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EC number: 203-808-3 | CAS number: 110-85-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
Piperazine has shown low toxicity in acute oral and dermal toxicity tests: LD50 oral, rat = 2600 mg/kg bw and LD50 dermal, rabbit = 8300 mg/kg bw. In acute inhalation toxicity tests (inhalation hazard tests) rats were exposed to the vapour; no LC50 was determined. At 1.61 mg/l exposure for 7 h slight mucosal irritation was noted. No clinical signs were noted at inhalation exposure of 0.57 mg/l for 7 h.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 600 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC0
- Value:
- > 2 mg/L air
- Physical form:
- inhalation: vapour
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 8 300 mg/kg bw
Additional information
Acute oral toxicity:
Three reliable acute oral toxicity studies
with very similar results are available. The key study was selected
based on the lower acute oral LD50 value and the reporting date.
In an acute toxicity study Sprague Dawley rats were dosed with
piperazine by gavage. Groups with 5 males and 5 females in each group
recevied doses of 1000, 1210, 1780, 2610 or 3830 mg/kg. The LD50 value
was 2600 mg/kg bw (BASF, 1980). In support, in an acute toxicity study
acccording to OECD401, 5 male and 5 female rats in five dose groups were
exposed to piperazine by oral gavage. The LD50 value for male and female
rats was 3200 mg/kg bw (Mallory, 1981). In an acute toxicity study, rats
were exposed to piperazine by gavage in six dose groups with 5 animals
per sex per dose. The LD50 was 2500 mg/kg bw (BASF, 1964).
Acute inhalation toxitiy:
In an Inhalation Hazard Test, no mortality was observed when 6 rats were exposed for 8 hours to an atmosphere saturated at room temperature; the calculated concentration was 1.61 mg/L. Slight mucosal irritaion was noted. Extrapolation using Haber´s law results in a LC0 for 4h of 2 mg/l (BASF, 1964). In support, no mortality was observed in an Inhalation Hazard Test, when 6 rats were exposed for 7 hours to a saturated atmosphere at room temperature; the calculcated concentration was 0.57 mg/L. No clinical signs were noted. Extrapolation using Haber´s law results in an LC0 for 4 h of 0.8 mg/L (BASF, 1980). Thus, inhalation of an enriched/saturated vapour-air-mixture represents an unlikely acute hazard.
Acute dermal toxicity:
In an acute dermal toxicity study in rabbits performed according to OECD402, but with deviations in number of animals used and abrasion of the skin, an LD50 value of 8300 mg/kg was found (Pharmakon Laboratories, 1981).
Other data:
Data on human exposure for piperazine as an anti-helmintic agent has shown neurotoxic effects for which a LOAEL of 110 mg/kg can be set.
Justification for classification or non-classification
Piperazine does not meet the criteria for classification for acute toxicity according to the CLP regulation (EU-GHS).
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