Authors

  • Sharif Sulaymanov
    Andijan State Technical Institute

DOI:

https://doi.org/10.71337/inlibrary.uz.jasss.129491

Abstract

This scientific paper analyzes the types of silk waste and the standards applied in their recycling process. Adhering to the standards for waste generated in sorting and silk reeling sections helps to improve product quality.

 

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TYPES OF COCOON RAW MATERIAL WASTES AND THEIR APPLICATION IN

THE RECYCLING PROCESS..

Andijan State Technical Institute

Sulaymanov Sharif Abdumanabovich

Abstract:

This scientific paper analyzes the types of silk waste and the standards applied in their

recycling process. Adhering to the standards for waste generated in sorting and silk reeling

sections helps to improve product quality.

Keywords:

los, gumbak, defective, ugly, spotted, soft, hole, unraveled, thin-shelled silk, kaznok,

control skeins, seriplan reels.

ВИДЫ КОКОНОВЫХ ОТХОДОВ И ИХ ИСПОЛЬЗОВАНИЕ В ПРОЦЕССЕ

ПЕРЕРАБОТКИ.

Андижанский государственный технический институт

Sulaymanov Sharif Abdumanabovich

Аннотация:

В данной научной работе анализируются виды шелковых отходов и

стандарты, применяемые в процессе их переработки. Соблюдение стандартов для отходов,

образующихся на этапах сортировки и перекручивания шелка, помогает улучшить

качество продукции.

Ключевые слова:

лос, гумбак, дефектные, уродливые, пятнистые, мягкие, с дырками, не

перекрученные, тонкокожие шелковые отходы, казнок, контрольные мотки, сериплановые

катушки.

The demand for silk fiber in the global market has been increasing significantly year by year.

According to data from the International Silk Association Committee (ISAC), in recent years,

more than 153,000 tons of raw silk have been produced worldwide [1]. On a global scale, special

attention is being paid to the efficient utilization of raw silk, increasing the use of silk waste

fibers as secondary raw materials, improving product quality, expanding product assortments,

reducing production costs, and identifying and eliminating factors that negatively affect product

quality at all stages of initial processing and reprocessing of silk waste fibers. From this

perspective, improving the consumer properties of silk fiber and increasing the competitiveness

of silk products in the global market is considered of great importance.

It is well known that in recent years, our country has ranked fourth in the world in

silkworm cocoon production, following China (650,000 tons), India (280,000 tons), and Vietnam

(50,000 tons), producing over 26,000 tons of silk annually [2]. The process of raising silkworms

and obtaining high-quality cocoons is closely connected to the availability and quality of

mulberry leaves, which serve as the main feed for silkworms [3]. Therefore, in order to ensure

the production of high-quality and abundant silk cocoons in our Republic, a total of 50,193.3

hectares of mulberry plantations have been established. These plantations contain around 80.7

million mulberry saplings (Table 1).

Table 1.


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Area of existing mulberry plantations and the amount of fresh cocoons produced during the 2023

silk season in our Republic

№ Regions

Existing mulberry orchards

Quantity of produced live

silkworms, t

Orchards,

h

Single-row

mulberry

trees, one thousand

pieces

1

Republic

of

Karakalpakstan

2541,0

3283,2

852,6

2

Andijan

4683,1

5397,6

3303,4

3

Bukhara

5222

13582

3099,71

4

Jizzakh

2192

2350

641,5

5

Kashkadarya

7303,1

3923,5

3082,1

6

Navoi

1444,5

2783

1007,9

7

Namangan

3048,2

6177,7

2727,2

8

Samarkand

8262

10413,5

2829,75

9

Surkhandarya

3434,2

7617,4

1552,7

10 Syrdarya

1551,5

1591,1

616,0

11 Tashkent

3053,7

5719,9

1641,44

12 Fergana

3297

13354,4

2714,94

13 Khorezm

4158

4540,5

2178,36

Total

50193,3

80733,8

26347,6

In our country, there are currently 28 silk-reeling enterprises for full processing of

26,347.6 tons of raw silk produced. In these silk-reeling enterprises, a total of 2,139 tons of raw

silk is being processed, mainly in yarns with densities of 2.33 and 3.23 tex.

The existing silk-reeling enterprises in our country are mainly equipped with 80 series of

automatic silk-reeling machines and 10 series of mechanical silk-reeling devices manufactured in

China (FEIYU-2000 EX, FY-2000 EX, FY-2008, and KMS), South Korea (KSS-RS-100, KMS),

Japan (NISSAN), and Uzbekistan (KSM-10, KS-10). The total number of hooks amounts to

32,550 (Table 2) [4].

Table 2.

Silk production enterprises in Uzbekistan

Name

of

the

enterprise

Installed

device

or

machine brand (country

of manufacture and

year)

Installed series and

number of hooks

Type and quantity

of products being

produced

number

of

series

number of

hooks

Raw silk,

tex

tons

Republic of Karakalpakstan
1

“Asian Silk”

LLC (Vietnam)

FEIYU

2000

EX

(China 2010 y.)

2

800

2,33 and

3,23

50

Andijan region


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2

“Harir Tola” OJSC FEIYU

2000

EX

(China 2010 y.)

1

400

2,33 and

3,23

25

3

“Royal Silk” OJSC КСС- RS-100

(South Korea, 2000 y.) 4

1600

2,33 and

3,23

100

4

“Sapfir Sanoat”

NISSAN

(Japan 1982 y.)

3

90

Row silk 15

5

“Andijan

Xonoy

Silk” OJSC

FEIYU

2000

EX

(China 2010 y.)

2

800

2,33 and

3,23

50

Bukhara region
6

“Bukhara Brilliant

Silk” QK

FY- 2008

(China 2010 y.)

8

3200

2,33 and

3,23

150

7

“Romstar”

QK

FEIYU

2000

EX

(China 2010 y.)

4

1600

2,33 and

3,23

80

KMS- 10 (Uzbekistan

1986 y.)

2

240

2,33 and

3,23

20

8

“Silk

Service”

OJSC

KS- 10

(Uzbekistan

2004 y.)

2

300

2,33 and

3,23

56

9

“Qumushkent

Silk” OJSC

KMS (South Korea

2012 y.)

2

300

2,33 and

3,23

50

Jizzakh region
10 “Bunsan Silk” QK FEIYU

2000

EX

(China 2010 y.)

3

1200

2,33 and

3,23

75

Kashkadarya region
11 “Radian Silk” QK

FEIYU

2000

EX

(China 2013 y.)

4

1600

2,33 and

3,23

120

Navoiy region
12 “Richard

Best

Silk” OJSC

FEIYU

2000

EX

(China 2012 y.)

2

800

2,33 and

3,23

50

13 “Xatirchi

Pilla

Xazinasi” XK

FEIYU

2000

EX

(China 2012 y.)

1

400

2,33 and

3,23

25

Namangan region
14 “Golden

Silk”

LLC

FEIYU

2000

EX

(China 2009 y.)

4

1600

2,33 and

3,23

100

15 “Marjona

Fayz-

Fiber” OJSC

FY 2000 EX

(China 2007 y.)

2

800

2,33 and

3,23

50

16 “Veregrov

Silk”

OJSC

FY 2008

(China 2013 y.)

3

1200

2,33 and

3,23

100

17 “Oydinkul Trade

Service” XK

KMS- 10 (Uzbekistan

1990 y.)

1

100

Row silk 7

KS- 10

(Uzbekistan

1992 y.)

1

160

Row silk 12

Samarkand region


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18 “Jiloi Malika” XK KMS

(China 2012 y.)

1

400

Row silk 25

19 “Kumush

Fiber”

XK

FEIYU

2000

EX

(China 2012 y.)

1

400

2,33 and

3,23

25

20 “Elbek TRJ”

FEIYU

2000

EX

(China 2013 y.)

1

400

2,33 and

3,23

25

Tashkent city
21 “Great

Turan

Gold” OJSC

FY- 2000

(China 2004 y.)

5

2000

2,33 and

3,23

150

22 “Silver Silk” QK

FEIYU

2000

EX

(China

2006- 2007 y.)

11

4400

2,33 and

3,23

275

Tashkent region
23 “Ravnaq Silk” QK FEIYU 2000

(China 2007 y.)

2

800

2,33 and

3,23

50

24 “Singapoor-

Samarkand” QK

FEIYU

2000

EX

(China

2007- 2008 y.)

10

4000

2,33 and

3,23

250

Fergana region
25 “Nurli Tong Silk”

OJSC

FEIYU

2000

EX

(China 2011 y.)

2

800

2,33 and

3,23

65

26 “Vodiy Mirjoni”

XF

KMS- 10 (Uzbekistan

2001 y.)

1

160

Row silk 14

Surkhandarya region
27 “Inter Silk Pro”

QK

FEIYU

2000

EX

(China 2012 y.)

2

800

2,33 and

3,23

50

Khorezm region
28 “Khorezm Fiber”

OJSC

FY- 2000

(China 2008 y.)

3

1200

2,33 and

3,23

75

Analysis of the data presented in the above tables shows that, on average, more than 10–12 kg of

fresh cocoons are consumed to produce 1 kg of raw silk in our country. In particular, in 2022–

2023, the dry cocoon yield coefficient from fresh cocoons was 2.87 kg, which is higher than the

standard agrotechnical norm of 2.72 kg. On average, 1,000–1,100 tons of silk fiber waste of 11

types are generated annually in silk-reeling enterprises (Table 3). Of these, 7 types are suitable

for spinning into silk yarn, cotton-silk, and wool-silk blended yarns due to their physical-

chemical and physical-mechanical properties [5]. The remaining 4 types are not suitable for

producing silk or blended yarns using the current production technologies, but are widely used in

the production of artificial and synthetic fibers, nonwoven materials and fabrics, silk wadding,

paper, surfactants, thermal insulation materials, and other nanotechnology products [6].

Currently, even in countries with a well-developed silk industry, great attention is paid to

the production of valuable goods from silk fiber waste, primarily yarn made of pure silk or a

mixture of natural and synthetic fibers. These waste fibers are efficiently used as low-cost natural

resources to produce various high-value products. Silk fiber waste is also used to make filters for


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purifying water from motor and vegetable oils, films for biomedical and other applications,

membranes for imparting the properties of natural silk to carbon fibers, and other similar

products (Table 3).

Table 3.

Some characteristics of silk fiber waste

Type of silk fiber waste

Descriptions and specific properties

Linear

density

(mg/tex)

Breaking

strength

(cN)

Elongation at

break (%)

Sericin

content (%)

Cocoon floss

375-385

6-7

13-14

35-38

String

360-376

7-9

13-15

25-27

Tangled silk

355-370

7-9

14-16

25-27

Silk fragments

233-323

7-9

16-18

20-22

Reeling scraps

233-323

7-9

16-18

20-22

Test bobbins

233-323

7-9

16-18

20-22

1st-grade waste

265-302

5-6

11-13

18-20

Fiber cut from rollers

302-342

7-9

13-15

25-27

Seed cocoons

250-380

6-7

12-15

25-30

Double cocoons

260-400

6-7

13-15

25-30

Unreelable cocoons

232-305

5-6

11-14

25-27

Analysis of the data in Table 3 shows that the characteristics and properties of silk fiber waste

are quite similar. Therefore, they can be processed under the same conditions. However, it is

necessary to improve the initial treatment technologies and prepare the fibers for spinning.

Because for spinning yarn from silk fiber waste, the material must meet technological

requirements, especially regarding the residual sericin, oils, waxy substances, and soap content.

However, the incoming raw materials (waste) to spinning enterprises often have significantly

higher sericin and oil content. Annually, more than 1,000–1,100 tons of 11 types of silk fiber

waste are generated in silk-reeling enterprises (Table 3). Of these, 7 types are suitable for

spinning due to their physical-chemical and mechanical properties [9]. The remaining 4 types are

not compatible with current production equipment and are thus used for manufacturing artificial

and synthetic fibers, nonwoven fabrics, silk wadding, paper, surfactants, insulation materials, and

other nanotech products [10].

In the sericulture sector and silk-reeling enterprises, a large volume of defective cocoons and silk

fiber waste is generated. These waste materials are highly valuable in the national economy

because, for every kilogram of raw silk produced, about one kilogram of various waste is also

generated. Defective cocoons and silk waste are considered valuable raw materials in spun silk

production. Meanwhile, pupae are used as feed for animals and fish, as they contain about 50%

protein and 27% fat.

Silk-reeling waste is categorized by its origin: from sorting sections, reeling sections, and quality

control units. Waste from the sorting section includes cotton-like floss, defective cocoons, highly

stained cocoons, large-sized or smooth-surfaced cocoons, and those with deformities such as

hollow, thin-shelled, or double cocoons. Waste from the reeling section includes cocoon floss,


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reeling residues, unreelable cocoons, silk fragments, and pupae. The quality control unit

produces waste such as silk fragments, sample bobbins, and seriplan packages.

Main part. Reprocessing the waste generated in sorting sections requires adherence to several

standards. Cotton-like floss accounts for 0.3–0.5% of the dry cocoon mass and contains various

impurities, including up to 40% sericin. After processing, it is divided into two grades and

pressed into bales. The first grade includes clean, uniform-colored floss with no more than 1%

impurities. The second grade includes manually or mechanically cleaned floss with mixed colors

and up to 3% plant impurities. Sorted floss is pressed into bales not exceeding 40 kg. The yield

of defective and double cocoons varies (subject to change) depending on sorting practices.

Name

Value

Double cocoons

1-2

Deformed shape

0,2-0,4

Soft cocoons

1,5-3,0

Spotted (surface spots)

1-2

Internal spots

0,5-1,0

Partially reeled

0,5-1,0

Thin-shelled

0,3-0,6

Pierced

0,1-0,2

Other defective cocoons

0,9-1,8

Total:

6-12

In the cocoon reeling workshop, the cocoon waste (reeling waste) may contain no more than 1%

of unusable cocoons, tangled cocoons, and double cocoons in relation to the total waste mass,

and no more than 0.5% of condensed knots. The average mass of the initial section of the thread

extracted from the cocoon waste must not exceed 1.1 g.

The cocoon waste from automatic reeling appears in two forms:

• Waste wound around the RK machine wheel. This type is cut off every 1.5–2 hours during

operation, straightened, tied together with a thread, and collected into bundles. This waste may

contain up to 2% of unusable cocoons, unreelable cocoons, and double cocoons in relation to the

waste mass.

• Knot-shaped waste. This is manually loosened and sent to the waste processing section. It may

contain up to 2% of unusable cocoons and double cocoons. The moisture content of cocoon

waste is around 200%.

In the waste processing section, cocoon waste is washed and squeezed in a centrifuge,


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cleaned from foreign impurities, dried, sorted by color, and packed into bales. Double cocoons

are categorized as either normal (round or oval) or deformed. The normal type is preferable for

reeling silk with a linear density of 5 deniers or more, while the deformed type is more suitable

for spun silk production.

Conclusion.

Processing waste in the cocoon industry not only brings economic benefits but also

holds great ecological importance. Through recycling, valuable products can be derived from

waste, thus reducing environmental pollution. Each type of waste has specific processing

requirements. For example, cotton-like waste must go through special cleaning processes to

reduce impurities. This type contains sericin, and it can be divided into two grades: the first

grade with fewer impurities, and the second grade with more plant-based contaminants.

Defective cocoons include double cocoons, deformed, pierced, thin-shelled, or spotted cocoons.

Each requires individual cleaning and sorting procedures. Double cocoons, when unusable for

reeling, may be processed into feed for animals and fish due to their high protein and fat content.

For this purpose, proper feed standards must be followed. In conclusion, adhering to standard

requirements for waste recycling in cocoon production enterprises ensures efficient utilization of

materials. Proper processing of waste from sorting and reeling departments increases production

efficiency and enables the creation of useful products. Understanding the composition of cocoon

waste and the specific processing requirements at each stage plays a key role in quality control

and improves both environmental and economic performance of production.

Reference

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ISAC. Cooperation@srcic.com, Decomber 17, 2021

2.G‘ulomov A.E., Khabibullaev D.A., Azamatov U.N., Zaripov B.Z. Analysis of existing silk

enterprises in the republic and the products produced there // J.Textile Problems. №1. 2017. –

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the process of winding mulberry silkworm cocoons //Journal of scientific publications for

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Cocoons and Properties of the Cocoon Shell //Engineering. - 2019. - T. 11. – no. 11. – S. 755.

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with Surface Active Substances." Design Engineering (2021): 10636-10647.

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study of highly reinforcing chemical components in natural silk // Academic Research in

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8. Sulaymonov Sh. Application of surfactants obtained from industrial waste in cocooning

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900.

9. Rakhimov A. Yu., Rakhimov A. A., Sulaymonov Sh. A. Methods of cleaning silkworm waste

cotton-wool. Methods of cleaning silkworm waste // Scientific Conference. – 2020. – P. 135.


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Silk Road Chamber of international committee Zhangjiajie, China From the Secretariat of the ISAC. Cooperation@srcic.com, Decomber 17, 2021

G‘ulomov A.E., Khabibullaev D.A., Azamatov U.N., Zaripov B.Z. Analysis of existing silk enterprises in the republic and the products produced there // J.Textile Problems. №1. 2017. –P.35–42.

Rakhimov A. Yu., Sulaymonov Sh. A., Rakhimov A. A. Use of produced artificial sponge in the process of winding mulberry silkworm cocoons //Journal of scientific publications for graduate students and doctoral students. – 2015. – No. 4. – P. 160–161.

Alisher R. et al. Study of the Influence of Silkworm Feeding Conditions on the Quality of Cocoons and Properties of the Cocoon Shell //Engineering. - 2019. - T. 11. – no. 11. – S. 755.

Rakhimov A. Yu., Abdurakhmanov A. A., Sulaymanov Sh. A. Izuchenie primeneniya Vata-sdiry i puti uluchshenia kachestva kokonnogo syrya // Jurnal nauchnykh publikatsiy aspirantov i doktorantov. – 2015. – no. 4. – P. 152–157.

Abdumanabovich, Sulaymanov Sharifjon, Sativaldiyev Aziz Kahramanovich, and Sulaymanov Sharifjon. "Theoretical Fundamentals of Cocoon Ball Moisten and its Modification with Surface Active Substances." Design Engineering (2021): 10636-10647.

Sulaymanov Sh. A. Methods of preserving cocoons using chemical preparations through the study of highly reinforcing chemical components in natural silk // Academic Research in Educational Sciences. – 2021. – T. 2. – No. 12. – P. 407–413.

Sulaymonov Sh. Application of surfactants obtained from industrial waste in cocooning enterprises // Academic Research in Educational Sciences. – 2021. – T. 2. – No. 10. – P. 894–900.

Rakhimov A. Yu., Rakhimov A. A., Sulaymonov Sh. A. Methods of cleaning silkworm waste cotton-wool. Methods of cleaning silkworm waste // Scientific Conference. – 2020. – P. 135.

Rakhimov A. A. et al. Classification, characteristics and properties of natural silk waste // Bulletin of Science and Education. - 2020. - No. 5-1 (83). – S. 16–20.

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