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EC number: - | CAS number: 313644-32-5
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 15.02.2018 - 21.02.2019
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
- Objective of study:
- excretion
- metabolism
- toxicokinetics
Test guideline
- Qualifier:
- no guideline followed
- GLP compliance:
- no
Test material
- Reference substance name:
- 1,4-bis(7-methyloctyl) cyclohexane-1,4-dicarboxylate
- Cas Number:
- 313644-32-5
- Molecular formula:
- C26H48O4
- IUPAC Name:
- 1,4-bis(7-methyloctyl) cyclohexane-1,4-dicarboxylate
- Test material form:
- liquid
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- CD® / Crl:CD(SD)
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Germany GmbH
- Age at study initiation: Stagger 1: 58 days
Stagger 2: 42 days
- Weight at study initiation: Stagger 1: 355.2 to 393.0 g
Stagger 2: 286.1 to 317.8 g
- Housing: The animals were kept singly in MAKROLON cages (type III plus) with a basal
surface of approximately 39 cm x 23 cm and a height of approximately 18 cm.
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 9 days per stagger
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C ±3°C
- Humidity (%): 55% ±10%
- Photoperiod (hrs dark / hrs light):The rooms were lit (about 150 lux at approx. 1.5 metres room height) and
darkened for periods of 12 hours each.
IN-LIFE DATES:
From: Test item administration Stagger 1: 16 February 2018
Stagger 2: 13 July 2018
To:Termination of in-life period Stagger 1: 17 February 2018
Stagger 2: 14 July 2018
Administration / exposure
- Route of administration:
- intravenous
- Vehicle:
- other: Stagger 1: 0.9% NaCl solution, Stagger 2: 5% Tween 80® in 0.9% NaCl solution
- Duration and frequency of treatment / exposure:
- Single dose on test day 1
Doses / concentrations
- Dose / conc.:
- 100 mg/kg bw/day
- Remarks:
- Group 1 and 2
- No. of animals per sex per dose / concentration:
- 16 male animals, allocated to 2 separate staggers
(8 animals per stagger).
Each stagger consisted of 2 groups (4 animals per
group).
Group 1: scheduled for PK sampling
Group 2: scheduled for urine sampling. - Control animals:
- no
- Details on study design:
- - Dose selection rationale:
The dose level for this study has been selected by the Sponsor based on available
data and the results of LPT study 35156.
In this study, 2 male rats were treated once intravenously with 10 mg DINCD/kg
b.w. on test day 1.
None of the two male rats treated intravenously with 10 mg DINCD/kg b.w. died
prematurely during the course of the study. No abnormalities in behaviour, external
appearance, or condition of faeces were observed. - Details on dosing and sampling:
- TOXICOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, blood
- Time and frequency of sampling:
Blood sampling time after dosing [hh:mm p.a.]: 00:05, 00:10, 00:20. 00:40, 01:20, 02:40
Urine sampling: Urine was collected for a period of 24 hours p.a.
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, blood
- Time and frequency of sampling: see above
- From how many animals: (samples pooled or not)
Blood sampling: Sampling from animal no. 1 – 4 and 9 – 12. Blod samples were pooled.
Urine sampling: Sampling from animal no .5 – 8 and 13 – 16 (group 2; stagger 1 and 2)
- Method type(s) for identification: semiquantitative HPLC-MS-MS and HPLC-MS-MS
- Limits of detection and quantification:
LLOQ for HPLC-MS-MS: 20 ng/mL for DINCD and its metabolite.
LLOQ for semiquantitative HPLC-MS-MS: 20 ng/mL for DINCD and 400 ng/mL of its metabolite.
- Other: The samples were analysed at Prolytic GmbH, Alt-Fechenheim 34, 60386 Frankfurt, Germany - Statistics:
- No statistical evaluation was performed.
Results and discussion
Toxicokinetic / pharmacokinetic studies
Transfer into organs
- Observation:
- not determined
- Details on excretion:
- The analysis of the urine samples by a semi-quantitative HPLC-MS/MS method
was the responsibility of the analytical laboratory.
Stagger 1
The analysis of the urine samples was postponed as hardly any test substance or
metabolite levels were detected in the plasma samples.
Stagger 2
Sample analysis was carried out on urine samples taken during a sampling period of
0 to 24 hours p.a.
In 3 of 4 animals, DINCD analyte concentrations were below the detection limit of
20 ng/mL. In one animal (animal no. 15) DINCD was determined in a concentration
of 940 ng/mL urine.
Quantification of the metabolite CHDCA in the urine samples revealed analyte
concentrations above the calibration range (i.e. >4000 ng/mL urine). Further
dilution of the urine samples into the calibration range was not advisable due to the
higher impact of matrix effects on the analytical results.
Toxicokinetic parameters
- Key result
- Toxicokinetic parameters:
- Cmax: The maximum DINCD in plasma concentrations determined 5 minutes post administration (p.a.) ranged from 2727.73 to 4229.63 ng/ml (3380.52 ± 769.95 ng/ml) for animal nos. 9 to 11.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- The metabolite CHDCA (cis- 1,4-cyclohexanedicarboxylic acid) was also detected and quantified in the plasma of all
animals treated once intravenously with 100 mg DINCD/kg b.w. Metabolite plasma
concentrations increased steadily with a peak value determined between 80 and
160 minutes p.a. (80 minutes p.a.: 540.22 ± 416.85 ng/ml; 160 minutes p.a.:
327.54 ±16.41 ng/ml).
Applicant's summary and conclusion
- Conclusions:
- The toxikokinetik study of Diisononyl
1,4-cyclohexanedicarboxylate (DINCD) following
a single intravenous bolus injection to male rats generates qualitative and only orienting results.
In the preliminary test, DINCD was insoluble in 0.9% NaCl (stability and solubility problems).
The suitable solvent for i.v.injection in the main experiment was 5% Tween 80 in 0.9% NaCl.
The results show a metabolism of DINCD to a metabolite (cyclohexanedicarboxylic acid) (Cmax peak between 120 and 240 min).
This hydrolyzation occurs after 5 min (maximum plasma concentration), T1 / 2 <5 min.
In conclusion, the esults are not linear (high fluctuations between the animals and time points), which is why further studies are needed to generate trustworthy data. - Executive summary:
The study was conducted in 2 separate phases (i.e. 2 staggers) based on the
analytical results obtained for the first stagger. Bioanalytical data of the plasma
sample analysis of the first stagger indicated that no test item was quantifiable in
plasma samples. Solubility testing at LPT revealed that the test item was insoluble
in 0.9% NaCI solution used as vehicle. lnsolubility resulted in the formation of two
separate clear phases and only 0.9% NaCI solution was presumably administered.
No formulation analysis was carried out and phase separation could not be
detected visually prior to administration.
Testing of various solvents (data not included in this report) confirmed
5% Tween 80® in 0.9% NaCI solution as the most suitable vehicle for
administration of DINCD with respect to solubility and tolerability in the given
animal model.
An additional stagger (stagger 2) was employed administered with the test item
using Tween 80® in 0.9% NaCI solution as vehicle. Bioanalytical data revealed
high data variability for both DINCD and CHDCA (DINCD metabolite) plasma levels.
The maximum DINCD in plasma concentrations determined 5 minutes post
administration (p.a.) ranged from 2727.73 to 4229.63 ng/ml (3380.52
± 769.95 ng/ml) for animal nos. 9 to 11.
The metabolite CHDCA was also detected and quantified in the plasma of all
animals treated once intravenously with 100 mg DINCD/kg b.w. Metabolite plasma
concentrations increased steadily with a peak value determined between 80 and
160 minutes p.a. (80 minutes p.a.: 540.22 ± 416.85 ng/ml; 160 minutes p.a.:
327.54 ±16.41 ng/ml).
Furthermore, formulation analysis revealed a high variance in sample recovery of
only a 60 to 84% recovery with respect to the test item concentration.
Due to the observed difficulties regarding solubility and stability of the test item
DINCD in various solvents, as well as to generate more reliable data, further
solubility testing are recommended associated with formulation analyses prior to
administration.
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