Triclosan: How a "Safe" Ingredient Got Banned From Soap
For decades, triclosan was the gold standard of antibacterial ingredients. Then the FDA asked one simple question: does it actually work better than plain soap?
The Quick Version
In September 2016, the FDA banned triclosan and 18 other antimicrobial ingredients from consumer antibacterial soaps. The reason wasn't toxicity - it was that manufacturers couldn't prove these ingredients worked any better than plain soap and water. Meanwhile, concerns about endocrine disruption, antimicrobial resistance, and environmental persistence accumulated. The EU has progressively restricted it since 2014. It's still permitted in toothpaste and deodorants, but the trajectory is clear: triclosan is being phased out.
40% of the Antibacterial Soap Market
Before the ban, triclosan was ubiquitous. About 40% of antibacterial soap products contained it. The marketing was compelling: "antibacterial" sounded like extra protection against germs.
But the FDA had been asking questions since the 1970s. In 1978, they first requested data showing that antibacterial soaps were more effective than regular soap. The industry kept delaying.
The 2016 Ban
On September 2, 2016, the FDA issued a final rule removing triclosan and 18 other antimicrobial ingredients from the list of Generally Recognized as Safe and Effective (GRASE) ingredients for consumer antiseptic wash products.
FDA's Key Statement
"Manufacturers did not provide the necessary data to establish safety and effectiveness... There isn't enough science to show that over-the-counter antibacterial soaps are better at preventing illness than washing with plain soap and water."
In December 2017, the FDA extended the ban to healthcare antiseptic products, concluding there was "insufficient safety and efficacy data" for 24 antimicrobial chemicals including triclosan.
The Efficacy Question
The central irony: the ban wasn't primarily about safety. It was about a lack of demonstrated benefit.
Triclosan works by blocking bacterial lipid synthesis at low concentrations and destabilizing cell membranes at higher concentrations. In a petri dish, it's highly effective against a broad spectrum of bacteria.
But hand washing isn't a petri dish. The contact time is seconds, not hours. The triclosan concentration in wash-off products is low. And the mechanical action of rubbing with soap already disrupts bacterial cell membranes and removes microbes from skin.
When manufacturers were finally forced to provide efficacy data, they couldn't demonstrate that antibacterial soaps worked better than regular soap in real-world conditions.
The Safety Concerns
While efficacy drove the FDA decision, safety concerns were accumulating:
Triclosan Safety Profile
| Concern | Evidence |
|---|---|
| Thyroid Disruption | Consistent decrease in T4/T3 in rodent studies; mechanism via hepatic catabolism |
| Antimicrobial Resistance | Theoretical concern; cross-resistance to clinical antibiotics not proven |
| Allergic Adjuvant Effect | Epidemiological association with aeroallergen sensitization |
| Environmental Persistence | Bioaccumulates; forms dioxins under certain conditions |
| Dermal Absorption | 6.3% through human skin (relatively low) |
| Sensitization | <1% in most studies (weak allergen) |
The Thyroid Data
Triclosan structurally resembles thyroid hormone (T4). Studies consistently show effects on the thyroid axis:
- Decreased serum T4 and T3 in rodent studies
- Increased hepatic catabolism of thyroid hormones
- Upregulation of phase II enzymes (glucuronidation)
- Inhibition of sulfotransferase and deiodinase activity
Human studies are less conclusive. One study found a marginal positive association between triclosan exposure and TSH in females (p=0.058). But the human thyroid appears less sensitive than the rodent thyroid to this mechanism.
The EU's Progressive Restrictions
The EU has taken a different approach - not an outright ban, but increasingly tight restrictions:
EU Regulatory Timeline
| Year | Action |
|---|---|
| 2014 | Restricted to rinse-off products only (Regulation 358/2014) |
| 2017 | Prohibited in biocidal products |
| 2022 | SCCS emphasizes endocrine disruption concerns (SCCS/1643/22) |
| 2024-2025 | New restrictions via Regulation 2024/996 |
What's Still Permitted
Triclosan isn't completely banned. In the EU, it remains permitted at 0.3% maximum in specific product categories:
EU Permitted Uses (0.3% max)
- Toothpastes
- Hand soaps
- Body soaps and shower gels
- Deodorants (non-spray only)
- Face powders and blemish concealers
- Nail products (for cleaning before artificial nails)
Prohibited Uses
- Body lotions (explicitly NOT SAFE per SCCS)
- Mouthwash (all ages)
- All other leave-on products
Toothpaste is the strongest remaining use case. Triclosan in toothpaste does show benefits for gingivitis reduction, and the exposure profile is different from skin application.
The Margin of Safety Debate
One of the more contentious aspects of triclosan regulation is the Margin of Safety calculation:
MoS Calculations (Various Studies)
| Study | MoS | Assessment |
|---|---|---|
| Norwegian VKM (all products) | 71.4 | "Matter of concern" |
| Korean Assessment (all products) | 84 | Below 100 threshold |
| Korean Assessment (rinse-off only) | 253.5 | Adequate |
| Rodricks et al. (product-based) | 630-1000 | Adequate |
| Rodricks et al. (biomonitoring) | 5,200-11,750 | Very adequate |
The variability (71 to 11,750) reflects different assumptions about exposure, absorption rates, and which NOAEL to use. Product-based calculations tend to overestimate exposure; biomonitoring-based calculations give higher safety margins.
The Allergic Adjuvant Effect
An unexpected finding from epidemiological research: triclosan may increase susceptibility to allergens even without being an allergen itself.
A study of 623 Norwegian children found that higher urinary triclosan was associated with a 2-fold increased risk of aeroallergen sensitization. The proposed mechanism is an "adjuvant effect" - triclosan may disrupt skin barrier integrity or alter immune responses in ways that enhance sensitization to environmental allergens.
Follow-up research found associations with childhood eczema (23% increased risk per doubling of urinary triclosan) and hay fever (12% increased risk).
Environmental Persistence
Perhaps the most damning aspect of triclosan's profile is environmental:
- Persists in aquatic environments
- Bioaccumulates in aquatic organisms
- Can form dioxins and chloroform under certain wastewater treatment conditions
- Detected in rivers, sediments, and fish tissues globally
When millions of people wash triclosan-containing products down drains daily, the environmental load accumulates rapidly.
The Industry Response
Most major manufacturers reformulated well before the FDA deadline. The writing was on the wall, and consumer perception had shifted. "Antibacterial" was no longer a selling point - it was becoming a liability.
Alternatives filled the gap:
- Benzalkonium chloride - Still permitted in hand sanitizers
- Ethanol-based formulations - The sanitizer boom during COVID
- Plain soap - Effective mechanical action without antimicrobials
The Bottom Line
Triclosan's fall from grace teaches several lessons:
- Efficacy matters - "Sounds good" isn't the same as "proven to work better"
- Regulatory patience runs out - After 40+ years, the FDA finally demanded proof
- Environmental impact matters - Persistence and bioaccumulation add to the risk profile
- Progressive restriction works - The EU's step-by-step approach narrowed uses gradually
- Consumer perception shifts - "Antibacterial" became a warning, not a selling point
Triclosan is still permitted in some applications, but the trajectory is clear. For formulators developing new products, it's not a sensible choice. For consumers checking ingredient lists, its presence signals a formulation that hasn't kept pace with regulatory and scientific evolution.
References
- FDA (2016). Safety and Effectiveness of Consumer Antiseptics; Topical Antimicrobial Drug Products for Over-the-Counter Human Use. 81 FR 61106.
- SCCS (2022). Safety of Triclocarban and Triclosan as substances with potential endocrine disrupting properties. SCCS/1643/22.
- Moss T, Howes D, Williams FM (2000). Percutaneous penetration and dermal metabolism of triclosan. Food Chem Toxicol, 38(4):361-370. DOI: 10.1006/fct.1999.0164
- Bertelsen RJ, et al. (2013). Triclosan exposure and allergic sensitization in Norwegian children. Allergy, 68(1):84-91. DOI: 10.1111/all.12058
- Lee JD, et al. (2019). Risk assessment of triclosan in cosmetics. Toxicol Res, 35(2):137-154. DOI: 10.5487/TR.2019.35.2.137
- Rodricks JV, et al. (2010). Triclosan: A critical review of the experimental data and development of margins of safety. Crit Rev Toxicol, 40(5):422-484. DOI: 10.3109/10408441003667514
- EU Regulation 2024/996 amending Annex V to Regulation (EC) No 1223/2009.
- CIR Expert Panel (2010). Final Report on Triclosan. Int J Toxicol, 29(Suppl 3):98S-114S.
Shahar Ben-David
Formulator. AI researcher. No products to sell.
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