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EC number: 284-461-5 | CAS number: 84896-44-6
- 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, other
- Remarks:
- In-vitro metabolism as part of a OECD 111 type study
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 27.10-27.11.2015
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- not under GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
Materials and methods
- Objective of study:
- metabolism
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD 111 (Hydrolysis as function of pH)
- Deviations:
- yes
- Remarks:
- The poorly soluable neat material was added without co-solvent to the buffer solutions
- GLP compliance:
- no
Test material
- Reference substance name:
- Diisotridecyl 3,3'-[(dibutylstannylene)bis(thio)]dipropionate
- EC Number:
- 284-461-5
- EC Name:
- Diisotridecyl 3,3'-[(dibutylstannylene)bis(thio)]dipropionate
- Cas Number:
- 84896-44-6
- Molecular formula:
- C40H80O4S2Sn
- IUPAC Name:
- 2-methyldodecyl 3-{[dibutyl({3-[(2-methyldodecyl)oxy]-3-oxopropyl}sulfanyl)stannyl]sulfanyl}propanoate
- Test material form:
- other: liquid
Constituent 1
- Radiolabelling:
- no
Administration / exposure
- Details on study design:
- yes
Details on sampling
the respective reaction mixtures were extracted with hexan after pre defined times. The solvent was
removed and analysed by 119Sn NMR
aqueous phase were analysed for tin content by AAS
Details on analytical methods
119-Sn-NMR for hexan solubla fraction
AAS fot tin content in aqueous phase
Buffers
pH 1.2 HCl 0.1 M
pH 4.0 HCl/NaCl/Citric acid
pH 7.0 Na2HPO4/NaH2PO4
pH 9.0 H3BO3/KCl/NaOH
Details on test conditions
Test item was incubated at pH 4 / 7 / 9 for 150 h at 50 °C resp at pH 1.2 for 150 h at 37 °C
At pH 1.2 / 37 °C the test item was incubated for 30 seconds, 30 minutes, 1, 2, 4, 8 hours
Number of replicates
The tests at low pH were run in duplicate
Results and discussion
- Preliminary studies:
- DBT-MPTD Hydrolysis at pH 1.2
A sample of the test item was added to an excess 0.1 M Hydrochloric Acid at 37 °C for 5 days (120
h). The 119Sn-NMR spectrum of the recovered reaction product showed that DBT-MPTD is hydrolyz
ed to DBTC-MPTD. Both substances were present in an equilibrium in a 15/85 DBT-MPTD / DBTCMPTD
mol. % ratio.
DBTC-MPTD, the product of hydrolysis, has been identified based on the 119 Sn-NMR signal. Pure
DBTC-MPTD substance was synthesized separately.
No signal corresponding to DBTC (typically present at 130 ppm) was detected.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Dibutyltin monochloro isotridecylmercaptopropionate / Dibutyltin tridecyl 3-mercaptopropionate
chloride was found as the only metabolite of the exposure to 0.1 M HCl in an equiibrium with the unreacted test item
Any other information on results incl. tables
Tier 1 Testing:
Hydrolysis at pH 4.0, 7.0, and 9.0:
Samples of the test item were added to the respective buffer solutions at 50 °C for 5 days (120 h). Th
e 119Sn-NMR spectra of the reaction products (Annex 2) show only slight signs of hydrolysis. The NM
R peak characteristic to the DBT-MPDT molecule at about 120 ppm decreased from 99 Mol% in the
untreated staring material to a minimal value of 90.7 Mol% in the pH 4 buffer solution. In all cases the
degree of hydrolysis was lower than 10 %. Thus, the higher tier testing was not considered for these
pH-value buffers.
DBT-MPTD Hydrolysis at pH 1.2
A sample of the test item was added to an excess 0.1 M Hydrochloric Acid at 37 °C for 5 days (120
h). The 119Sn-NMR spectrum of the recovered reaction product showed that DBT-MPTD is hydrolyz
ed to DBTC-MPTD. Both substances were present in an equilibrium in a 15/85 DBT-MPTD / DBTCMPTD
mol. % ratio.
DBTC-MPTD, the product of hydrolysis, has been identified based on the 119 Sn-NMR signal. Pure
DBTC-MPTD substance was synthesized separately.
No signal corresponding to DBTC (typically present at 130 ppm) was detected.
Tier 2 testing at pH 1.2
Additional 1 g (1.2 mmol) samples of the test item were hydrolyzed over 6 different time periods (from
30 seconds to 8 hours) in an excess of 0.1 M Hydrochloric Acid at 37 °C. The recorded 119Sn-NMR
spectra detected DBTC-MPTD (# ~ 71 ppm) as the only product of DBT-MPTD hydrolysis.
Kinetics of the hydrolysis was studied measuring intensities of the NMR-signals for DBT-MPTD and
DBTC-MPTD. The sum of both signal intensities remains constant The kinetics of the first and the
second test series were nearly identical so following the average of both test series are used.
After 30 seconds of contact with the preheated buffer (an aqueous solution of hydrochloric acid), the
test item was worked up immediately. The 119Sn-NMR showed that the DBT-MPTD signal was r
educed by about 60 % of its initial signal intensity. Conversion of DBT-MPTD continued during 30
minutes of hydrolysis to about 20 % of the initial signal intensity, whereas the DBTC-MPTD signal in
creased proportionally at the same rate.
The rate of hydrolysis remained constant – with slight variation – at ~ 20 % of DBT-MPTD between 1
and 8 hours of incubation. The long term incubation from Tier 1 resulted in a 15 % DBT-MPTD / 85
% DBTC-MPTD equlibribrium..
Applicant's summary and conclusion
- Conclusions:
- The study showed that DBT-MPTD at pH 9, 7 and 4 can be considered hydrolytically stable. After 5
days at 50 °C less than 10% DBT-MPTD was hydrolyzed (t 0.5 25°C > 1 year).
Under the simulated gastric conditions (0.1 M HCl / pH 1.2 / 37 °C) DBT-MPTD was hydrolyzed to
DBTC-MPTD, its monochloro ester.
It can be concluded that DBTC-MPTD is the only metabolite of DBT-MPTD that was formed in the si
mulated mammalian gastric environment.
No DBTC was formed under the conditions of this study. - Executive summary:
The study showed that DBT-MPTD is hydrolytically stable at pH 9, 7 and 4. After 5 days of hydrolysis
at 50 °C less than 10% DBT-MPTD was hydrolyzed (t 0.525°C> 1 year).
At the simulated gastric conditions (0.1 M HCl/pH 1.2 /37°C) 75% DBT-MPTD was hydrolyzed to it’s
monochloride DBTC-MPTD
No formation of DBTC was detected under the conditions of the study.
Hydrolysis of DBT-MPTD can be monitored by the decrease in the relative intensity of the respective
119Sn-NMR signal at ~ 120 ppm and the increase of the DBTC-MPTD signal at ~ 71 ppm. The sum of
both intensities agrees well with DBT-MPTD signal intensity of the untreated test item.
DBTC could not be identified in any of the hydrolyzed DBT-MPTD samples atdDBTC= 130 ppm using
the 119Sn-NMR spectroscopy.
A comparable result for Dioctyltin bis-2-ethylhexyl mercaptoacetate (DOTE) is described in literature for
the fate of DOTE in PVC [6]
AAS analysis has been conducted to ensure completeness of the analysis and recover all tin compounds
in aqueous phases including all possible water-soluble organotin substances and their breakdown
components.
The analyses detected tin in amounts of 25-40 ppm, which demonstrates that only traces of the water
soluble tin compounds remain in the aqueous phase.
This is consistent with the high, nearly quantitative, recovery rates found in all experiments.
6
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