-industrial, and pre-industrial scale) conducted during the different stages of the fatliquoring process: the pH control of the leather in the neutralising stage, colour penetration, fat fixing, and the draining of the leather hides by hanging them on horses, etc. Ensayos escala laboratorio: emulsión engrase Ensayos escala laboratorio: dosificación reactivos 20 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Ensayos escala semi-industrial: neutralización Ensayos escala semi-industrial: tintura y engrase de las pieles. 21 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Ensayos escala semi-industrial: aspecto pieles engrasadas Ensayos escala semi-industrial: aspecto final de las pieles 22 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Ensayos escala pre-industrial: control pH Ensayos escala pre-industrial: dosificación reactivos 23 Study on the fatliquoring agents environmental impact LIFE10 /ENV/IT/000364 Ensayos escala pre-industrial: tintura y engrase de las pieles. 24