Chemical Exposure from New Clothing: A Comparative
Case-Cum-Research Study of Nylon, Polyester, Cotton, Linen and Saree Fabrics
Across India and Selected Countries

Abstract
Clothing is generally considered a
protective barrier between the human body and the external environment.
However, textile manufacturing involves dyeing, bleaching, printing, finishing,
softening, wrinkle resistance, shrink resistance, water repellence and other
chemical treatments. Consequently, the biological safety of clothing cannot be
determined solely from whether a fibre is natural or synthetic.
This case-cum-research study
examines potential human exposure to textile chemicals in nylon, polyester, cotton,
linen and saree fabrics, with particular attention to azo dyes,
formaldehyde-releasing finishing agents and other textile auxiliaries. The
study compares the regulatory approaches of India, the European Union, the
United States, Switzerland and Japan. The European Union has particularly
developed restrictions on hazardous substances in clothing and skin-contact
textiles under REACH, while voluntary systems such as OEKO-TEX STANDARD 100
test finished textiles for a large range of harmful substances.
The study develops a comparative
analytical framework covering chemical exposure, skin-contact potential,
moisture/heat retention, consumer awareness, washing behaviour and perceived
adverse effects. Chi-square, independent-samples t-test, one-way ANOVA and
correlation analysis are proposed for empirical testing. The results
demonstrate why the statement "synthetic clothes are harmful" is too
broad. The scientifically stronger conclusion is that chemical treatment and
residual substances, rather than fibre origin alone, are important determinants
of textile-related health risk.
Keywords: textile chemicals, nylon, polyester, cotton, linen,
formaldehyde, azo dyes, textile dermatitis, REACH, OEKO-TEX, consumer health,
clothing safety
1. Introduction
Clothing comes into prolonged and
repeated contact with the human body. Under normal conditions, a garment may
remain in contact with the skin for several hours every day. The situation
becomes particularly relevant in underwear, shirts, trousers, sarees,
sportswear, children's clothing and bedding.
The textile industry uses numerous
chemical substances during fibre production, bleaching, dyeing, printing and
finishing. These chemicals can improve colour, softness, wrinkle resistance,
durability, shrink resistance, water repellency and appearance.
Dermatological evidence indicates
that textile contact dermatitis is more frequently associated with chemicals
used in textile processing than with the textile fibre itself. Formaldehyde finishing
resins, textile dyes and other chemical additives are recognised causes of
textile-related allergic or irritant reactions.
This creates an important research
question:
Does the health risk of new clothing
arise primarily from the fibre itself, or from the chemicals used to
manufacture, dye and finish the garment?
The distinction is particularly
important when comparing polyester and nylon with cotton, linen and traditional
Indian sarees.
2. Background of the Case
A consumer purchasing a new garment
normally observes:
colour;
softness;
shine;
texture;
price;
brand;
design;
comfort; and
durability.
The consumer normally cannot
observe:
residual formaldehyde;
restricted azo-dye cleavage products;
finishing chemicals;
dye carriers;
softeners;
resin residues;
heavy-metal impurities;
other restricted substances.
Consequently, a garment may appear
attractive and comfortable while its chemical composition remains largely
invisible to the consumer.
This is particularly important for
inexpensive fast-fashion garments, heavily dyed clothing, wrinkle-resistant
fabrics and garments marketed as "easy care", "permanent
press", "non-iron" or "stain resistant".
3. Problem Statement
The central problem investigated in
this study is the potential gap between:
consumer perception of textile
safety
and
the actual chemical composition and
regulatory compliance of finished clothing.
The study specifically examines
whether:
synthetic fibres such as nylon and polyester should
automatically be considered harmful;
natural fibres are necessarily safer;
formaldehyde-containing finishing treatments can affect
consumers;
azo dyes can create exposure concerns;
sweating and friction increase skin exposure;
new garments should be washed before first use;
consumer awareness is adequate; and
regulatory controls differ substantially between countries.
4. Research Objectives
Objective
1
To examine potential chemical
exposure associated with new nylon, polyester, cotton, linen and saree fabrics.
Objective
2
To investigate the role of
formaldehyde-containing finishing treatments in cotton, linen and other
fabrics.
Objective
3
To examine the potential
toxicological significance of azo dyes and aromatic amines.
Objective
4
To compare textile chemical
regulations in India and selected countries.
Objective
5
To examine consumer awareness
regarding textile chemical residues.
Objective
6
To analyse whether consumers report
more skin discomfort after wearing new garments before washing.
Objective
7
To determine whether fibre type
alone is a statistically significant predictor of reported skin discomfort.
Objective
8
To develop recommendations for consumers,
manufacturers, regulators and exporters.
5. Research Questions
Are nylon and polyester intrinsically harmful to human
health?
What chemicals are potentially present in new garments?
Can formaldehyde-based finishing agents remain in cotton and
linen?
Can azo dyes generate potentially hazardous aromatic amines?
Does sweating increase the possibility of chemical release
from textiles?
Are consumers sufficiently aware of textile chemical
exposure?
Do countries differ in their regulatory treatment of textile
chemicals?
Does washing new clothing reduce reported irritation?
Is skin discomfort related to chemical treatment rather than
fibre type?
6. Research Hypotheses
H01
There is no significant association
between fibre category and reported skin discomfort after wearing new clothing.
H02
There is no significant difference
in reported skin discomfort between consumers who wash new garments before use
and those who do not.
H03
There is no significant relationship
between consumer awareness of textile chemicals and the practice of washing new
garments before first use.
H04
There is no significant difference
in perceived chemical exposure risk among nylon, polyester, cotton, linen and
saree fabrics.
H05
There is no significant relationship
between sweating/friction exposure and reported textile-related skin
irritation.
7. Conceptual Framework
The study proposes the following
model:
Fibre type
↓
Dyeing / bleaching / finishing /
softening
↓
Chemical residues
↓
Sweat + heat + friction + prolonged
skin contact
↓
Potential chemical
migration/exposure
↓
Skin irritation / sensitisation /
dermatitis in susceptible individuals
The second pathway is physiological:
Synthetic or tightly woven fabric
↓
Heat and moisture retention
↓
Sweating
↓
Friction and microbial growth
↓
Irritation/intertrigo in susceptible
individuals
These two pathways should not be
confused.
8. Mechanism of Harm
8.1
Pathway I — Chemical Exposure
The chemical pathway includes:
Dye → residual chemical →
sweat/moisture → skin contact → absorption or local irritation
The risk depends upon:
chemical identity;
concentration;
residual amount;
duration of contact;
temperature;
sweating;
skin condition;
friction;
frequency of use; and
individual sensitivity.
Therefore, simply identifying a
polyester or nylon fibre does not establish toxicity.
9. Azo Dyes
Azo dyes are an important class of
textile colourants.
Research has demonstrated that some
azo dyes can be metabolised by skin microorganisms to aromatic amines. Certain
aromatic amines possess mutagenic or carcinogenic properties.
A Swiss study examining 153 clothing
textiles found potentially concerning non-regulated aromatic amines in 17% of
samples, with some samples exceeding 30 mg/kg and a maximum reported
concentration of 622 mg/kg. The study illustrates the importance of chemical
testing but does not mean that 17% of all clothing globally is unsafe.
The European Union has consequently
restricted clothing textiles containing specified carcinogenic, mutagenic or
reprotoxic substances under REACH.
10. Formaldehyde in Cotton and Linen
Cotton and linen are natural fibres,
but natural fibre does not mean chemically untreated.
During textile processing,
formaldehyde-containing resins may be used for:
wrinkle resistance;
crease resistance;
shrink resistance;
easy-care finishes;
durability;
antimicrobial applications in certain textile products.
Dermatological literature identifies
formaldehyde resins used in textiles as a potential cause of allergic contact
dermatitis. Sweat and sebum may facilitate release of free formaldehyde from
some formaldehyde-containing resins.
Thus:
Cotton ≠ automatically chemical-free
and
linen ≠ automatically chemical-free.
At the same time, this does not
mean that every cotton or linen garment contains hazardous formaldehyde
concentrations.
11. Sarees as a Special Indian Case
Sarees may contain:
cotton;
silk;
polyester;
rayon;
viscose;
nylon blends;
metallic threads;
dyes;
printing chemicals;
stiffening agents;
finishing agents;
softeners;
starches;
resins.
The traditional or cultural
character of a saree does not determine its chemical safety.
A handwoven natural-fibre saree and
an industrially finished synthetic saree may therefore have very different
chemical profiles.
12. Nylon and Polyester: Scientific Interpretation
The study deliberately rejects the
simplistic statement:
"All nylon and polyester
clothing is harmful."
Instead, the research proposition
is:
Nylon and polyester may present
exposure concerns when particular dyes, finishing chemicals, additives or
contaminants remain in finished garments, while the physical properties of some
synthetic fabrics may also influence heat, sweat and friction.
DermNet notes that natural and
synthetic fibres can all be associated with textile dermatitis, while chemical
additives are often the more important cause of allergic reactions.
Therefore, the correct comparison
is:
|
Factor |
Nylon |
Polyester |
Cotton |
Linen |
Saree |
|
Fibre origin |
Synthetic |
Synthetic |
Natural |
Natural |
Depends on fibre |
|
Dye requirement |
Often |
Often |
Often |
Often |
Often |
|
Finishing possible |
Yes |
Yes |
Yes |
Yes |
Yes |
|
Formaldehyde-resin treatment
possible |
Yes |
Yes |
Yes |
Yes |
Yes |
|
Azo dye exposure possible |
Yes |
Yes |
Yes |
Yes |
Yes |
|
Heat/moisture effect |
Product-dependent |
Product-dependent |
Generally breathable |
Generally breathable |
Highly variable |
|
Chemical-free automatically? |
No |
No |
No |
No |
No |
|
Health risk determined by fibre
alone? |
No |
No |
No |
No |
No |
13. Comparative International Regulatory Framework
13.1
India
India has a large textile
manufacturing and export sector and operates a system of BIS standards, textile
regulations and export-related requirements.
BIS maintains standards covering
numerous textile products and testing methods. For example, BIS lists standards
for polyester-blended woven shirting and suiting among its textile standards.
However, a major research issue is
that consumers generally do not receive a complete chemical inventory of every
garment.
13.2
European Union
The EU provides a particularly
important benchmark because REACH restricts specified hazardous substances in
clothing, related accessories, skin-contact textiles and footwear.
The EU's REACH framework restricts
33 CMR substances in clothing, textiles and footwear under Entry 72, applicable
from November 2020. The restrictions recognise possible consumer exposure
through skin contact, inhalation and accidental ingestion of textile dust.
The EU also introduced restrictions
on formaldehyde emissions from consumer articles, with textile articles
included within the relevant framework.
13.3
Switzerland
Switzerland provides an important
research example because published analytical research on clothing textiles has
detected potentially concerning aromatic amines in retail samples.
13.4
United States
The United States uses a combination
of federal chemical legislation, consumer-product regulation, state-level
chemical restrictions and voluntary textile certification systems.
The regulatory philosophy differs
from the EU's highly integrated REACH model, making the US useful for
comparative research.
13.5
Japan
Japan has developed
chemical-management and product-safety systems covering hazardous substances
and consumer products, while Japanese textile manufacturers and exporters may
additionally comply with international buyer standards.
14. OEKO-TEX as an International Benchmark
OEKO-TEX STANDARD 100 is
particularly relevant because it tests finished textile products for harmful
substances.
The system considers the intended
use of the product, with stricter requirements for products involving greater
skin contact. Product Class 1 applies to babies and young children, while
Product Class 2 covers products with direct skin contact.
OEKO-TEX reported that in its 2025
ECO PASSPORT testing data, 2.7% of 2,174 formaldehyde-related tests exceeded
the applicable threshold. This is not a prevalence estimate for all clothing,
because the tests concerned specific ECO PASSPORT submissions and parameters.
This distinction is essential in
academic writing.
15. Comparative Regulatory Table
|
Dimension |
India |
EU |
USA |
Switzerland |
Japan |
|
Textile chemical regulation |
Yes |
Extensive |
Extensive but distributed |
Strong |
Strong |
|
REACH system |
No |
Yes |
No |
Not EU REACH |
No |
|
Restricted hazardous substances |
Yes, through applicable
rules/standards |
Extensive |
Substance-specific |
Strong |
Substance-specific |
|
Voluntary textile certification |
Available |
Widely used |
Widely used |
Widely used |
Widely used |
|
Consumer chemical transparency |
Developing |
Relatively stronger |
Variable |
Strong |
Strong |
|
Export compliance pressure |
High |
Very high |
High |
High |
High |
|
Research concern |
Market compliance |
Chemical restrictions |
Fragmented regulation |
Analytical monitoring |
Chemical management |
16. Proposed Research Methodology
Research
design
A mixed-method case-cum-research
design is recommended.
Primary
research
Suggested sample:
300 consumers
India: 200
comparison-country respondents: 100
Sampling
Convenience sampling may be used for
exploratory consumer research, followed by purposive sampling for textile
retailers, manufacturers and dermatology/textile experts.
Secondary
sources
scientific publications;
PubMed;
government regulations;
BIS;
EU REACH;
OECD;
WHO/IARC where relevant;
OEKO-TEX;
textile industry reports.
Variables
Independent variables
fibre type;
garment colour;
finishing;
newness;
washing before use;
sweating;
duration of wear.
Dependent variable
reported skin irritation/discomfort.
17. Illustrative Consumer Dataset
The following table is a model
dataset for demonstrating statistical analysis. It must be replaced by
actual field-survey observations before publication as empirical research.
|
Fibre/category |
Sample |
Reported
irritation |
No
irritation |
|
Nylon |
50 |
15 |
35 |
|
Polyester |
50 |
14 |
36 |
|
Cotton |
50 |
9 |
41 |
|
Linen |
50 |
7 |
43 |
|
Saree fabrics |
50 |
10 |
40 |
|
Other/mixed |
50 |
11 |
39 |
|
Total |
300 |
66 |
234 |
Overall reported irritation:
66 / 300 = 22.0%
This is an illustrative statistical
demonstration and not a claim that 22% of consumers nationally experience
textile irritation.
18. Chi-Square Test
H0
There is no significant association
between fibre category and reported irritation.
H1
There is a significant association
between fibre category and reported irritation.
Using the illustrative table:
χ² ≈ 4.40
df = 5
p ≈ 0.49
Interpretation
At the 5% significance level:
p > 0.05
Therefore, the illustrative dataset
does not provide evidence that fibre category alone is significantly associated
with reported irritation.
This result is scientifically
valuable because it contradicts the simplistic assumption that "synthetic
= harmful."
The important implication is that chemical
treatment, individual sensitivity, garment construction, sweat, friction and
exposure duration should also be investigated.
19. Washing Before First Use
Illustrative data:
|
Consumer
practice |
Irritation |
No
irritation |
Total |
|
Washed before first use |
21 |
129 |
150 |
|
Not washed |
45 |
105 |
150 |
|
Total |
66 |
234 |
300 |
Illustrative chi-square result:
χ² ≈ 9.06
df = 1
p < 0.01
Interpretation
The illustrative model indicates a
statistically significant association between washing practice and reported
irritation.
However, this does not prove that
washing removes all harmful chemicals or that washing caused the reduction.
Actual research would need controlled testing of garments before and after
washing.
20. Consumer Awareness Analysis
Illustrative 5-point awareness
scale:
|
Group |
Mean
awareness score |
SD |
|
Consumers washing new clothes |
3.72 |
0.81 |
|
Consumers not washing new clothes |
2.84 |
0.92 |
Illustrative independent-samples
t-test:
t ≈ 8.72
p < 0.001
Interpretation
The illustrative result indicates a
significant difference in awareness between the two groups.
Again, the values are demonstration
data rather than observed population statistics.
21. ANOVA: Perceived Chemical Risk
Illustrative mean risk scores:
|
Fabric |
Mean
risk score |
|
Nylon |
3.71 |
|
Polyester |
3.64 |
|
Cotton |
2.91 |
|
Linen |
2.65 |
|
Saree |
2.88 |
Illustrative one-way ANOVA:
F(4,295) ≈ 8.31
p < 0.001
Interpretation
The illustrative ANOVA indicates
statistically significant differences in perceived risk among fabric
categories.
A post-hoc test such as Tukey HSD
would then identify which groups differ.
Importantly, perceived risk is
not equivalent to measured toxicological risk.
22. Correlation Analysis
Illustrative variables:
hours of daily clothing contact;
sweating frequency;
frequency of wearing unwashed new clothes;
skin discomfort score.
Illustrative Pearson correlation:
|
Variables |
r |
Interpretation |
|
Sweat × irritation |
+0.42 |
Moderate positive |
|
Unwashed-new-clothes × irritation |
+0.36 |
Moderate positive |
|
Awareness × washing |
+0.48 |
Moderate positive |
|
Daily contact time × irritation |
+0.29 |
Weak positive |
All four illustrative relationships
would require confirmation using real observations.
23. Comparative Risk Matrix
|
Exposure |
Nylon |
Polyester |
Cotton |
Linen |
Saree |
|
Dye-related exposure |
Medium |
Medium/High |
Medium |
Medium |
Medium/High |
|
Finishing chemicals |
Medium |
Medium/High |
Medium/High |
Medium |
Medium |
|
Formaldehyde-resin possibility |
Possible |
Possible |
Possible |
Possible |
Possible |
|
Sweat/friction concern |
Medium/High |
Medium/High |
Medium |
Low/Medium |
Variable |
|
Consumer awareness |
Low/Medium |
Low/Medium |
Medium |
Medium |
Medium |
|
Fibre alone establishes toxicity? |
No |
No |
No |
No |
No |
The table represents a research
framework, not laboratory measurements.
24. Body Parts Potentially Affected
Textile-related reactions may occur
particularly where clothing is tight, rubbing or heavily exposed to sweat.
Common areas include:
neck;
armpits;
waist;
inner thighs;
groin;
behind knees;
elbows;
back;
chest;
areas beneath tight elastic;
areas beneath bra/underwear;
face and neck where scarves or collars contact skin.
DermNet specifically notes that
textile dermatitis associated with formaldehyde-containing clothing may occur in
areas of substantial friction, including the inner thighs, gluteal folds and
backs of the knees.
25. New Clothing and the "Chemical Smell"
A noticeable odour from new clothing
does not by itself prove that the garment contains a dangerous concentration of
toxic chemicals.
Possible sources include:
finishing agents;
dyes;
packaging;
storage conditions;
volatile substances;
manufacturing residues.
Therefore:
smell ≠ proof of carcinogenicity
but
unusual chemical odour + prolonged
skin contact + irritation warrants
caution.
26. Is Formaldehyde a Carcinogen?
Formaldehyde is recognised as a
carcinogenic substance, but the health risk depends heavily on route,
concentration and duration of exposure.
The European Commission describes
formaldehyde as having carcinogenic and mutagenic properties and notes that it
can act as a toxicant and skin sensitiser.
However, the presence of a
formaldehyde-based finishing technology does not automatically establish that a
particular garment exposes its wearer to a carcinogenic dose.
This distinction is critical for
responsible academic research.
27. Why Natural Fibre Is Not Automatically Safer
The study proposes the following
principle:
Natural fibre describes the origin
of the fibre; it does not describe the chemical history of the finished
garment.
Cotton may undergo:
bleaching → dyeing → mercerisation →
softening → wrinkle-resistant finishing → washing
Linen may undergo:
scouring → bleaching → dyeing →
finishing → softening
Silk may undergo:
degumming → bleaching/dyeing →
finishing → softening
Therefore, "natural"
should not be interpreted as "chemical-free."
28. Why Synthetic Fibre Is Not Automatically Dangerous
Similarly:
Synthetic fibre describes the
material from which the fibre is manufactured; it does not by itself establish
the toxicity of the finished garment.
A polyester garment manufactured and
tested under strict chemical controls may have a lower chemical exposure risk
than a poorly processed cotton garment containing problematic finishing
residues.
Consequently, the correct scientific
question is:
What substances are present in the
finished garment, at what concentration, and under what exposure conditions?
29. International Comparative Case Findings
India
Large textile production and
domestic consumption create a need for stronger consumer awareness and
consistent testing.
European
Union
REACH provides a strong model for
restricting hazardous substances in clothing and skin-contact textiles.
Switzerland
Analytical research has demonstrated
the value of laboratory surveillance of clothing chemicals.
United
States
The regulatory framework is more
distributed across federal and state mechanisms.
Japan
Chemical-management controls and
demanding consumer/export markets encourage high compliance among major
manufacturers.
International
voluntary benchmark
OEKO-TEX STANDARD 100 demonstrates
how finished garments can be assessed according to intended skin contact and
harmful-substance criteria.
30. Major Findings of the Case Study
Fibre type alone is insufficient to determine textile health
risk.
Chemical processing is a major factor.
Azo dyes require particular attention because some can
release hazardous aromatic amines.
Formaldehyde-containing textile finishes can cause allergic
contact dermatitis in susceptible people.
Cotton and linen can also contain chemical finishing
residues.
Polyester and nylon can also be chemically treated and dyed.
Sweat, heat and friction may increase the likelihood of
local irritation.
New garments may benefit from washing before first use,
especially for sensitive consumers.
International regulation is increasingly focused on chemical
content rather than fibre origin alone.
Consumer awareness remains important.
Laboratory testing is necessary before making claims that a
specific garment is dangerous.
"Synthetic = harmful" and "natural =
safe" are both scientifically inadequate generalisations.
31. Managerial Implications
For
textile manufacturers
Reduce hazardous chemicals.
Use safer dyes.
Minimise formaldehyde-releasing finishes.
Maintain batch-level chemical testing.
Improve chemical traceability.
Adopt internationally recognised certification.
For
retailers
Provide chemical-safety information.
Encourage washing instructions.
Prefer certified suppliers.
Maintain supplier compliance documentation.
For
consumers
Wash new garments before wearing when practical.
Pay particular attention to garments with strong chemical
odours.
Avoid prolonged use if irritation develops.
Prefer certified textiles where available.
Choose breathable clothing for hot and humid environments.
Individuals with known textile allergies should seek
professional medical advice.
32. Policy Recommendations for India
Recommendation
1
Introduce stronger consumer-facing
chemical-safety information for garments.
Recommendation
2
Develop a standardised textile
chemical disclosure framework.
Recommendation
3
Increase random market testing.
Recommendation
4
Give greater attention to
formaldehyde, restricted azo dyes and aromatic amines.
Recommendation
5
Strengthen testing of children's and
underwear products because of direct skin contact.
Recommendation
6
Encourage OEKO-TEX or equivalent
certification for export-oriented and high-risk products.
Recommendation
7
Create a QR-based textile safety
disclosure system.
33. Proposed Textile QR Code
A future garment label could
provide:
QR CODE
→ Fibre composition
→ Country of manufacture
→ Dye category
→ Formaldehyde test result
→ Restricted azo-dye test result
→ Heavy-metal test
→ Certification
→ Batch number
→ Washing recommendation
→ Manufacturer
This would transform textile safety
from an invisible characteristic into a measurable consumer attribute.
34. Export-Import Implications
Chemical compliance is increasingly
important for Indian textile exporters.
A garment acceptable in one domestic
market may require additional testing or certification before entering another
market.
Therefore:
Textile quality = physical quality +
chemical safety + regulatory compliance + traceability.
This is especially relevant for
India's export competitiveness in the EU and other highly regulated markets.
35. Research Gap
Existing research frequently
examines individual chemicals, individual textile products or dermatological
outcomes.
A broader research gap exists in
integrating:
fibre type + textile chemicals +
consumer behaviour + washing practice + sweating + regulatory differences +
export compliance
within one comparative framework.
This study attempts to bridge that
gap.
36. Limitations
Textile chemical concentration cannot be established from
consumer perception alone.
Skin irritation has many possible causes.
Fibre composition varies between garments.
Finishing chemicals differ among manufacturers.
Washing behaviour varies.
Laboratory analysis is required to establish actual chemical
concentrations.
Cross-country comparisons are affected by differences in
testing methodologies.
Illustrative statistical tables in this paper are not
substitutes for laboratory or field data.
37. Conclusion
The case study does not support the
blanket conclusion that nylon and polyester are inherently harmful to the
human body.
Instead, the evidence supports a
more precise conclusion:
The potential health risk associated
with clothing is determined by the combination of fibre, chemical processing,
residual substances, exposure conditions and individual susceptibility.
Nylon and polyester may involve dyes
and finishing chemicals, while cotton, linen and sarees can also undergo
substantial chemical processing. Formaldehyde-containing finishing resins are
particularly relevant to textile contact dermatitis, while certain azo dyes can
generate aromatic amines of toxicological concern.
The most important policy shift is
therefore from:
"natural versus synthetic"
to:
"chemically tested versus
chemically unverified."
For consumers, washing new garments
before first use is a reasonable precaution, particularly for people who
experience textile irritation. For manufacturers and regulators, however, the
long-term solution is chemical testing, safer chemistry, traceability and
transparent labelling, rather than simply replacing synthetic fibres with
natural ones.
Selected References
Brüschweiler, B. J., & Merlot,
C. (2017). Azo dyes in clothing textiles can be cleaved into a series of
mutagenic aromatic amines which are not regulated yet. Regulatory Toxicology
and Pharmacology, 88, 214–226.
Brüschweiler, B. J., et al. Research
on non-regulated aromatic amines in clothing textiles. Regulatory Toxicology
and Pharmacology. The Swiss retail-sample study analysed 153 textile
samples.
DermNet. Textile Contact
Dermatitis. Discussion of textile fibres, formaldehyde resins, dyes and
other textile additives.
DermNet. Formaldehyde and
Formalin Contact Allergy. Evidence concerning textile exposure, sweating,
friction and allergic contact dermatitis.
European Commission. REACH
Restrictions. Restrictions on CMR substances in clothing, textiles and
footwear.
European Commission. (2023). Chemicals:
The EU restricts exposure to carcinogenic substance formaldehyde in consumer
products.
OEKO-TEX. STANDARD 100.
International textile safety certification and harmful-substance testing
framework.
OEKO-TEX. (2025). ECO PASSPORT
Findings. Textile chemical testing findings concerning formaldehyde and
other substances.
Bureau of Indian Standards. Textile
Standards. Indian standards relating to textile products and testing.
APPENDICES
Appendix A — Chemicals Used in Textile
Processing and Their Potential Effects
|
Chemical
/ chemical group |
Where
used |
Main
purpose |
Potential
human-health concern |
Particularly
relevant fabrics |
|
Formaldehyde
/ formaldehyde-releasing resins |
Finishing |
Wrinkle/crease resistance, easy-care finish |
Skin irritation and allergic contact dermatitis;
formaldehyde is classified as carcinogenic by IARC |
Cotton, linen, viscose, blends |
|
Azo
colourants |
Dyeing/printing |
Colouring |
Some restricted azo dyes can release carcinogenic
aromatic amines |
Cotton, polyester, nylon, wool and blends |
|
Disperse
dyes |
Dyeing synthetic fibres |
Colouring polyester/nylon and other synthetics |
Some disperse dyes are associated with allergic
contact dermatitis |
Polyester, nylon, acetate |
|
Phthalates |
Printing, coatings, plastics |
Flexibility/softness |
Some phthalates have endocrine/reproductive
toxicity concerns |
Printed textiles, coated fabrics |
|
Bleaching
agents |
Pre-treatment |
Whitening/cleaning |
Irritation if residues remain; process chemicals
require controlled handling |
Cotton, linen |
|
Sodium
hydroxide (caustic soda) |
Mercerisation/scouring |
Cleaning and fibre modification |
Strong irritant/corrosive in concentrated form;
finished textile risk depends on adequate processing/washing |
Cotton |
|
Hydrogen
peroxide |
Bleaching |
Whitening |
Irritation at sufficiently high exposure; normally
decomposes during controlled processing |
Cotton, linen |
|
Sodium
hypochlorite/chlorine compounds |
Bleaching |
Whitening/disinfection |
Irritation; undesirable by-products possible
depending on process |
Cotton and other washable textiles |
|
Heavy
metals such as lead/cadmium/chromium |
Dyes, pigments, trims |
Colour fixation/pigmentation or components |
Certain metals can cause systemic toxicity,
sensitisation or organ effects |
Dyed/printed textiles and trims |
|
Nickel |
Buttons, zippers, metallic accessories |
Hardware |
Allergic contact dermatitis in sensitised persons |
Clothing with metal components |
|
Organotin
compounds |
Certain finishing/coating applications |
Antimicrobial/industrial finishing |
Toxicological concern; restricted in many
applications |
Coated/treated textiles |
|
Perfluoroalkyl
substances/PFAS-related chemistry |
Water/oil/stain resistance |
Repellency |
Some PFAS are persistent and associated with
significant environmental and health concerns |
Outdoor/protective textiles |
|
Phenolic/chlorophenolic
compounds |
Historical preservative/antimicrobial applications |
Preservation |
Toxicological and environmental concerns;
restricted substances exist |
Certain treated textiles |
|
Softeners/fragrance
chemicals |
Finishing |
Softness and consumer appeal |
Can cause irritation or sensitisation in
susceptible individuals |
Cotton, linen, synthetic and blended fabrics |
Interpretation: The table demonstrates why “natural” and
“synthetic” are not sufficient classifications of textile safety. Chemical
processing must also be considered. OEKO-TEX STANDARD 100 specifically tests
finished textile products for a broad list of harmful substances and applies
stricter requirements as skin contact becomes more intensive.
Appendix B — Chemical Exposure Mechanism
|
Stage |
Textile
process |
Possible
chemical source |
Potential
exposure route |
Possible
outcome |
|
1 |
Fibre production |
Fibre-processing chemicals |
Residual contact |
Irritation/sensitisation |
|
2 |
Scouring |
Alkalis/detergents |
Residues |
Skin irritation |
|
3 |
Bleaching |
Peroxide/chlorine chemistry |
Residues/by-products |
Irritation |
|
4 |
Dyeing |
Azo/disperse/reactive dyes |
Direct skin contact |
Sensitisation/dermatitis |
|
5 |
Printing |
Pigments, binders, plasticisers |
Skin contact |
Irritation/sensitisation |
|
6 |
Finishing |
Formaldehyde resins, softeners |
Skin contact |
Dermatitis |
|
7 |
Packaging |
Volatile substances/odours |
Inhalation/contact |
Discomfort/irritation |
|
8 |
Wearing |
Sweat + heat + friction |
Skin exposure |
Increased local irritation |
|
9 |
Repeated wearing |
Cumulative repeated contact |
Prolonged exposure |
Persistent dermatitis in susceptible people |
|
10 |
Washing |
Removal of some residues |
Reduced exposure |
Potential reduction in irritation |
Research conclusion: The biological effect depends on the identity,
concentration, persistence and migration of the chemical, not merely
on the name of the fibre.
Appendix C — Nylon, Polyester, Cotton and
Linen: Comparative Evidence
|
Characteristic |
Nylon |
Polyester |
Cotton |
Linen |
|
Fibre origin |
Synthetic |
Synthetic |
Natural |
Natural |
|
Requires dyeing for coloured garments |
Usually |
Usually |
Usually |
Usually |
|
Can contain finishing chemicals |
Yes |
Yes |
Yes |
Yes |
|
Can use formaldehyde-based finishes |
Possible |
Possible |
Possible |
Possible |
|
Can contain restricted dye residues if poorly
controlled |
Possible |
Possible |
Possible |
Possible |
|
Heat/moisture behaviour |
Product dependent |
Product dependent |
Generally breathable |
Generally breathable |
|
Main textile-health concern |
Dyes/finishes + heat/friction |
Dyes/finishes + heat/friction |
Finishes/dyes |
Finishes/dyes |
|
Fibre itself proves toxicity? |
No |
No |
No |
No |
|
Chemical testing required? |
Yes |
Yes |
Yes |
Yes |
Key finding
The comparison does not justify the statement:
“Nylon and polyester are inherently poisonous.”
The scientifically defensible statement is:
Synthetic and natural textiles can both carry chemical residues; the
health relevance depends on the chemicals present, their concentration,
exposure conditions and individual susceptibility.
Appendix D — Formaldehyde: Fabric, Function
and Effect
|
Item |
Evidence-based
interpretation |
|
Chemical |
Formaldehyde |
|
Why used in textiles |
Certain finishing/resin technologies provide
wrinkle/crease resistance and easy-care properties |
|
Fabrics potentially affected |
Cotton, linen, rayon, blends and other treated
textiles |
|
Main route of concern |
Skin contact and, depending on circumstances,
inhalation |
|
Main dermatological concern |
Irritant or allergic contact dermatitis |
|
Is every treated garment dangerous? |
No |
|
Does natural fibre eliminate the concern? |
No |
|
Does washing necessarily remove all formaldehyde? |
Not
necessarily; effectiveness depends on the
chemical formulation and garment |
|
How should exposure be established? |
Laboratory testing |
|
Regulatory importance |
Formaldehyde is subject to restrictions/limits in
several regulatory and certification systems |
The European regulatory framework has specifically addressed formaldehyde
exposure from consumer articles, while textile certification schemes also
include formaldehyde testing.
Appendix E — Azo Dyes and Aromatic Amines
|
Parameter |
Finding |
|
Chemical group |
Azo colourants |
|
Main application |
Textile dyeing |
|
Main concern |
Certain azo dyes can reductively cleave to
aromatic amines |
|
Important distinction |
Not every azo dye is carcinogenic |
|
Restricted substances |
Specific carcinogenic aromatic amines are
restricted |
|
Exposure route |
Primarily prolonged skin contact for relevant
clothing |
|
EU approach |
Restricts specified azo dyes capable of releasing
listed aromatic amines above the applicable threshold |
|
Indian testing |
BIS standards/testing systems include aromatic
amines released from azo dyes |
|
Recommended analytical method |
Laboratory extraction and chromatographic analysis |
|
Consumer conclusion |
Colour alone cannot determine chemical safety |
EU REACH restricts azo dyes that can release specified aromatic amines above
30 mg/kg in relevant textile and leather articles intended for direct and
prolonged skin contact.
Appendix F — Indian BIS Chemical-Safety
Testing Evidence
Recent BIS documentation demonstrates that textile/product standards and
testing frameworks can include chemical parameters such as:
|
Chemical/parameter |
BIS
testing evidence |
|
Formaldehyde |
Included in applicable textile/product testing |
|
Aromatic amines from azo dyes |
Included |
|
Allergenic/carcinogenic disperse dyes |
Included in applicable requirements |
|
Chromium VI |
Included in applicable requirements |
|
Dimethyl fumarate |
Included in applicable requirements |
|
Organotin compounds |
Included in applicable requirements |
|
Chlorophenols |
Included in applicable requirements |
|
pH |
Included |
|
Phthalates |
Included |
|
Nickel/skin-contact parameters |
Included in applicable requirements |
BIS laboratory records explicitly list testing for formaldehyde, azo-dye
aromatic amines, allergenic/carcinogenic disperse dyes, chromium VI,
phthalates, pH and other chemical parameters under applicable product
standards.
Appendix G — Selected Regulatory Comparison
|
Parameter |
India/BIS
evidence |
European
Union |
OEKO-TEX
STANDARD 100 |
|
Formaldehyde |
Tested under applicable standards |
Restricted/controlled under applicable chemical
framework |
Tested |
|
Azo-derived aromatic amines |
Tested under applicable standards |
Restricted under REACH |
Tested |
|
Disperse dyes |
Tested under applicable product requirements |
Restricted substances under applicable frameworks |
Tested |
|
Phthalates |
Tested under applicable requirements |
Restricted in relevant articles |
Tested |
|
Heavy metals |
Tested where applicable |
Restricted substances in relevant products |
Tested |
|
pH |
Applicable textile requirements |
Product/standard dependent |
Tested where relevant |
|
Skin-contact sensitivity |
Product dependent |
Important for restrictions |
Requirements become stricter with greater skin
contact |
OEKO-TEX states that STANDARD 100 tests every certified component of a
textile article against a list of more than 1,000 harmful substances, with
requirements adjusted according to intended use and skin contact.
Appendix H — Actual Regulatory Limit
Examples
|
Substance/parameter |
Regulatory/example
limit |
Significance |
|
Azo-derived aromatic amines under EU REACH |
30 mg/kg
for specified amines in relevant articles |
Above the specified threshold, relevant azo dyes
are prohibited |
|
Formaldehyde in applicable EU consumer articles |
0.080 mg/m³ released formaldehyde
under the applicable restriction |
Addresses consumer exposure from relevant articles |
|
BIS example — formaldehyde |
300 ppm maximum
in the cited current BIS textile-product document |
Product-specific; not a universal limit for every
garment |
|
BIS example — pH |
5–9
in the cited product requirement |
Product-specific |
|
BIS example — total phthalates |
0.1% maximum
in the cited product requirement |
Product-specific |
Important: BIS limits are standard/product specific
and should not be presented as one universal Indian limit applicable to every
textile. The cited BIS document, for example, specifies 300 ppm formaldehyde
and 0.1% total phthalates for the particular product requirement in that
document.
Appendix I — Health Effects by Body System
|
Body
part/system |
Possible
textile-related effect |
Main
potential cause |
|
Skin |
Redness |
Dyes, finishing chemicals, friction |
|
Skin |
Itching |
Sensitising dyes/finishes |
|
Skin |
Contact dermatitis |
Formaldehyde resins, dyes and other allergens |
|
Skin |
Burning/irritation |
Irritant residues |
|
Neck |
Rash |
Collar/friction + chemical exposure |
|
Underarms |
Irritation |
Sweat + friction + dyes/finishes |
|
Waist |
Dermatitis |
Tight clothing + sweat + finishes |
|
Inner thighs |
Irritation |
Friction + perspiration |
|
Respiratory system |
Irritation in susceptible situations |
Volatile substances/dust |
|
Eyes |
Irritation |
Dust/volatile substances |
|
General comfort |
Heat/discomfort |
Fabric construction and moisture retention |
Important: These are possible associations, not proof that
a particular garment caused a disease.
Appendix J — Before-Washing and
After-Washing Evidence Framework
|
Fabric |
Before
washing |
After
washing |
Research
interpretation |
|
Nylon |
Chemical residues may be present |
Some removable residues may decline |
Requires laboratory comparison |
|
Polyester |
Dye/finishing residues may be present |
Some residues may decline |
Requires laboratory comparison |
|
Cotton |
Finishing/dye residues may be present |
Some residues may decline |
Formaldehyde release should be measured |
|
Linen |
Finishing/dye residues may be present |
Some residues may decline |
Laboratory confirmation required |
|
Saree |
Highly variable according to fibre and processing |
Variable |
Fibre and finish must be identified |
Research rule: Washing should be treated as a risk-reduction
precaution, not as proof that all chemicals have been removed.
Appendix K — Laboratory Results That Should
Be Reported
|
Test |
Unit |
Before
washing |
After
washing |
%
reduction |
|
Free/releasable formaldehyde |
mg/kg |
Laboratory
result |
Laboratory
result |
Calculated |
|
Aromatic amines |
mg/kg |
Laboratory
result |
Laboratory
result |
Calculated |
|
Phthalates |
mg/kg |
Laboratory
result |
Laboratory
result |
Calculated |
|
Chromium VI |
mg/kg |
Laboratory
result |
Laboratory
result |
Calculated |
|
Nickel release |
µg/cm²/week |
Laboratory
result |
Laboratory
result |
Calculated |
|
pH |
pH units |
Laboratory
result |
Laboratory
result |
Difference |
|
Disperse dyes |
mg/kg |
Laboratory
result |
Laboratory
result |
Calculated |
Percentage reduction
[
\text{Reduction (%)} =
\frac{\text{Before washing}-\text{After washing}}
{\text{Before washing}}\times100
]
This table should contain actual laboratory observations,
rather than invented numerical results.
Appendix L — Statistical Analysis of Actual
Garment Testing
If 100 or more garments are laboratory tested, the following analysis can be
reported:
|
Statistical
test |
Research
question |
|
Mean |
Average chemical concentration |
|
Median |
Typical residue level |
|
Standard deviation |
Variation between garments |
|
Paired t-test |
Before vs. after washing |
|
Wilcoxon signed-rank |
Before vs. after washing when data are non-normal |
|
ANOVA |
Difference among fibre categories |
|
Kruskal-Wallis |
Non-parametric comparison among fabrics |
|
Chi-square |
Compliance/non-compliance association |
|
Pearson correlation |
Relationship between chemical concentration and
irritation score |
|
Spearman correlation |
Rank relationship where assumptions for Pearson
are not satisfied |
|
Multiple regression |
Predict irritation using chemical and physical
exposure variables |
Appendix M — Final Comparative Risk Table
|
Factor |
Nylon |
Polyester |
Cotton |
Linen |
Saree |
|
Chemical dye exposure |
Possible |
Possible |
Possible |
Possible |
Possible |
|
Formaldehyde-finishing exposure |
Possible |
Possible |
Possible |
Possible |
Possible |
|
Azo-dye concern |
Possible |
Possible |
Possible |
Possible |
Possible |
|
Disperse-dye concern |
More relevant |
More relevant |
Less characteristic |
Less characteristic |
Depends on fibre |
|
Sweat/friction |
Product dependent |
Product dependent |
Product dependent |
Product dependent |
Product dependent |
|
Natural/synthetic status |
Synthetic |
Synthetic |
Natural |
Natural |
Variable |
|
Automatically safe |
No |
No |
No |
No |
No |
|
Automatically dangerous |
No |
No |
No |
No |
No |
|
Laboratory testing needed |
Yes |
Yes |
Yes |
Yes |
Yes |
Appendix N — Evidence-Based Final Finding
The complete evidence supports the following conclusion:
FIBRE ≠ CHEMICAL SAFETY
A garment's potential health risk should be assessed through:
Fibre + dye + finishing + chemical concentration + migration + skin
contact + duration + individual susceptibility.
Therefore, the appropriate scientific conclusion is not:
“Nylon and polyester are harmful to the body.”
The stronger conclusion is:
“Certain chemicals used in the manufacture, dyeing, printing and
finishing of both synthetic and natural textiles may cause adverse health
effects under relevant exposure conditions; therefore, textile safety should be
assessed by chemical testing and regulatory compliance rather than by fibre
origin alone.”
This conclusion is consistent with the existence of regulatory testing for
formaldehyde, azo-derived aromatic amines, disperse dyes, phthalates and other
substances in textile/product standards.
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