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Diss Factsheets

Administrative data

Key value for chemical safety assessment

Effects on fertility

Description of key information

NOAEL was estimated to be 781 mg/kg bw when rat were exposed with Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts. 

Link to relevant study records
Reference
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:
- Name of test material (IUPAC name): Dialkyl(C1-C14)dithiophosphoric acid, zinc salt
- Common name: Phosphorodithioic acid, O,O–di–C1–14–alkyl esters, zinc salts
- Molecular formula: C28H60O4P2S4Zn
- Molecular weight: 716.38 g/mol
- Smiles notation: [Zn+2].CCCCCCCOP(=S)([S-])OCCCCCCC.CCCCCCCOP(=S)([S-])OCCCCCCC
- InChl: 1S/2C14H31O2PS2.Zn/c2*1-3-5-7-9-11-13-15-17(18,19)16-14-12-10-8-6-4-2;/h2*3-14H2,1-2H3,(H,18,19);/q;;+2/p-2
- Substance type: Organic
- Physical state: liquid
Species:
rat
Strain:
Wistar
Details on species / strain selection:
not specified
Sex:
male/female
Details on test animals or test system and environmental conditions:
not specified
Route of administration:
oral: gavage
Type of inhalation exposure (if applicable):
not specified
Remarks on MMAD:
not specified
Vehicle:
water
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:
The duration of treatment covered a 2-week premating and a mating period in both sexes, approximately 1 week post-mating in males,and the entire gestation period as well as 4 days of lactation and 2 weeks thereafter in females.
Frequency of treatment:
daily
Details on study schedule:
not specified
Dose / conc.:
781 mg/kg bw/day
No. of animals per sex per dose:
10
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:
781 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
reproductive performance
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:
no effects observed
Dermal irritation (if dermal study):
not specified
Mortality / viability:
no mortality observed
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:
no effects observed
Histopathological findings:
not examined
Other effects:
not specified
Behaviour (functional findings):
not specified
Developmental immunotoxicity:
not specified
Dose descriptor:
NOAEL
Generation:
F1
Effect level:
781 mg/kg bw/day
Based on:
test mat.
Sex:
male/female
Basis for effect level:
clinical signs
mortality
body weight and weight gain
gross pathology
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
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

The prediction was based on dataset comprised from the following descriptors: NOAEL
Estimation method: Takes average value from the 5 nearest neighbours
Domain  logical expression:Result: In Domain

(((((((("a" or "b" or "c" or "d" or "e" or "f" )  and ("g" and ( not "h") )  )  and ("i" and ( not "j") )  )  and ("k" and ( not "l") )  )  and "m" )  and ("n" and ( not "o") )  )  and ("p" and ( not "q") )  )  and ("r" and "s" )  )

Domain logical expression index: "a"

Referential boundary: The target chemical should be classified as Zinc metal and salts by OECD HPV Chemical Categories

Domain logical expression index: "b"

Referential boundary: The target chemical should be classified as Soluble complexes of Zinc by US-EPA New Chemical Categories

Domain logical expression index: "c"

Referential boundary: The target chemical should be classified as Alkoxy AND Thiophosphate by Organic Functional groups

Domain logical expression index: "d"

Referential boundary: The target chemical should be classified as Alkoxy AND Overlapping groups AND Thiophosphate by Organic Functional groups (nested)

Domain logical expression index: "e"

Referential boundary: The target chemical should be classified as Aliphatic Carbon [CH] AND Aliphatic Carbon [-CH2-] AND Aliphatic Carbon [-CH3] AND Miscellaneous sulfide (=S) or oxide (=O) AND Phosphite, aliphatic attach [-O-P] AND Sulfur, phosphorus attach [-S-] AND Thio-phosphorus [S=P] AND Zinc [Zn] by Organic functional groups (US EPA)

Domain logical expression index: "f"

Referential boundary: The target chemical should be classified as Anion AND Cation by Organic functional groups, Norbert Haider (checkmol)

Domain logical expression index: "g"

Referential boundary: The target chemical should be classified as Non binder, MW>500 by Estrogen Receptor Binding

Domain logical expression index: "h"

Referential boundary: The target chemical should be classified as Non binder, impaired OH or NH2 group OR Non binder, non cyclic structure OR Non binder, without OH or NH2 group by Estrogen Receptor Binding

Domain logical expression index: "i"

Referential boundary: The target chemical should be classified as Not possible to classify according to these rules (GSH) by Protein binding potency

Domain logical expression index: "j"

Referential boundary: The target chemical should be classified as Slightly reactive (GSH) OR Slightly reactive (GSH) >> 2-Alkenyl carbonitriles (MA) OR Slightly reactive (GSH) >> Alkyl cinnamates (MA) by Protein binding potency

Domain logical expression index: "k"

Referential boundary: The target chemical should be classified as Stable form by Tautomers unstable

Domain logical expression index: "l"

Referential boundary: The target chemical should be classified as Hydroxyazo form - 1,5-H shift by Tautomers unstable

Domain logical expression index: "m"

Similarity boundary:Target: CCCCCCCOP(=S)(OCCCCCCC)S{-}.[Zn]{2+}.S{-}P(=S)(OCCCCCCC)OCCCCCCC
Threshold=40%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization

Domain logical expression index: "n"

Referential boundary: The target chemical should be classified as Alkoxy AND Overlapping groups AND Thiophosphate by Organic Functional groups (nested)

Domain logical expression index: "o"

Referential boundary: The target chemical should be classified as Dihydroxyl group by Organic Functional groups (nested)

Domain logical expression index: "p"

Referential boundary: The target chemical should be classified as Alkoxy AND Overlapping groups AND Thiophosphate by Organic Functional groups (nested)

Domain logical expression index: "q"

Referential boundary: The target chemical should be classified as Cycloalkene by Organic Functional groups (nested)

Domain logical expression index: "r"

Parametric boundary:The target chemical should have a value of log Kow which is >= 2.58

Domain logical expression index: "s"

Parametric boundary:The target chemical should have a value of log Kow which is <= 18.9

Conclusions:
NOAEL was estimated to be 781 mg/kg bw when rat were exposed with Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts.
Executive summary:

In an prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts. The NOAEL was estimated to be 781 mg/kg bw when rat were exposed with Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts. 

Effect on fertility: via oral route
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
781 mg/kg bw/day
Study duration:
subchronic
Species:
rat
Quality of whole database:
Data is Klimisch 2 and from OECD QSAR toolbox
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: Oral

In different studies, Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts has been investigated for reproductive toxicity to a greater or lesser extent. Often are the studies based on in vivo experiments and estimated data in rodents, i.e. most commonly in rats along with the study available on structurally similar read across substanceQuat-Silsesquioxane (CAS no 27668-52-6)and Calcium distearate (CAS no 1592-23-0). The predicted data using the OECD QSAR toolbox has also been compared with the experimental studies.

In an prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts. The NOAEL was estimated to be 781 mg/kg bw when rat were exposed with Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts.

 

In another experimental study conducted by Siddiquiet al(Fundamental And Applied Toxicology 21, 6 6 - 7 0 (1993)) on structurally similar read across substanceQuat-Silsesquioxane (CAS no 27668-52-6),Sprague-Dawley female rats by using Quat-Silsesquioxane in the concentration of 0, 100, 300, or 1000 mg/kg/day orally by gavage in corn oil.No maternal mortality and clinical signs or behavioral changes were observed in treated female rats as compared to control. No effect on body weight and feed consumption changes were observed in treated female rats as compared to control. Similarly, no effect on reproductive parameters such as number of corpora lutea, number of live fetuses per litter, litter size, mean fetal body weight, or mean crown-rump length was observed in treated rats. Ratio of male and female pups at the 1000 mg/ kg/day dose level was significantly different from the control group but was not considered treatment related. Slight but significant increase in relative liver weight of treated female rats was observed as compared to control. In addition, No effect on viability, fetal body weight and external malformations were observed in treated fetuses as compared to control. One fetus with bent limb bones, two fetuses from different mothers with microphthalmia and two other fetuses with omphalocele were observed at 1000 mg/kg/day and single fetus with multiple malformations were observed at 300 mg/kg/day in treated fetuses as compared to control. The incidence of developmental variations in the treated litters was not significantly increased over the control incidence. They occurred in low frequency and were distributed randomly across the Quat-Silsesquioxanetreated and control groups. Therefore,NOAEL was considered to be 300 mg/kg bw for P generation and 1000 mg/kg for F1 generation when Sprague-Dawley female rats were treated withQuat-Silsesquioxane orally by gavage from day 6 to 15 of gestation.

Further supported by experimental study conducted byDupont Chem Co (NTRL,OT50546181, 09/01/92, National Technical Information Service, 1992) on structurally similar read across substanceQuat-Silsesquioxane (CAS no 27668-52-6), Albinofemale rats by using Dow Corninc @Q9-5700 in the concentration of 0, 100, 300 and 1000 mg/kg orally. 1 nongravid rats died at 1000 mg/kg and 1 pregnant rats died at 100 mg/kg as compared to control. No untoward behavioral reactions were observed in treated female rats as compared to control.Similarly,Noeffect on gestation andgross pathological changes were observed in treated female rat as compared to control. In addition, No effect on fetuses Body weight were observed as compared to control. No external abnormalities and skeletal and internal developmental effect were observed in treated fetuses as compared to control. Therefore, NOAEL was considered to be 1000 mg/kg for P and F1 generation when  Albinofemale rats were treated with Dow Corninc @Q9-5700 orally from gestation days 6 through 15.

This further supported by experimental study conducted by Organization for Economic Cooperation and Development (CoCAM 2, 17-19 April 2012)on structurally similar read across substance Calcium distearate (CAS no 1592-23-0), Sprague-Dawley male and female rats were treated with Calcium distearate in the concentration of 0, 250, 500 and 1000 mg/kg bw orally by gavage. Alopecia was observed in the control and treatment groups of both sexes. No mortality and change in body weight were observed in treated male and female rats we compared to control. A decrease of statistically significant change in food consumption was observed at 2 weeks in 1000 mg/kg bw/day group. No statistically significant change in organ weights among the groups. Splenomegaly and testicular atrophy were observed in 1 and 1 males of the 0 and 1000 mg/kg bw/day groups, respectively. Discoloration of adrenal gland was observed in 1 female of the 250 mg/kg bw/day group. However, there was no toxic effect of the test article on these organs in histopathology; therefore, this was considered to be a sporadically occurring sign In all reproductive organs in control and high dose groups, the lesion related with the test article was not observed. Adrenocortical necrosis was observed in 1 female of the 250 mg/kg bw/day group. In addition, No statistically significant differences were observed in the following parameters examined: gestation period, the number of corpora lutea and implantation, delivery index, the number of live and dead pups, the percentage of live and dead pups to implantations, pre-implantation loss, post-implantation loss, sex ratio, viability ratio, number of neonates with external anomalies, and body weights of pups on post-natal day 0 and day 4. Therefore, NOAEL was considered to be 1000 mg/kg bw/day for P and F1 generation when Sprague-Dawley male and female rats were treated with Calcium distearate orally by gavage.

Thus, based on the above studies and predictions on Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts and its read across substances, it can be concluded that NOAEL value is 781 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts can be Not classified as reproductive toxicant.

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 studies and predictions on Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts and its read across substances, it can be concluded that NOAEL value is 781 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, Phosphorodithioic acid, O,O-di-C1-14-alkyl esters, zinc salts can be Not classified as reproductive toxicant.

Additional information