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Article

Characterisation of Fibre Mechanical Recycled Cotton Denim Fibres and the Effects of Their Properties on Yarns and Knits

1
VTT Technical Research Centre of Finland Ltd., P.O. Box 1000, 02044 Espoo, Finland
2
Department of Technology, LAB University of Applied Sciences, Mukkulankatu 19, 15210 Lahti, Finland
3
CITEVE Technological Centre for the Textile and Clothing Industries, Rua Fernando Mesquita, nº 2785, 4760-034 Vila Nova de Famalicão, Portugal
*
Author to whom correspondence should be addressed.
Recycling 2025, 10(5), 177; https://doi.org/10.3390/recycling10050177
Submission received: 4 July 2025 / Revised: 15 August 2025 / Accepted: 13 September 2025 / Published: 19 September 2025

Abstract

The purpose of this study was to obtain a holistic view of mechanically recycled cotton from denim fabrics and the repurposing and recycling methods for similar fibres. A pre-consumer denim and three types of post-consumer denims were shredded into new fibres, which were characterised with single-fibre tensile testing, SEM imaging and DSC analysis. The opened cotton fibres were then blended with primary cotton with varying ratios and spun into yarns of 40 tex with a ring spinning machine. A ratio of 75/25 of recycled fibres to virgin fibres was obtained, with promising tensile strength results. Further, the yarns were knitted into single jersey fabrics, and abrasion testing was performed to evaluate their wearing out. Best abrasion resistance was obtained for knits consisting of 100% virgin cotton fibres and the knits consisting of a blend of pre-consumer and virgin fibres. The results suggest the yarns made with mechanically opened fibres are suitable for single jersey knits. SEM and DSC confirm the input of mechanical recycling defines the output. Moreover, the SEM pictures indicate there is little to no damage to single fibres caused by mechanical shredding, causing no further barriers for secondary use as raw materials.

1. Introduction

The European Waste Framework Directive was revised in 2018, setting stricter rules for the disposal of textiles. As of January 2025, the EU member states must organise a separate collection of textile waste, ultimately due to high discarding rates and low recycling rates [1]. According to a 2019 finding [2], the EU discards 12.6 million tonnes of textiles yearly. Majority of the discarded textiles, 87%, are post-consumer waste. Another widely quoted figure is the yearly discarding rate of 11.3 kg per European consumer [3,4]. Approximately 22% of post-consumer textile waste is collected for reuse or recycling, and the remainder is directed to landfills or incineration [2]. The low recycling rates and obligations have led the industry to search for suitable collection methods, followed by identification, sorting and recycling technologies. Chemical, thermal or thermo-mechanical, and mechanical recycling are the most common methods for textile recycling. Mechanical recycling is considered a cost- and energy-efficient process [5] that can, at least in theory, break down all materials similarly by shredding, as opposed to having to accommodate the different chemical or thermal properties of different fibres. In general, the staple fibres obtained in the mechanical recycling process can be converted into yarn again.
The global textile industry produced 124 million tonnes of textile fibres in 2023 [6]. By 2030, that total is expected to grow to 160 million tonnes, a number that has been reevaluated from 147 million tonnes—the estimation made a year earlier [7]. Invisible in the numbers is another issue: during the year 2023, the fashion industry was estimated to produce 2.5 to 5 billion garments too many [8]. Cotton fibres represent 19.9% of the global fibre production, and recycled cotton fibres approximately 1% of that, totalling to 0.25 million tonnes in 2023. The most widely applied recycled fibres are thermo-mechanically recycled polyester fibres made from PET bottles [6].
While the legislative obligation to collect consumer textiles suggests greater amounts of post-consumer textile in the future, it is more difficult to forecast the material content of the textile waste and the consequential supply of secondary markets. Consulting the care labels in one’s wardrobe gives valuable insight into estimating how challenging it will be to obtain an output of 100% desired fibre type by recycling consumer textiles. The material composition of a mechanical recycling process output is defined by the input. Therefore, the feasibility of closed-loop recycling of textiles, or fibre-to-fibre recycling, is directly dependent on efficient and traceable collection, identification and sorting of materials. Controlling the colour and material composition of post-consumer textiles is one of the greatest challenges of mechanical fibre-to-fibre recycling; see [9,10].
The other great challenge is related to the quality of mechanically recycled (MR) fibres. Mechanically recycled cotton is often referred to as possessing a “lower quality”, which is why it is often blended with other fibres, especially longer, virgin fibres [5] to facilitate easier spinning. In the shredding process, the fibre is exposed to mechanical forces that shorten the fibre, contributing to a high short fibre content (SFC) [11,12,13] and causing nepping [14], characteristics that affect both the spinnability and overall quality of yarn. It is advised to use 20–30% of recycled fibres in yarns for fabric production [15], although higher percentages have been obtained by many. Current research of yarns made with MR cotton (or post-consumer waste containing cotton fibres) covers blends with usually virgin cotton [12,14,16] and virgin polyester [17,18], but also blends of recycled cotton and recycled polyester are researched by some [17,19]. Jamshaid et al. [20] successfully spun a 100% recycled cotton yarn with pre-consumer cotton obtained from the different stages of spinning line. The term “mechanically recycled” in this context means a staple fibre obtained from mechanical opening or shredding. However, discussing recycled fibres often suggests the fibre comes from post-use, or other post-consumer sources. The literature presented in this paper is divided on the subject.
The short fibre length of MR fibres has been reported to affect the total strength [11] and other qualities, such as uniformity and fineness [12], in yarns, depending on the spinning method described in the respective papers. There is a slight upward trend in research into mechanical recycling currently; however, many of the papers present merely a case study. When it comes to fibre properties, there are a handful of recent studies about MR cotton or cotton blend fibre lengths and length distributions of both post-consumer [11,13,14] and pre-consumer textiles [14,20,21]. Yarns made with MR cotton have been produced mainly by open-end spinning [12,15,16,17,18,19,20] but also by ring spinning [14,22] and compact ring spinning [16]. There is a need for studies arching from the primary fibre or textile properties through to a thorough analysis of secondary textile properties. The opening parameters have been examined through reverse engineering to understand what kinds of textiles are more suitable for mechanical recycling [11,21,23]. There is a gap linking this data to yarn spinning. There is another gap between understanding the fibre properties and their impact on yarn properties, as only a few studies [14,17,20] touch upon the subject before this study. Disregarding the fibre analysis, the properties of MR yarns and their effect on fabric production has been studied by some [12,15,17,22].
In addition to the heterogeneity of textile waste and the short fibre length, the small number of available mechanical recycling technologies [9], as well as the tendency of MR fibres often becoming raw material for products of lower value, such as insulation [24,25], are the other hurdles on the way to truly sustainable fibre-to-fibre recycling. To be preferred over recycling, the reduction of waste should be considered a priority within the textile industry. Considering the top position of cotton as the most abundant natural fibre, and all its widely reported negative environmental effects [26], prioritizing recycling of cotton and consequently slowing down virgin cotton production is considered important.
One aim of this study is to characterise mechanically opened fibres and establish the properties of ring spun yarns and single jersey knits produced with the fibres. This study examined the properties—namely, the tenacity, elongation, fineness and length—of three different post-consumer cottons and one pre-consumer cotton. Moreover, a qualitative analysis of the composition of mechanically recycled cotton fibres was made against the virgin cotton. The fibres were ring spun into yarns obtaining various compositions and thicknesses and further knitted into single jersey fabrics that were tested for rubbing.
The other aim of this study is to highlight the significance of familiarizing oneself with post-consumer textiles, the amount of which can be expected to increase due to recent legislation. In this paper, the familiarization is conducted through an analytic comparison of virgin, post- and pre-consumer cotton fibres. The qualitative composition analysis of fibres offers valuable information about the thought-of quality of mechanically recycled cotton and its cleanness. While recycled cotton is often used in compositions below 50% [12,14,15], this study shows a possibility of using at least 75% recycled content in a yarn.

2. Results

2.1. Fibre Characterisation

2.1.1. Efficiency of Opening

The mechanically opened cottons and the primary, reference cotton were cleaned with the ‘Shirley’ Trash Analyser. The analyser separated the cotton into accept and reject. The efficiencies of opening were calculated, as described by [27], after the cleaning by comparing the accept weight to the total input weight of the raw material. The efficiencies of opening (EFO) varied between 51% and 68% for the mechanically opened cottons (Figure 1), and most of the unopened threads were separated during the cleaning; see Figure 2b and Figure 3b. The primary cotton, vCO, obtained an EFO of 88% with the lint forming most of the reject (Figure 2a and Figure 3a).

2.1.2. Fibre Length

The fibre lengths were measured on a manually operated apparatus, adjusting the American standard and a Suter-Webb comb method. The number of fibres was not known, and the mean length was calculated according to the average length of the length groups. The mean lengths are reported in Table 1. A single-factor ANOVA (confidence level α = 0.05) and a pairwise comparison revealed that the vCO fibre length is statistically significantly different from the other fibres, and the pre-CO fibre length is different from the post-CO fibre lengths. The obtained post-CO fibre lengths were not concluded to be significantly different from one another.
Some of the fibres were lost in the measuring process, some were unmeasurable, and some unopened threads and neps were discovered. The unopened threads and neps were removed by hand during the length measurements. The vCO sample had no threads or neps. The opening qualities of the different mechanically opened cottons are presented in Figure 4. The values are calculated by comparisons of weight share.
All the samples included an amount of very short fibres referred to as fibre dust. The fibre dust was unmeasurable for length, even if the samples were measured for their length to the authors’ best ability. The weight of unmeasurable fibres (neps, threads, dust) was in general higher for the post-consumer fibres and almost similar between vCO and pre-CO. There were no clear differences between the post-consumer samples.

2.1.3. Fibre Tensile Properties

The tensile properties of the fibres were tested on single-fibre measurements with a Textechnos Favimat+ using a 10 mm gauge distance. The vCO was tested as the average of 10 single-fibre measurements and the mechanically opened cottons as the average of 20 fibres. Their breaking tenacities, elongations and linear densities alongside the standard deviations and coefficients of variation are reported in Table 2. The average force–elongation curves are shown in Figure 5.
There are subtle differences in the tenacities, elongations, and linear densities between the fibres (Table 1). However, the average breaking curves do not display significant differences between the cotton types (Figure 5). A single-factor ANOVA revealed there are no statistically significant differences with a confidence level α = 0.05, as the p-values are 0.24 for fibre tenacity, 0.09 for fibre elongation and 0.11 for fibre linear density.

2.1.4. Surface Inspection

The surface inspection was conducted with scanning electron microscope (SEM) after gold coating of the samples. Selected results of the accept samples are shown in Figure 6a–e. When compared with the primary, reference cotton, the surfaces of the mechanically opened fibres generally seemed to be in as good a condition (Figure 6a). However, there was some fibrillation damage (Figure 6c), dirt (Figure 6b–e), uneven fibre thicknesses (Figure 6e) and a variation in fibre types (Figure 6d) in the mechanically opened samples that were not identified for the primary cotton.
It was observed that in general, the post-consumer fibres had particles attached on their surfaces, which indicated that there was dirt in post-consumer fibres. The signs of mechanical damage caused by the opening lines were scarce. Figure 7 shows possible damage of the mechanical opening line: cuts and shreds of individual fibres were detected on some of the samples.

2.1.5. Fibre Composition

The chemical compositions of the samples were examined with differential scanning calorimetry (DSC). The samples were observed between the temperatures of 20 °C and 300 °C. The degradation of cotton cannot be seen at this temperature scale, but melting points of common polymers used in textiles, such as polyamide or polyester, could be observed. Figure 8 and Figure 9 show the DSC curves of the samples during the first and the second heating, respectively. Marked in the pictures is a vertical line at 250 °C to visualise the typical melting point for some types of polyester.
There were no peaks detected for the vCO and pre-CO samples. For the post-consumer samples there are melting peaks between the 250 and 260 °C areas. The melting peaks of the uncleaned samples are more distinctive than the peaks of the accept samples. In general, all peaks are less sharp during the second heating, although the changes in enthalpy are not significant for the peaks at around 250 °C. The enthalpy changes for the accept samples are from 2.44 J/g to 1.55 J/g for post-CO1, 3.41 J/g to 2.75 J/g for post-CO2 and 3.93 J/g to 3.5 J/g for post-CO. For the uncleaned samples, the changes in enthalpy are 5.96 J/g to 3.54 J/g for post-CO1, 22.46 J/g to 17.18 J/g for post-CO2 and 13.67 J/g to 10.59 J/g. Figure 10 shows melting for post-consumer uncleaned samples between 20 and 30 °C during the second heating. This melting is not observed for the other cottons.

2.2. Yarns

Yarn Tensile Properties

Mechanically opened pre- and post-consumer cotton fibres were blended with primary cotton fibres in different ratios and ring spun to yarns with a targeted linear density of 40 tex. The recycled fibre content varied between 25% and 75% (Table 3). The mechanical properties of the yarns were rather similar and in the typical level of 40–50 tex ring spun cotton yarns. From all the opened fibres it was possible to spin yarn with 50% of recycled content. The mechanical properties of the yarns with 50% recycled content were similar, and no clear effects were detected whether the fibres originated from pre- or post-consumer textiles. The yarn from the post-consumer sample containing elastane (post-CO3) showed slightly lower tenacity compared to other yarns with a 50% recycled fibre content. The post-consumer sample opened with softener allowed an increase in recycled fibre content to 75%. However, the yarn tenacity was decreased from 3.8 cN/tex to 2.8 cN/tex. The pre-consumer sample opened with softener did not withstand the increase in recycled fibre content to 75%. The carding was still possible, but the drawing of the sliver failed. However, when softener was added to fibres before carding, it was possible to increase the recycled fibre content to 75% without decreasing the yarn tenacity.
The breaking strength of the yarns tended to increase with a decreased linear density. Moreover, increasing the recycled fibre content with post-consumer fibres, tenacity and elongation seemed to decrease and linear density increase.

2.3. Knits

Martindale Tests

All ring spun yarns shown in Table 3 were knitted with a laboratory-scale circular knitting machine to single jersey knits.
Resistance to abrasion of the knitted fabrics was tested according to EN-ISO 12947-2 using the Martindale abrasion instrument. The samples were subjected to a rubbing motion until knitted fabric threads were broken or the number of 20,000 revolutions was reached. Knitted fabric weight loss was determined as the difference in the weight of fabric samples before and after the Martindale abrasion test. The break point (14,000, 17,000 or 20,000 rubs) and weight loss (%) are shown in Figure 11.
There were no thread breakdowns with most of the samples after 20,000 rubs. Post-CO1, consisting of the smallest percentage of recycled fibres i.e., 25%, was broken already after 14,000 rubs with a relatively high weight loss-%, 15.8%. Surprisingly, the post-CO2 sample (75% recycled fibre) had only a 12.6% weight loss after 20,000 rubs. The lowest weight losses were obtained with pre-CO samples.

2.4. Correlation Analysis Results

The correlations and their significance were tested with regression analysis for a selection of results. For the sake of cohesion, the fibre properties were given to different yarns in the same proportion as the contents of the yarns in terms of virgin and recycled fibres (see Table 4). Although there are correlations >0.5 for many properties, the only fibre property affecting the yarn properties with a statistical significance (p-value < 0.05) is the fibre tenacity. Its effect on yarn tenacity and yarn linear density obtain p-values of 0.023 and 0.011, respectively. Table 5 shows the correlations and p-values for fibre properties (fibre length, fibre tenacity, fibre elongation, fibre linear density, amount of measurable fibres) relative to yarn properties (yarn tenacity, yarn elongation, yarn linear density) and fabric properties (weight loss by abrasion) and fabric abrasion resistance relative to yarn properties.

3. Discussion

The fibre characterisation was conducted by comparing the efficiencies of opening, fibre length, tensile properties, appearance and the chemical composition of the fibres. The efficiency of opening is rather an opening line property than a fibre property [27], and its values were deviating even between the post-consumer samples opened on the same opening line. The ‘Shirley’ Trash Analyser is designed for the cleaning of cotton, which can also be seen in the results. The vCO cotton obtained an EFO of 88.1%, and Figure 3a shows how only the lint and other dirt was separated off the clean fibre. Figure 3b shows a similar result for pre-CO in terms of accept versus reject size, but the reported EFO for pre-CO in Figure 1 is only 53.4%. The low EFO is most likely due to the instrument not being able to separate only the unopened threads but removing some opened fibre, too. On the other hand, the unopened threads are likely heavier than lint and take up a great share of the initial weight, thus decreasing the EFO. Conclusively, the EFO of vCO cotton should be compared with the EFOs of the mechanically opened cottons with caution. The EFOs can be increased by a more efficient opening of the textile on the opening line, by for example increasing the number of opening cycles. However, it has also been reported that an increase in the number of opening cycles may decrease the fibre length [25] resulting in difficulties in spinning.
The result of the fibre length measurements suggests that the fibre lengths are reduced during mechanical opening. This result has also been reported by other studies [11,14,25]. The suggestion is based on the result that the vCO mean length was longer than the studied mechanically opened fibres. However, there is no data of the actual fibre lengths before the mechanical opening for the textile waste. For the analysis and comparison of the results, it needs to be assumed that the vCO is similar to a type of cotton fibre suitable for use in denim production. The fibre length reduction is caused by a variety of factors: Firstly, the textile is cut in pieces for a more effective opening, and, depending on the cut size, the fibres can be shortened already under the guillotine. Secondly, the opening line parameters, such as speed, cylinder size, number of cylinders or opening settings, are adjusted to the shredded material to achieve the desired output [23,25]. Lastly, the inherent fibre properties such as fabric structure, yarn structure, colour, tenacity and fibre length, etc., could play their role in the output fibre properties. Denim is often produced with coarser, open end spun yarns that have been reported easier to detangle than ring spun yarns [14]. Shorter fibres are also easier to detangle than long ones [11]. It can be assumed that the denim fabric in pre-CO and the jeans in post-consumer samples are made with coarser yarns, but there is a possibility of deviation in the fibre lengths depending on the spinning methods, number of twists and other yarn and fabric properties.
In this study, a softener was used in the opening of pre-CO and post-CO2 fibres. Softener use has been reported to positively contribute to fibre length [21], while other studies [28] have shown softener use does not seem to have an effect on fibre quality but rather on the yarn quality. Similarly, in this paper, post-CO2 fibre length was not found to be significantly different from the other post-consumer cottons. The length of pre-CO was shown to be statistically significant from the post-consumer MR fibres; however, this can be due to other opening parameters or the overall quality of the denim fabric. The effect of softeners and lubricants should be studied further.
The tenacities of the opened fibres were established on single-fibre tensile tests. The measurements showed little to no difference between the different cotton types for the breaking tenacity and elongation or the linear density. Similar results, without significant differences in the linear density between virgin and mechanically opened cotton fibres, have been presented earlier [14,17]. Yuksekkaya et al. [17] tested the tenacity of fibre bundles of virgin and mechanically recycled cotton fibres respectively. They found a subtle decrease in the tenacity of white pre-consumer cotton fibres compared to virgin fibres. Especially, the post-consumer samples presented in the results of this paper may consist of fibres other than cotton; there are yarns from seams, possible embroidery and care labels included in the mix. The fibres used to make these may deviate the result and not give a clear picture of what the breaking tenacity and elongation of pure cotton would be post-opening. Additionally, primary cotton fibres have differences, and it must be assumed that the vCO sample could be used for denim manufacturing to allow a somewhat objective comparison of the results. The ANOVA or Tukey test did not conclude any differences, so the hypotheses of MR fibres’ reduced or increased tenacity, elongation or linear density cannot be rejected. For the purpose of ring spinning and knitting, all the MR fibres were deemed suitable.
The SEM imaging showed no significant damage on the fibre surfaces of the MR fibres. Post-consumer textile waste can sometimes be worn out and thus damaged [29], and the blades of the mechanical shredding lines could impose damage on the fibres. These results suggest, however, no surface damage is present on a wider scale, and only individual flaws could be detected. Aronsson et al. [11] have earlier discovered the wearing out of garments does not necessarily reduce the fibre length. There is no way of knowing the level of wearing out of the post-consumer jeans studied here. However, the SEM pictures do not indicate any barriers for using these MR fibres as raw material for yarn spinning or other textile products.
The sorting of post-consumer jeans was performed by colour and contents of the garments. Although samples post-CO1 and post-CO2 were first collected as “blue denim”, and post-CO3 as “black denim”, controlling the fractions is difficult. For pre-consumer samples the colour control may be easier. Nevertheless, Figure 2b shows the variety of blue shades that made up the sample pre-CO. In cotton denim, warp yarns determine the colour, while weft yarns are often left undyed. Thus, natural colours will end up in the mechanically opened fibre mix with the dark warp yarns, resulting in a mélange colour; see [14,30].
The fibre composition analysis was conducted with DSC. The melting peaks between 250 and 260 °C suggested the presence of a melting material, such as polyester, which is widely used in seam yarns and embroidery. A commonly used polyester, polyethylene terephthalate (PET), has melting points at 530–540 K, i.e., 256–266 °C [31], and a moderate degree of crystallinity [32]. The differences between the first and the second heating indicate that the molecular structure of the test specimen changes when heated. In the post-consumer cotton samples, where melting peaks can be observed, the peaks are less defined during the second heating. The cause of the melting peak differences can be due to the polymers melting and degrading, re-crystallising and presenting differently upon secondary heating. Due to its moderate crystallinity, PET is prone to side reactions, such as branching or crosslinking new reactive groups, when heated. The modification changes the crystalline structure of the polymer, presenting differently during new heating and cooling cycles. The differences between the total enthalpies of the melting peaks during first and second heating around the temperature of 250 °C are not significant but suggest the molecular structure and crystallinity of the melting polymer has changed. Nonetheless, the presence of the melting peaks indicates melting behaviour, a thermoplastic property, not detected in 100% cotton samples. The post-consumer cottons are collected from consumers, making it impossible to say what type of polyester they might include. It is also unknown what other types of polymers or textile fibres they contain, and how those may react with PET. There is a requirement for accurate technology in identification and content quantification [33,34,35]. Inaccurate care labels [36] or missing care labels present challenges for efficient textile sorting and recycling. There is another gap in research in identifying all the different chemical treatments included in textiles and thus understanding their effect in textile recycling. DSC analysis could offer one way of quickly identifying possible other materials in post-consumer waste collected as “cotton” when care labels are missing or inaccurate.
Boschmeier et al. [34] reported a method for quantification of elastane in textiles. They found that the soft segments of elastane show a peak in the DSC second heating run at 20 °C, making them distinguishable from other commonly used textile fibres. In this study, melting peaks positioned between 20 °C and 30 °C were observed for post-consumer cottons during the DSC trials, as shown in Figure 10. While post-CO3 was collected as “black denim containing up to 10% elastane”, it is likely that post-CO1 and post-CO2 also contain elastane, as elastane is added to jeans for comfort [37]. As was earlier confirmed [34], DSC offers a feasible method for identifying elastane prior to recycling.
One of the aims of this study was to showcase the possibility to make yarns and knits with a high recycled content. The use of softener in carding processes prior to spinning can allow the increasing of the ratio of recycled fibres to virgin fibres in ring spun yarns. In this study, a yarn containing 75% pre-consumer fibres was successfully spun with 25% primary fibres, when softener was applied in the carding phase. Moreover, post-CO2 cotton was successfully spun with primary fibres with a 75/25 ratio without an additional softener in the carding phase. However, the 75% post-CO2 yarn was thicker and not as strong as the one with 75% pre-CO fibres. Interestingly, the correlation results in Table 5 suggest that increased single-fibre tenacity could decrease the overall yarn tenacity. This correlation has a p-value of 0.023, and although it seems contradictory, the reason could lie in the composition of the samples. Post-CO cottons receive higher tenacity values in single-fibre testing than vCO and pre-CO fibres, possibly affected by the unknown contents of the sample; it is possible that the fibre tenacity for post-CO cottons is made up by polyester or other fibres or affected by chemical treatments and physical modifications present in post-consumer textiles. However, the fibre tensile testing results showed no statistically significant differences between the different cotton types, and other causing factors for yarn tenacities could be in applied twist, fibre orientation or fibre packing during spinning processes. Moreover, the fibre strength positively correlated with yarn linear density as well (Table 5), with a p-value of 0.011. These results indicate there could be a relationship between fibre tenacity and yarn thickness and yarn strength.
According to the yarn tensile testing results, the use of softener in the carding phase could increase the potential for a higher content of MR fibres. While increasing the recycled content generally decreases the fibre tenacity and increases the linear density, the effect of softener seems to give opposite results, as seen in the pre-CO yarns. The knits made from the two yarns with 75% MR fibres experienced similar abrasion resistances to each other, with a slightly higher percentual weight loss than yarns made with 100% primary cotton. It is difficult to say whether the softener had a significant effect on any of these results. While the use of softeners in opening processes has been studied, it should be further researched, as to how and to what extent the use of softener in yarn spinning can contribute to yarn tenacity.
The fibre properties affecting spinnability, yarn properties and final knit properties are fibre type, fineness, length, tensile strength and resiliency [37]. As was seen in the yarn tensile testing results (Table 3), the addition of post-consumer recycled content increased the thickness and reduced the tenacity and elongation of yarns. As the tenacities of the MR fibres were like that of vCO (Figure 5) with no statistically significant differences, and the measured linear densities did not differ notably (Table 2), the resulting yarn tenacity must be attributed to something else. The fibre dust content (Figure 4) was higher in post-consumer samples, and the fibre length was shorter (Table 1) than the pre-consumer cotton and primary cotton fibres in this study. Reduced fibre length is often named as the most inhibiting parameter for the successful spinning of high-quality yarns [10,20,23,25]. The fibre length of vCO was statistically significantly different from the MR fibre lengths, and the pre-CO length was different from the other MR fibre lengths. The vCO and pre-CO yarns obtained higher tenacities than post-CO yarns, giving reason to believe fibre length also potentially affected the yarn strength in this study.
Lindström et al. [23] earlier called for research to evaluate the abrasion properties of different MR fibres, yarns and fabrics. The abrasion resistance is strongest in samples made with 100% vCO, 50% pre-CO, 75% pre-CO and 75% post-CO2. The latter, the yarn with 75% post-CO2 fibres, obtained the lowest yarn strength, while the other yarns experienced the highest tenacities. The strongest yarn strength was measured for the yarn including 25% post-CO1 fibres. However, the knit made of this yarn broke after 14,000 rubs, the only knit breaking so early. A Martindale value of 14,000 rubs is considered enough for a knitted fashion garment intended for everyday use [38]. Given the correlations between fibre or yarn properties and fabric weight loss, the most likely property to have some effect on abrasion resistance is the number of measurable fibres in the cotton. This hypothesis means that neps, unopened yarns, high short fibre content and other factors reducing the fibre length and quality should be limited in knits made with MR fibres. More research should be conducted to justify or elaborate the relationships between fibre, yarn and fabric properties.
Nevertheless, the abrasion resistance cannot be contributed to measurable fibres alone, but factors such as yarn twist, surface roughness and fibre blend homogeneity in the knit should be considered. The short fibres and a reduced fibre length uniformity lead to yarn irregularities [20]. The fibre packing may be difficult to control with varying lengths of fibres. Yilmaz et al. [39] used waste from cotton spinning processes and re-spun it into yarns with varying content. They found that ring spun yarns are sensitive to irregularities and thin and thick places the higher the waste content was. Properties such as yarn’s unevenness or hairiness could also play a role in abrasion resistance or resulting pilling [40]. The high content of unmeasurable fibres likely result in uneven yarns, further causing pilling or breaking. The generally more apparent weight loss for the post-consumer knits could be attributed to the longer mean length of vCO and pre-CO fibres and the higher fibre dust content of post-CO cotton samples. The presence of long fibres allows for better entanglement of fibres, resulting in yarns with better durability and less pilling. A yarn twist is often applied to increase the strength of the yarn, but too high a twist can cause spirality during knitting [41].

4. Materials and Methods

4.1. Fibres and Yarns

The recycled cotton materials studied in this report were obtained from two different mechanical opening lines, the pre-CO from one in Portugal and all the post-CO samples from another in Finland. The fibres are compared with a sample of primary cotton fibres, referred to as vCO (virgin cotton) in the text. All the fibre materials are reviewed in Table 6.
The pre-CO sample was obtained from pre-consumer denim waste, a woven twill fabric with a 100% cotton composition. The opening of pre-CO was conducted at Citeve with a pilot-scale opening line. Pre-CO fabric was passed through the cutting line twice. After the cutting, a softener (PANTOCTAL CT-40; Dilube, Spain) was sprayed on the fabric pieces before feeding them to the opening line. The fabric pieces were fed through the mechanical opening line with five opening cylinders according to the parameters in Table 7.
The post-consumer end-of-life textiles were collected by South-West Finland waste management company (LSJH). Jeans were manually identified and collected separately for mechanical opening. There were two classes for post-consumer jeans: blue denim clothing without elastane (post-CO1 and post-CO2) and black denim clothing with elastane (post-CO3). The material was identified with the help of care labels and occasionally with NIR. The identification of chemical treatments was not conducted, and it is therefore impossible to say if the post-consumer samples contain unknown chemical treatments or washing detergents. However, the post-consumer denim has been subject to use and laundering, so industrial treatments may have been washed off. The blue denim clothes were divided into two batches for the mechanical opening: one batch was opened as such (post-CO1), and for the other batch a softener was sprayed on directly after guillotine cutting and before fibre opening to reduce the friction in the shredding process (post-CO2). The post-consumer denims were mechanically opened with LSJH’s recycling line, which includes components for guillotine cutting, hard parts’ removal, fibre opening and fibre bale pressing. The fibre opening is based on mechanical opening cylinder technology, and the line has four opening cylinders. The capacity of the line is 1000 kg/h.
The fibres in Table 6 were used in yarn production at Citeve. A reference yarn with 100% vCO fibre was spun to compare the properties of the yarns that had mechanically opened fibres. Seven different yarns with mechanically opened cotton fibres were produced, with the recycled fibres used in varying amounts, namely 25%, 50% or 75% of the yarn contents. The recycled and primary cotton fibres were mixed in the desired ratios by hand and fed to the card. Selected samples were sprayed with a softener before feeding to the card. Samples were carded twice with a laboratory carding machine (Mesdan, Italy). The carded webs were fed to the draw frame (Mesdan Stiro Roving Lab, Italy) and drawn twice, finally winding the roving on a spool. The rovings were moved to the ring spinning unit (Mesdan Ring Lab, Italy) and spun into yarns with 1.2 pre-draft, 1100 twist/m and machine speed 5400 rpm. The draft was adjusted from 22 to 36 based on the tex number of the roving and to obtain 40 tex yarns.

4.2. Knitting

Knitted samples of the produced yarns were made using a laboratory-scale circular knitting machine (Tricolab) with a 3.75″ cylinder, gauge 14 (corresponding to 168 needles) and one single feeder. The chosen knit was single jersey for all knitted samples.

4.3. Fibre Characterisation

The fibres were cleaned with the ‘Shirley’ Trash Analyser prior to the testing. The instrument is engineered for cotton cleaning i.e., separating the lint and other dirt from cotton. The instrument provides an “accept” in one compartment and a “reject” in another. The accept, reject and uncleaned (obtained from the opening lines) fibre samples were used in the different characterisation tests to better suit the different requirements of the tests.
The fibre length measurements were executed on a manually operated comb apparatus, adjusting the American standard (ASTM 1440-07) and Suter-Webb array method. A bundle of 75 ± 2 mg of fibres was taken for each measurement. The bundle was drawn apart by hand, and the separated parts were laid on top of each other repeatedly, so that the fibres were parallel and straightened prior to the testing. Accept fibres were used for the fibre length measurements, as the unopened threads of reject and uncleaned samples were caught in the combs. The parallel, straightened fibres were brushed against the combs of the apparatus and set down at one end of the combs, between the teeth. A pair of wide-grasp forceps was used to pick a small tuft of fibres from behind the combs and place the tuft from the one end of the combs to the other. The ends of the fibres were aligned as close to the outermost comb as possible. The whole sample was moved down this way, until no fibres could not be picked up. The remaining fibres were picked up with a narrow-grasp forceps, straightened and laid down as before. This allowed for further picking of fibres to increase the measurable sample size. The picking up and laying down of the remaining fibres was conducted an additional third time until only dust-like fibres were left. The fibres that were moved down to the other end were then compressed between the combs’ teeth with a teethed depressor. The apparatus was then pivoted 180˚, and the combs nearest to the tester were dropped down successively until a fringe of fibres was visible. The fringe was picked up with wide-grasp forceps and laid down on a velvet board. Further combs were dropped down to allow for picking up of the successively shorter fibres. The laid-down fibres formed an array on the velvet board. After that, the fibres were divided into length groups (1–3, 4–6, 7–9, … mm), and the length groups were weighed to calculate the weight-based mean length (mm).
The mechanical properties of fibres were determined as an average of 10 and 20 measurements according to the ISO 1973 and ISO 5079 standards, using a Favigraph testing machine (Textechno GmbH, Germany). The testing speed was 20 mm min−1 and the gauge length 10 mm. The tests included titre (dtex), tenacity (cN dtex−1) and elongation (%).
The surface structures of the mechanically opened fibres were studied with a JEOL scanning electron microscope, model T100, after coating them with gold.
Differential scanning calorimetry (DSC) measurements were performed for ~3–8 mg fibre samples encapsulated in aluminium pans using a Netzsch DSC instrument. The temperature range was 20 °C to 300 °C, and the dynamic heating rate was 10 °C/min with a constant nitrogen gas purge of 50 mL/min.
A single-factor Analysis of Variance (ANOVA) was calculated for the fibre length, tenacity, elongation and linear density results. A pairwise comparison of fibre lengths was executed with the Tukey method.

4.4. Yarn Analysis: Tensile Testing

The linear density of the yarns was determined according to EN-ISO 2060 as an average of ten measurements. The breaking force and elongation were determined according to EN-ISO2062:2009 as an average of ten measurements with an automatic single-yarn strength tester. The yarns were conditioned at 20 °C and 65% RH for 24 h.

4.5. Knit Analysis: Abrasion Resistance

Abrasion resistance of the knitted samples was evaluated by using the Martindale abrasion instrument (James Heal, Halifax, UK) according to EN-ISO 12947-2. Two parallel samples were tested, and mean values were calculated, using 9 kPa pressure and standard wool fabric as an abradant material specified in EN-ISO 12947-1. The samples were subjected to a rubbing motion until knitted fabric threads were broken, or the number of 20,000 revolutions was reached. Knitted fabric weight loss was determined as the difference in the weight of fabric samples before and after the Martindale abrasion test.

4.6. Correlation Analysis

A correlation analysis was conducted to test the effect of fibre properties on yarns and fabrics, and yarn properties on fabrics, to support the credibility of the results. For the analysis, averaged fibre properties were calculated for yarns consisting of more than one of the studied cotton samples.

5. Conclusions

In this paper, the properties of mechanically recycled cotton fibres and their impact on yarn and knit properties were evaluated. To efficiently utilize the collected pre-consumer textiles, it advisable to aim for a high percentage of MR fibres in yarns. The attributes of yarn found in this study were similar to those of earlier ones; MR yarns often possess weaker tenacity due to decreased fibre lengths. They are also more uneven in both yarn silhouette and colour than yarns with only virgin fibres. The colour of MR/virgin blend yarns is often described as a mélange, as colour is a difficult parameter to control when collecting post-consumer waste. The texture and unevenness of yarns is affected by the different fibre properties in the recycling batch. This paper contributes to the highly topical theme of mechanical recycling by reaching the following conclusions:
  • The fibre dust in MR fibres may cause problems in spinning. Presence of fibre dust seems to affect the unevenness and tenacity of yarn, ultimately leading to lower abrasion resistance of knits. The best ways to eliminate fibre dust should be evaluated.
  • Post-consumer fibres can be used in ring spinning similarly to fibres obtained from pre-consumer sources. A steady 50%, and up to 75%, of MR fibres can be used in blends of MR and primary fibres.
  • There is no notable damage on post-consumer fibres, making them suitable for further processing.
  • Elastane and polyester are often present in post-consumer collected garments, and they are not removed by the mechanical opening processes.
  • The DSC offers a quick qualitative method to check for thermoplastic textile fibres, such as polyester or elastane fibres in cotton batches. It is a well-established method with room for improvement as a more analytical method.
It is proven that the mechanical recycling of post-consumer textile waste into new textile products is possible, and that the fibres can be characterised and spun into yarns with properties similar to yarns with virgin fibres. As the MR fibres are collected from two different mechanical opening lines, the adjustment of opening parameters is excluded in this study. The shredding process affects the MR fibre and yarn properties, as is shown by the results. While the opening and spinning parameters can be optimised, what we are less familiar with is what kind of textile waste will be collected and used in recycled textile products in the future.

Author Contributions

Conceptualisation, T.K., E.K., L.H., C.J.S. and J.M.G.; Methodology, E.K., T.K. and L.H.; Investigation, E.K., L.H., T.K., C.J.S. and J.M.G.; Writing—original draft preparation E.K., T.K. and L.H.; Writing—review editing, E.K., T.K., L.H., C.J.S. and J.M.G.; Project administration, T.K., L.H. and C.J.S.; Funding acquisition, T.K., L.H. and C.J.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was partially funded by Business Finland, grant number 6478/31/2021.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Acknowledgments

Senior Scientist Ugur Kaya and Research Scientist Emma Väre are acknowledged for offering help in analysing the DSC results and Senior Scientist Eetta Saarimäki is acknowledged for offering help in SEM imaging. Technical assistance from Kaisa Helminen is gratefully acknowledged.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
EFOEfficiency of opening
MRMechanically recycled
pre-COPre-consumer cotton
post-COPost-consumer cotton
vCOVirgin cotton

References

  1. Köhler, A.; Watson, D.; Trzepacz, S.; Löw, C.; Liu, R.; Danneck, J.; Konstantas, A.; Donatello, S.; Faraca, G. Circular Economy Perspectives in the EU Textile Sector; EUR 30734 EN; Publications Office of the European Union: Luxembourg, 2021; ISBN 978-92-76-38646-9. JRC125110. [Google Scholar] [CrossRef]
  2. Huygens, D.; Foschi, J.; Caro, D.; Patinha Caldeira, C.; Faraca, G.; Foster, G.; Solis, M.; Marschinski, R.; Napolano, L.; Fruergaard Astrup, T.; et al. Techno-Scientific Assessment of the Management Options for Used and Waste Textiles in the European Union; Publications Office of the European Union: Luxembourg, 2023; JRC134586. [Google Scholar] [CrossRef]
  3. European Environmental Bureau. Advancing Resource Efficiency in Europe: Indicators and Waste Policy Scenarios to Deliver a Resource Efficient and Sustainable Europe. Published 24 May 2014. Available online: https://eeb.org/library/advancing-resource-efficiency-in-europe/ (accessed on 27 June 2025).
  4. Manshoven, S.; Christis, M.; Vercalsteren, A.; Arnold, M.; Nicolau, M.; Lafond, E.; Mortensen, L.F.; Coscieme, L. Textiles and the Environment in a Circular Economy. Eionet Report—ETC/WMGE 2019/6. Available online: https://www.eea.europa.eu/publications/textiles-in-europes-circular-economy/textiles-in-europe-s-circular-economy (accessed on 27 June 2025).
  5. van Duijn, H.; Carrone, N.P.; Bakowska, O.; Huang, Q. Sorting for Circularity Europe: An Evaluation and Commercial Assessment of Textile Waste Across Europe. Published September 2022. Available online: https://www.fashionforgood.com/case-study/sorting-for-circularity-europe-an-evaluation-and-commercial-assessment-of-textile-waste-across-europe/ (accessed on 27 June 2025).
  6. Textile Exchange. Materials Market Report. 2024. Available online: https://textileexchange.org/knowledge-center/reports/materials-market-report-2024/ (accessed on 27 June 2025).
  7. Textile Exchange. Materials Market Report. 2023. Available online: https://textileexchange.org/knowledge-center/reports/materials-market-report-2023/ (accessed on 27 June 2025).
  8. McKinsey & Company. The State of Fashion 2025: Challenges at Every Turn. Published 11 November 2024. Available online: https://www.mckinsey.com/industries/retail/our-insights/state-of-fashion (accessed on 27 June 2025).
  9. Riemens, J.; Lemieux, A.-A.; Lamouri, S.; Garnier, L. A Delphi-Régnier Study Addressing the Challenges of Textile Recycling in Europe for the Fashion and Apparel Industry. Sustainability 2021, 13, 11700. [Google Scholar] [CrossRef]
  10. Heikkilä, P.; Heikkilä, J.; Kamppuri, T.; Keskisaari, A.; Määttänen, M.; Saarimäki, E.; Heikinheimo, L.; Koivula, A.; Rintala, N.; Harlin, A. Technologies and Model for Sustainable Textile Recycling. VTT Technical Research Centre of Finland. VTT Research Report VTT-R-00941-22. 2024. Available online: https://cris.vtt.fi/en/publications/technologies-and-model-for-sustainable-textile-recycling (accessed on 27 June 2025).
  11. Aronsson, J.; Persson, A. Tearing of post-consumer cotton T-shirts and jeans of varying degree of wear. J. Eng. Fiber Fabr. 2020, 15, 1–9. [Google Scholar] [CrossRef]
  12. Rabbi, K.F.; Banna, B.U.; Mia, R.; Islam, M.R.; Hasan, M.M. Utilization of post-consumer waste for sustainable denim manufacturing. Case Stud. Chem. Environ. Eng. 2023, 8, 100415. [Google Scholar] [CrossRef]
  13. Badara, O.; Rämö, V.; Rissanen, M.; Tehrani-Bagha, A. Mechanically recycled textile fibers in carded and needle-punched non-wovens: Implications on processability, structure, and performance. Text. Res. J. 2024, 95, 1617–1636. [Google Scholar] [CrossRef]
  14. Arafat, Y.; Uddin, A.J. Recycled fibers from pre- and post-consumer textile waste as blend constituents in manufacturing 100% cotton yarns in ring spinning: A sustainable and eco-friendly approach. Heliyon 2022, 8, e11275. [Google Scholar] [CrossRef] [PubMed]
  15. Sari, B.; Uzumcu, M.B.; Ozsahin, K. Analysing the effect of mechanically recycled cotton fibres from pre-consumer wastes on mechanical and fastness properties of knitted fabrics. Int. J. Cloth. Sci. Tech. 2025, 37, 663–678. [Google Scholar] [CrossRef]
  16. Ütebay, B.; Celik, P.; Cay, A. Valorization of fabric wastes through production of recycled cotton yarns by compact ring and open-end rotor spinning. J. Clean. Prod. 2023, 409, 137135. [Google Scholar] [CrossRef]
  17. Yuksekkaya, M.E.; Celep, G.; Dogan, G.; Tercan, M.; Urhan, B. A Comparative Study of Physical Properties of Yarns and Fabrics Produced from Virgin and Recycled Fibers. J. Eng. Fiber. Fabr. 2016, 11, 68–76. [Google Scholar] [CrossRef]
  18. Gun, A.D.; Akturk, H.N.; Macit, A.S.; Alan, G. Dimensional and physical properties of socks made from reclaimed fibre. J. Text. Inst. 2014, 105, 1108–1117. [Google Scholar] [CrossRef]
  19. Muthukumar, N.; Thilagavathi, G. Properties of knit fabrics made from recycled cotton/r-PET blended yarns. Indian J. Fibre Text. Res. 2024, 49, 252–256. [Google Scholar] [CrossRef]
  20. Jamshaid, H.; Hussain, U.; Mishra, R.; Tichy, M.; Muller, M. Turning textile waste into valuable yarn. Clean. Eng. Technol. 2021, 5, 100341. [Google Scholar] [CrossRef]
  21. Lindström, K.; Sjöblom, T.; Persson, A.; Kadi, N. Improving mechanical textile recycling by lubricant pre-treatment to mitigate length loss of fibers. Sustainability 2020, 12, 8706. [Google Scholar] [CrossRef]
  22. Raiskio, S.; Periyasamy, A.; Hummel, M.; Heikkilä, P. Transforming mechanically recycled cotton and linen from post-consumer textiles into quality ring yarns and knitted fabrics. WMB 2025, 3, 76–86. [Google Scholar] [CrossRef]
  23. Lindström, K.; van der Holst, F.; Berglin, L.; Persson, A.; Kadi, N. Mechanical textile recycling efficiency: Sample configuration, treatment effects and fibre opening assessment. Results Eng. 2024, 24, 103252. [Google Scholar] [CrossRef]
  24. Tang, K.H.D. State of the Art in Textile Waste Management: A Review. Textiles 2023, 3, 454–467. [Google Scholar] [CrossRef]
  25. Ütebay, B.; Çelik, P.; Çay, A. Effects of cotton textile waste properties on recycled fibre quality. J. Clean. Prod. 2019, 222, 29–35. [Google Scholar] [CrossRef]
  26. Chen, S.; Zhu, L.; Sun, L.; Huang, Q.; Zhang, Y.; Li, X.; Ye, X.; Li, Y.; Wang, L. A systematic review of the life cycle environmental performance of cotton textile products. Sci. Total Environ. 2023, 883, 163659. [Google Scholar] [CrossRef]
  27. Schwippl, H. The Increasing Importance of Recycling in the Staple-Fiber Spinning Process. Rieter Machine Works Ltd. Published December 2020. Available online: https://www.rieter.com/fileadmin/user_upload/services/documents/expertise/textile-technology/rieter-special-print-recycling-3379-v2-94958-en.pdf (accessed on 30 June 2025).
  28. Liu, Z.; Cano, F.; Ardanuy, M. The effect of the process conditions and lubricant application on the quality of yarns produced by mechanical recycling of denim-like fabrics. AUTEX Res. J. 2025, 25, 20250041. [Google Scholar] [CrossRef]
  29. Juanga-Labayen, J.P.; Labayen, I.V.; Yuan, Q. A Review on Textile Recycling Practices and Challenges. Textiles 2022, 2, 174–188. [Google Scholar] [CrossRef]
  30. Uddin, A.J.; Roy, P. Transforming melange fabric waste into mélange yarn employing compact, Siro, and compact-Siro spinning: A cleaner and sustainable strategy. Clean. Waste Syst. 2024, 8, 100142. [Google Scholar] [CrossRef]
  31. Kong, Y.; Hay, J.N. Multiple melting behaviour of poly(ethylene terephthalate). Polymer 2003, 44, 623–633. [Google Scholar] [CrossRef]
  32. Fried, J.R. Polymer Science and Technology, 3rd ed.; Prentice Hall: Upper Saddle River, NJ, USA, 2014. [Google Scholar]
  33. Cura, K.; Rintala, N.; Kamppuri, T.; Saarimäki, E.; Heikkilä, P. Textile recognition and sorting for recycling at an automated line using near infrared spectroscopy. Recycling 2021, 6, 11. [Google Scholar] [CrossRef]
  34. Boschmeier, E.; Archodoulaki, V.-M.; Schwaighofer, A.; Lendl, B.; Bartl, A. A novel quantification tool for elastane in textiles using thermal treatment. Polym. Test. 2023, 118, 107920. [Google Scholar] [CrossRef]
  35. Paz, M.L.; Sousa, C. Discrimination and Quantification of Cotton and Polyester Textile Samples Using Near-Infrared and Mid-Infrared Spectroscopies. Molecules 2024, 29, 3667. [Google Scholar] [CrossRef] [PubMed]
  36. Wilting, J.; van Duijn, H. Clothing Labels: Accurate or Not? Published April 2020. Available online: https://www.circle-economy.com/resources/clothing-labels-accurate-or-not (accessed on 10 August 2025).
  37. Eryuruk, S.H. The effects of elastane and finishing processes on the performance properties of denim fabrics. Int. J. Cloth. Sci. Technol. 2019, 31, 243–258. [Google Scholar] [CrossRef]
  38. Euratex Technical Clothing Group. Recommendations Concerning Characteristics and Faults in Fabrics to Be Used for Clothing. Published March 2006. Available online: https://www.etitex.be/ECLA%202006-03.pdf (accessed on 12 August 2025).
  39. Yilmaz, D.; Yelkovan, S.; Tirak, Y. Comparison of the Effects of Different Cotton Fibre Wastes on Different Yarn Types. Fibres Text. East. Eur. 2017, 25, 19–30. [Google Scholar] [CrossRef]
  40. Ute, T.B.; Celik, P.; Uzumcu, M.B. Utilization of Cotton Spinning Mill Wastes in Yarn Production. In Textile Industry and Environment; Körlü, A., Ed.; IntechOpen: London, UK, 2019. [Google Scholar] [CrossRef]
  41. Khan, A.A.; Jamshaid, H.; Mishra, R. Yarns in Knitting. In Knitting Science, Technology, Process and Materials: A Sustainable Approach; Jamshaid, H., Mishra, R., Eds.; Springer: Cham, Switzerland, 2024; pp. 13–44. [Google Scholar] [CrossRef]
Figure 1. The accepts, rejects, and the lost fibres measured after ‘Shirley’ trash cleaning. The dotted line shows the efficiency of opening (EFO) as described by [27].
Figure 1. The accepts, rejects, and the lost fibres measured after ‘Shirley’ trash cleaning. The dotted line shows the efficiency of opening (EFO) as described by [27].
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Figure 2. The sample appearance of (a) vCO and (b) pre-CO before cleaning.
Figure 2. The sample appearance of (a) vCO and (b) pre-CO before cleaning.
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Figure 3. The accept versus reject of (a) vCO and (b) pre-CO after cleaning.
Figure 3. The accept versus reject of (a) vCO and (b) pre-CO after cleaning.
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Figure 4. The measurable and unmeasurable fibres quantified for the different cottons. The unmeasurable fibres are unopened threads, neps, dust-like fibres and disappeared fibres (loss of weight).
Figure 4. The measurable and unmeasurable fibres quantified for the different cottons. The unmeasurable fibres are unopened threads, neps, dust-like fibres and disappeared fibres (loss of weight).
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Figure 5. The average force–elongation graphs for the different cottons, measured with a 10-millimetre gauge distance.
Figure 5. The average force–elongation graphs for the different cottons, measured with a 10-millimetre gauge distance.
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Figure 6. SEM pictures of the cotton samples magnified 500 times: (a) vCO; (b) pre-CO; (c) post-CO1; (d) post-CO2; (e) post-CO3.
Figure 6. SEM pictures of the cotton samples magnified 500 times: (a) vCO; (b) pre-CO; (c) post-CO1; (d) post-CO2; (e) post-CO3.
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Figure 7. SEM picture of post-CO2 sample magnified 200 times. The fibre in the middle may be broken by the mechanical opening line.
Figure 7. SEM picture of post-CO2 sample magnified 200 times. The fibre in the middle may be broken by the mechanical opening line.
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Figure 8. The DSC curves during the 1st heating.
Figure 8. The DSC curves during the 1st heating.
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Figure 9. The DSC curves during the 2nd heating.
Figure 9. The DSC curves during the 2nd heating.
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Figure 10. The DSC curves during the 2nd heating between 0 to 50 °C areas. The peaks on post-consumer samples indicate melting between 20 °C and 30 °C.
Figure 10. The DSC curves during the 2nd heating between 0 to 50 °C areas. The peaks on post-consumer samples indicate melting between 20 °C and 30 °C.
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Figure 11. The abrasion resistance and weight loss of different knitted fabrics.
Figure 11. The abrasion resistance and weight loss of different knitted fabrics.
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Table 1. The fibre mean lengths by weight distribution for each cotton sample.
Table 1. The fibre mean lengths by weight distribution for each cotton sample.
Mechanically Opened FibreMean Length by Weight Distribution (mm)Standard DeviationCoefficient of Variation
vCO18.80.920.05
pre-CO11.30.190.02
post-CO19.80.130.01
post-CO29.90.660.07
post-CO39.90.250.02
Table 2. The fibre tensile testing results.
Table 2. The fibre tensile testing results.
Mechanically Opened FibreNumber of SpecimensTenacity (cN/dtex)SD/CVElongation (%)SD/CVLinear Density (dtex)SD/CV
vCO101.910.96/0.507.45.57/0.752.180.24/0.11
pre-CO201.870.78/0.425.72.22/0.391.990.30/0.15
post-CO1201.870.85/0.455.72.94/0.522.210.38/0.17
post-CO2202.390.96/0.406.85.78/0.852.170.25/0.12
post-CO3202.481.72/0.699.98.15/0.822.230.33/0.15
Table 3. The yarn tensile testing results.
Table 3. The yarn tensile testing results.
Used FibreRecycled Fibre Content (%)Tenacity (cN/tex)Elongation (%)Linear Density (tex)
vCO05.75.537
pre-CO504.85.444
75 *6.73.830
post-CO1257.84.827
504.54.442
post-CO2503.85.452
752.84.254
post-CO3503.75.452
* Softener added to opened fibres before carding.
Table 4. The averaged fibre properties in yarns.
Table 4. The averaged fibre properties in yarns.
Yarn ContentsAverage Fibre Length (mm) in Yarns *Average Amount (%) of Fibres Measurable in Yarns **Average Fibre Tenacity (cN/dtex) in Yarns ***Average Fibre Elongation (%) in Yarns ***Average Fibre Linear Density (dtex) in Yarns ***
100% vCO18.862.711.917.42.18
50% pre-CO, 50% vCO
75% pre-CO, 25% vCO
15.162.051.896.62.09
13.261.721.886.12.04
25% post-CO1, 75% vCO 50% post-CO1, 50% vCO16.659.521.907.02.19
14.356.321.896.62.20
50% post-CO2, 50% vCO
75% post-CO2, 25% vCO
14.456.772.157.12.18
12.153.792.277.02.17
50% post-CO3, 50% vCO14.458.112.208.72.21
* See Table 1 for fibre values. ** See Figure 4 for fibre values. *** See Table 2 for fibre values.
Table 5. Correlation results of fibre properties with yarn and fabric properties, and fabric properties with yarn properties.
Table 5. Correlation results of fibre properties with yarn and fabric properties, and fabric properties with yarn properties.
Fibre/Fabric
Property
Yarn TenacityYarn
Elongation
Yarn Linear DensityFabric Weight Loss by Abrasion
Fibre length in yarnsCorrelation0.5070.612−0.455−0.317
p-value0.2000.1070.2570.444
Fibre tenacity in yarnsCorrelation−0.7790.0980.8310.355
p-value0.0230.8170.0110.389
Fibre elongation in yarnsCorrelation−0.3500.6040.4520.262
p-value0.3950.1130.2610.530
Fibre linear density in yarnsCorrelation−0.3210.3910.3630.502
p-value0.4380.3380.3770.205
Amount of measurable fibresCorrelation0.6650.278−0.639−0.614
p-value0.0720.5050.0880.105
Fabric weight loss by abrasionCorrelation−0.148−0.1540.186-
p-value0.7270.7160.659-
Table 6. The mechanically opened cottons used for the characterisation and the production of yarns and knits.
Table 6. The mechanically opened cottons used for the characterisation and the production of yarns and knits.
Fibre CodeRaw MaterialMechanical Opening Line
vCO100% primary cotton fibres-
pre-CO100% cotton, softener used during opening, pre-consumer denim waste (fabric)Citeve
post-CO198–100% cotton with other fibres, post-consumer denim waste (jeans)LSJH
post-CO298–100% cotton with other fibres, softener used during opening, post-consumer denim waste (jeans)LSJH
post-CO390–100% cotton with elastane, post-consumer denim waste (jeans)LSJH
Table 7. Parameters of the Citeve pilot-scale opening line.
Table 7. Parameters of the Citeve pilot-scale opening line.
Parameters1st Cylinder2nd Cylinder3rd Cylinder4th Cylinder5th Cylinder
Speed (rpm)16001800199521452300
Feeding speed (m/min)0.801.021.151.291.50
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Kärkkäinen, E.; Kamppuri, T.; Heikinheimo, L.; Silva, C.J.; Gomes, J.M. Characterisation of Fibre Mechanical Recycled Cotton Denim Fibres and the Effects of Their Properties on Yarns and Knits. Recycling 2025, 10, 177. https://doi.org/10.3390/recycling10050177

AMA Style

Kärkkäinen E, Kamppuri T, Heikinheimo L, Silva CJ, Gomes JM. Characterisation of Fibre Mechanical Recycled Cotton Denim Fibres and the Effects of Their Properties on Yarns and Knits. Recycling. 2025; 10(5):177. https://doi.org/10.3390/recycling10050177

Chicago/Turabian Style

Kärkkäinen, Ella, Taina Kamppuri, Lea Heikinheimo, Carla Joana Silva, and Joana M. Gomes. 2025. "Characterisation of Fibre Mechanical Recycled Cotton Denim Fibres and the Effects of Their Properties on Yarns and Knits" Recycling 10, no. 5: 177. https://doi.org/10.3390/recycling10050177

APA Style

Kärkkäinen, E., Kamppuri, T., Heikinheimo, L., Silva, C. J., & Gomes, J. M. (2025). Characterisation of Fibre Mechanical Recycled Cotton Denim Fibres and the Effects of Their Properties on Yarns and Knits. Recycling, 10(5), 177. https://doi.org/10.3390/recycling10050177

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