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EC number: 202-816-4 | CAS number: 100-07-2
- 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
Key value for chemical safety assessment
Effects on fertility
Description of key information
NOAEL was estimated to be 248 mg/kg bw when Wistar male and female rats were orally exposed with Anisoyl chloride.
Thus, as per criteria of CLP regulation, Anisoyl chloride can be not classified for reproductive toxicity.
Link to relevant study records
- Endpoint:
- toxicity to reproduction
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- Data is predicted using OECD QSAR toolbox version 3.3 and the supporting QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: as below
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3
- GLP compliance:
- not specified
- Limit test:
- no
- Specific details on test material used for the study:
- - IUPAC Name: 4-Methoxybenzoyl Chloride
- InChI:1S/C8H7ClO2/c1-11-7-4-2-6(3-5-7)8(9)10/h2-5H,1H3
- SMILES:COc1ccc(C(=O)Cl)cc1
- Mol. formula: C8H7ClO2
- Molecular Weight: 170.5943 g/mole - Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- polyethylene glycol
- Details on exposure:
- not specified
- Details on mating procedure:
- not specified
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 46 days
- Frequency of treatment:
- Daily
- Details on study schedule:
- not specified
- Dose / conc.:
- 248 mg/kg bw/day
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- not specified
- Positive control:
- not specified
- Parental animals: Observations and examinations:
- not specified
- Oestrous cyclicity (parental animals):
- not specified
- Sperm parameters (parental animals):
- not specified
- Litter observations:
- not specified
- Postmortem examinations (parental animals):
- not specified
- Postmortem examinations (offspring):
- not specified
- Statistics:
- not specified
- Reproductive indices:
- not specified
- Offspring viability indices:
- not specified
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- not specified
- Dose descriptor:
- NOAEL
- Effect level:
- 248 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- reproductive performance
- Remarks on result:
- other: No effect observed
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not specified
- Mortality / viability:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings:
- not specified
- Other effects:
- not specified
- Behaviour (functional findings):
- not specified
- Developmental immunotoxicity:
- not specified
- Dose descriptor:
- other: not specified
- Generation:
- other: not specified
- Based on:
- not specified
- Sex:
- not specified
- Basis for effect level:
- other: not specified
- Remarks on result:
- other: not specified
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Reproductive effects observed:
- not specified
- Treatment related:
- not specified
- Relation to other toxic effects:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Conclusions:
- NOAEL was estimated to be 248 mg/kg bw when Wistar male and female rats were orally exposed with Anisoyl chloride.
- Executive summary:
In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for Anisoyl chloride. The NOAEL was estimated to be 248 mg/kg bw when Wistar male and female rats were orally exposed with Anisoyl chloride.
Reference
The
prediction was based on dataset comprised from the following
descriptors: NOAEL
Estimation method: Takes average value from the 8 nearest neighbours
Domain logical expression:Result: In Domain
(((((((("a"
or "b" or "c" or "d" )
and ("e"
and (
not "f")
)
)
and "g" )
and "h" )
and ("i"
and (
not "j")
)
)
and "k" )
and "l" )
and ("m"
and "n" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Acyl chloride OR Acyl halide OR
Alkylarylether OR Aromatic compound OR Carbonic acid derivative OR
Carboxylic acid derivative OR Ether OR Halogen derivative by Organic
functional groups, Norbert Haider (checkmol) ONLY
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Aliphatic Carbon [CH] OR
Aliphatic Carbon [-CH2-] OR Aliphatic Carbon [-CH3] OR Aromatic Carbon
[C] OR Carbonyl, olefinic attach [-C(=O)-] OR Carbonyl, one aromatic
attach [-C(=O)-] OR Chlorine, olefinic attach [-Cl] OR Miscellaneous
sulfide (=S) or oxide (=O) OR Olefinic carbon [=CH- or =C<] OR Oxygen,
one aromatic attach [-O-] by Organic functional groups (US EPA) ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Acyl halide OR Aryl OR Ether OR
Overlapping groups by Organic Functional groups (nested) ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Acyl halide OR Aryl OR Ether by
Organic Functional groups ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Non binder, without OH or NH2
group by Estrogen Receptor Binding
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Non binder, MW>500 OR Non
binder, non cyclic structure by Estrogen Receptor Binding
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Acylation AND Acylation >>
Direct acylation involving a leaving group AND Acylation >> Direct
acylation involving a leaving group >> (Thio)Acyl and (thio)carbamoyl
halides and cyanides by Protein binding by OASIS v1.3 ONLY
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Acylation AND Acylation >>
Direct Acylation Involving a Leaving group AND Acylation >> Direct
Acylation Involving a Leaving group >> Acyl halides (including benzyl
and carbamoyl deriv.) by Protein binding by OECD ONLY
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Not known precedent reproductive
and developmental toxic potential by DART scheme v.1.0
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as AhR binders.Polycyclic aromatic
hydrocarbons (PAHs) (3b-3) OR Known precedent reproductive and
developmental toxic potential OR Toluene and small alkyl toluene
derivatives (8a) by DART scheme v.1.0
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as Bioavailable by Lipinski Rule
Oasis ONLY
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as Acyl chloride AND Acyl halide
AND Alkylarylether AND Aromatic compound AND Carbonic acid derivative
AND Carboxylic acid derivative AND Ether AND Halogen derivative by
Organic functional groups, Norbert Haider (checkmol) ONLY
Domain
logical expression index: "m"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 1.15
Domain
logical expression index: "n"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 4.35
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 248 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- Data is Klimisch 2 and from the OECD QSAR toolbox (2018)
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Reproductive toxicity:
In different studies, Anisoyl chloride has been investigated for reproductive toxicity to a greater or lesser extent. Often are the studies based on in vivo experiments and estimation in rodents, i.e. most commonly in rats for Anisoyl chloride along with the study available on structurally similar read across substance 4-methoxybenzaldehyde; Anisaldehyde (CAS no 123-11-5) and 4-methoxyphenylacetic acid (CAS no 104-01-8). The predicted data using the OECD QSAR toolbox has also been compared with the experimental studies.
In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for Anisoyl chloride. The NOAEL was estimated to be 248 mg/kg bw when Wistar male and female rats were orally exposed with Anisoyl chloride.
In another experimental study given by Organization for Economic Co-operation and Development (Environment Directorate Joint Meeting of the chemicals committee and the working party on chemicals, pesticides and biotechnology Feb 27th, 2012) on structurally similar read across substance 4-methoxybenzaldehyde; Anisaldehyde (CAS no 123-11-5), male and female rats were treated with p-methoxybenzaldehyde in the concentration of 0, 20, 100 and 500 mg/kg bw orally by gavage for approx. 63 days. Epididymidal weight was decreased in males at 500 mg/kg group. The compound showed no adverse effects in terms of estrous cycle, number of corpora lutea and implant rate at any dose level. In the 500 mg/kg bw group, the number of non-pregnant females was increased although all pairs copulated. The delivery index was lower than in controls at 500 mg/kg bw/day. In addition, the number of pups and the number of live pups on lactation day 0 and 4 were lower than in the controls at 500 mg/kg bw/day. No effect on viability of treated rats was observed as compared to control. No effect on body weight of pups observed as compared to control. Therefore, NOAEL was considered to be 100 mg/kg bw for P and F1 generation when male and female rats were treated with p-methoxybenzaldehyde orally by gavage for approx. 63 days.
Further supported by experimental study given by Kotinet al(National Cancer Institute Division of Cancer Cause &Prevention Carcinogenesis Program Bethesda, Maryland, 1968) on structurally similar read across substance 4-methoxyphenylacetic acid (CAS no 104-01-8), B6C3F1 female mice were treated with (4-methoxyphenyl) acetic acid in the concentration of 0 and 215 mg/kg bw/day in 0.5% gelatin for 7 to 28 day and after dose is administer through diet at 560 ppm for 18 months. Body weight gain was observed with the increase in duration of treatment. No gross pathological changes were observed in treated female mice. In addition, no fibroadenoma and carcinoma mammary gland were observed in treated female mice as compared to control. Therefore, NOAEL was considered to be > 215 mg/kg bw when B6C3F1 female mice by using (4-methoxyphenyl) acetic acid for 18 months.
Thus, based on the above study and predictions on Anisoyl chloride and its read across substances, it can be concluded that NOAEL value is 248 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, Anisoyl chloride can be not classified for reproductive toxicity.
Effects on developmental toxicity
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Based on the above study and predictions on Anisoyl chloride and its read across substances, it can be concluded that NOAEL value is 248 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, Anisoyl chloride can be not classified for reproductive toxicity.
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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