Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Toxicological information

Developmental toxicity / teratogenicity

Currently viewing:

Administrative data

Endpoint:
developmental toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
1966
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: well documented study result, which meets basic scientific principles, conducted on the read-across substance Choline chloride
Cross-reference
Reason / purpose for cross-reference:
reference to same study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1966
Report date:
1966

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
In the feeding studies the animals (16 / 12 / 11 or 7 pregnant mice, gestation day 1 -18) were treated daily via the diet with Choline chloride (1 %, 2.5 %, 5 % and 10 % in feed). The rats ingested daily approximately 5 gr of food. On gestation day 19 all animals were subjected to necropsy and the uteri and fetuses were examined.
GLP compliance:
not specified
Remarks:
study was performed prior to implementation of GLP
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Choline chloride
EC Number:
200-655-4
EC Name:
Choline chloride
Cas Number:
67-48-1
Molecular formula:
C5H14NO.Cl
IUPAC Name:
2-hydroxy-N,N,N-trimethylethanaminium chloride
Test material form:
other: liquid
Details on test material:
- Name of test material (as cited in study report): N-Trimethyl-ß-hydroxyäthyl-ammoniumchlorid

Test animals

Species:
mouse
Strain:
NMRI
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Ivanova Kisslegg, Germany
- Housing: single in glasses
- Diet (e.g. ad libitum): every second day one piece of bread per animal per day. Thus about 5 grams of food were taken in.
- Water (e.g. ad libitum): ad libitum (out of drinking bottles)
For the investigations, NMRI mice of the company Ivanova Kisslegg in Germany, were used. Their fertility, rate of spontaneous foetal resorptions and rate of anomalies are known through extensive testing. The methodology corresponded to the one described in the laboratories previous reports.

Administration / exposure

Route of administration:
oral: feed
Vehicle:
unchanged (no vehicle)
Details on exposure:
Feeding trials:
Food preparation: For the preparation of feed with 1 %, 2.5 %, 5 % and 10 % of Choline chloride (= 10 000 ppm - 100 000 ppm), 5 g, 12.5 g, 25 g or 50 g of Choline chloride were finely distributed in 300 mL of a 1 % aqueous traganth suspension in the Ultra-Turrex, then finely ground with 500 g of rats bread (Lab Blox from Allied Mills, Chicago) in the Star-mix and mixed with a special machine, divided in 50 approximately equal pieces and dried for 14 - 15 hours at +80 °C. The pieces of bread weighed 9.5 to 11 g.

Experiment:
The choline containing bread was given to all experimental animals (pregnant mice from 1 - 18 day of gestation). The number of pregnant mice in the individual test groups was in the "1 % - group" 16, in the "2, 5 % group" 12, in the "5 % group" ~ 11, and the "10 % - group "7 animals.
All mice were housed singly in glases and provided with 1 piece of bread every second day and water ad libitum. Of the bread thus were taken in about 5 grams of food per day. On gestation day 19, all animals were sacrificed and the uteri and fetuses were examined.
Analytical verification of doses or concentrations:
not specified
Details on mating procedure:
no data
Duration of treatment / exposure:
between the 1st and 18th day of gestation
Frequency of treatment:
via the feed (rat bread), the feed for 2 days was given at once every second days
Duration of test:
19 days
Doses / concentrationsopen allclose all
Dose / conc.:
1 other: %
Remarks:
Basis: nominal conc.
Dose / conc.:
2.5 other: %
Remarks:
Basis: nominal conc.
Dose / conc.:
5 other: %
Remarks:
Basis: nominal conc.
Dose / conc.:
10 other: %
Remarks:
Basis: nominal conc.
No. of animals per sex per dose:
1 % in rat bread - 16 animals
2.5 % in rat bread - 12 animals
5 % in rat bread - 11 animals
10 % in rat bread - 7 animals
Control animals:
yes, historical

Examinations

Maternal examinations:
On the 19th day of gestation, all animals were sacrificed and the uteri and fetuses examined in the manner described earlier.
Ovaries and uterine content:
On the 19th day of gestation, all animals were sacrificed and the uteri and fetuses examined in the manner described earlier.
Fetal examinations:
mean number of offsprings, the mean foetal body weight, mean foetal length, the foetal resportion rate and the number of anomalies

Results and discussion

Results: maternal animals

General toxicity (maternal animals)

Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
The average body weight gain between day 1.-19. of gestation was in the "1 %" Choline chloride group 25.2 g. The average body weight gain was reduced in a dose-dependent manner with the increased Choline chloride concentration. The reduced body weight gain in mice, as shown in table 2, is only partly due to the abortion, because in the "2.5 -group", and even more in the "5 %group" dams, which did not abort, had a significantly lower body weight gain, as the mice which received the feed with 1 % Choline chloride.

Maternal developmental toxicity

Number of abortions:
effects observed, treatment-related
Description (incidence and severity):
In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (=50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1% (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).
This "abortion effect"' is not an expression of a specific embryotoxic toxicity but sign of a general toxicity, because not only the mice with abortion but also the animals without abortion had a significantly reduced body weight than any untreated pregnant mice. This thesis - the lack of a specific embryotoxic effect of Choline chloride - is also supported by the fact that the gavage of food with 1 %(= 10,000 ppm) Choline chloride over the entire period of gestation was well tolerated by the dams without symptoms and the foetal development was not disturbed. Choline chloride thus had under the given experimental conditions, no teratogenic effect, since the product caused only altered development in the foetuses at doses, which also had toxic effects on the dams.
Pre- and post-implantation loss:
effects observed, treatment-related
Description (incidence and severity):
In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (=50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1% (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).
Total litter losses by resorption:
no effects observed
Early or late resorptions:
no effects observed
Dead fetuses:
effects observed, treatment-related
Description (incidence and severity):
In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (=50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1% (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).
Changes in pregnancy duration:
effects observed, treatment-related
Description (incidence and severity):
In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (=50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1% (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).
Changes in number of pregnant:
no effects observed
Details on maternal toxic effects:
Maternal toxic effects:yes

Details on maternal toxic effects:
Decrease in body weight gain with increasing dose of Choline chloride, see table 2.

Effect levels (maternal animals)

open allclose all
Dose descriptor:
NOAEL
Effect level:
4 160 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
other: developmental toxicity
Dose descriptor:
NOAEL
Effect level:
3 610 mg/kg bw/day (nominal)
Based on:
other: choline hydroxide
Basis for effect level:
other: developmental toxicity
Dose descriptor:
NOEL
Effect level:
10 000 ppm (nominal)
Based on:
test mat.
Basis for effect level:
other: developmental toxicity
Dose descriptor:
NOEL
Effect level:
1 250 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
other: developmental toxicity
Dose descriptor:
NOEL
Effect level:
1 085 mg/kg bw/day (nominal)
Based on:
other: choline hydroxide
Basis for effect level:
other: developmental toxicity
Dose descriptor:
NOEL
Effect level:
1 250 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
other: maternal toxicity
Dose descriptor:
NOEL
Effect level:
1 085 mg/kg bw/day (nominal)
Based on:
other: choline hydroxide
Basis for effect level:
other: maternal toxicity
Dose descriptor:
LOAEL
Effect level:
4 160 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
other: other:
Dose descriptor:
LOAEL
Effect level:
3 610 mg/kg bw/day (nominal)
Based on:
other: choline hydroxide
Basis for effect level:
other: other:
Dose descriptor:
LOAEL
Effect level:
10 800 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
other: developmental toxicity
Dose descriptor:
LOAEL
Effect level:
9 373 mg/kg bw/day (nominal)
Based on:
other: choline hydroxide
Basis for effect level:
other: developmental toxicity

Results (fetuses)

Reduction in number of live offspring:
effects observed, treatment-related
Description (incidence and severity):
In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (=50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1% (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).
Details on embryotoxic / teratogenic effects:
Embryotoxic / teratogenic effects:yes.
Remark: Observed adverse effects are not related to teratogenic effects of Choline chloride but maternal toxicity.

Details on embryotoxic / teratogenic effects:
See table 3

Effect levels (fetuses)

open allclose all
Dose descriptor:
NOAEL
Effect level:
10 000 ppm (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: The administration of food with a content of 1 % (=10,000 ppm) Choline chloride did not affect the development of the offsprings
Dose descriptor:
NOAEL
Effect level:
8 678 ppm (nominal)
Based on:
test mat.
Basis for effect level:
other: Recalculated from NOAEL of choline chloride, regarding the molecular weight of both substances. Basis for effect level: development of the offsprings

Fetal abnormalities

Abnormalities:
not specified

Overall developmental toxicity

Developmental effects observed:
not specified

Any other information on results incl. tables










Result:
The amount of Choline chloride uptake is given per animal and day; per kg mouse/day and within the whole time of experimental treatment as well as per kg intake of Choline chloride in table 1.

























































Table 1
Amount of Choline chloride uptake
Choline chloride concentration in feed (%)mean body weight during experimentmean amount of Choline chloride uptaken
per daytotal
per mouseper kg mouseper mouseper kg mouse
1,0 %40 g0,05 g1,25 g0,90 g22,5 g
2,5 %30 g0,125 g4,16 g2,25 g74,8 g
5,0 %30 g0,250 g10,80 g4,50 g194,4 g
10,0 %25 g0,5 g20,00 g9,00 g360,0 g


The average body weight gain between day 1.-19. of gestation was in the "1 %" Choline chloride group 25.2 g. The average body weight gain was reduced in a dose-dependent manner with the increased Choline chloride concentration. The reduced body weight gain in mice, as shown in table 2, is only partly due to the abortion, because in the "2.5 % group", and even more in the "5 % group" dams, which did not abort, had a significantly lower body weight gain, as the mice which received the feed with 1 % Choline chloride.































































Table 2
mean body weight gain of pregnant mice from day 1-19 of gestation
Choline concentration in feed (%)number of pregnant micemean body weiht gain (g)
1 %=  10 000 ppmtotal 16+ 25,2
without abortion 16+ 25,2
with abortion 0-
2,5 % =  25 000 ppmtotal 12+ 11,9
without abortion 8+ 16,6
with abortion 4+ 2,7
5 % = 50 000 ppmtotal 11+ 3,7
without abortion 3+ 12,6
with abortion 8+ 0,2
10 % = 100 000 ppmtotal 7- 5,2
with abortion 7- 5,2


I
n all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (= 50 000 ppm) it resulted in expulsion of all fetuses, so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the " 5 % group" were well behind in development. The administration of food with a content of 1 % (=10,000 ppm) Choline chloride did not affect the development of the offsprings (Table 3).





























Applicant's summary and conclusion

Conclusions:
The study was classified as reliable with restrictions (Klimisch 2) and meets the requirements for a developmental toxicity study, which was performed on the read-across substance choline chloride. Hence, the results can be considered as reliable and be used for the assessment of possible developmentally toxic effects.
The read-across from Choline chloride to Choline base is justified because the absorption after oral application is very likely to have remained unchanged, information gained from choline chloride for this endpoint can be used without modification. This is due to the fact that, if ingested orally, the contact time of the basic solution to the oesophagus is rather short for causing severe chemical burns which will be necessary to enlarge the oral uptake. Once reaching the stomach, the basic pH of the choline base solution will be immediately neutralized by the gastric acid. Only when ingesting large amounts of choline base, the neutralization capacity of the stomach acid will be used up. However, this scenario is unlikely due to expected pain in the oral cavity and pharynx caused by hydroxide. Also, in case it would have been decided to neutralize the test compound in order to avoid diminished food intake due to the undesired taste and pain, chlorous acid would be the recommended one, resulting in choline chloride anyway.
Hence, only effects of the choline cation have to be regarded and the results gained from choline chloride can be used without modifications.
The feeding of choline chloride over the entire period of gestation, in concentrations of 2.5 %, 5 % and 10 % (25 000 ppm to 100000 ppm), resulted in expulsion of all fetuses and thus to complete abortion in the majority of animals, beginning with 34.8 % abortions (4,160 mg/kg bw/d) to complete loss of all fetuses (20,000 mg/kg bw/d). This "abortion effect"' is not an expression of a specific embryotoxic toxicity but sign of a general toxicity, because not only the mice with abortion but also the animals without abortion had a significantly reduced body weight compared to untreated pregnant mice. This thesis - the lack of a specific embryotoxic effect of Choline chloride - is also supported by the fact that the gavage of food with 1% (= 10,000 ppm ≙ 1,250 mg/kg bw/d) Choline chloride over the entire period of gestation was well tolerated by the dams without symptoms and the fetal development was not disturbed.
The only reason to determine the NOAEL to be 4160 mg/kg bw/d choline chloride (2.5 % in feed, corresponding to 3610 mg/kg bw/day choline hydroxide) and to take this dose level for further risk assessment, was because the IUCLID software requires a numeric value and the first effects on the fetal development were seen in the next higher dose (5 % in feed), although they are not related to possible developmentally toxic effects of the compound itself but to maternal toxicity.
Choline chloride thus had under the given experimental conditions no teratogenic effect, since the product caused only altered development in the fetuses at doses, which also had toxic effects on the dams.
As a consequence, choline chloride and hence choline hydroxide does not need to be classified as toxic to reproduction according to Regulation 1272/2008/EC.
Executive summary:





























In the feeding studies the animals (16 / 12 / 11 or 7 pregnant mice, gestation day 1 -18) were treated daily via the diet with Choline chloride (1 %, 2.5 %, 5 % and 10 %, BASF, 1966). The choline containing bread was given to all experimental animals (pregnant mice from 1 - 18 day of gestation). The number of pregnant mice in the individual test groups was in the "1 % - group" 16, in the "2, 5 % group" 12, in the "5 % group" ~ 11, and the "10 % - group "7 animals. All mice were housed singly in glases and provided with 1 piece of bread every second day and water ad libitum. Thus about 5 grams od food per day were taken in. On gestation day 19, all animals were sacrificed and subject to necropsy and the uteri and fetuses were examined and the mean number of offsprings, the mean foetal body weight, mean foetal length, the foetal resportion rate and the number of anomalies were noted.









The average body weight gain between day 1.-19. of gestation was in the "1 %" Choline chloride group 25.2 g. The average body weight gain was reduced in a dose-dependent manner with the increased Choline chloride concentration. The reduced body weight gain in mice, was only partly due to the abortion, because in the "2.5 % group", and even more in the "5 % group" dams, which did not abort, had a significantly lower body weight gain, as the mice which received the feed with 1 % Choline chloride.









In all 7 animals receiving the Choline chloride 10 % solution (= 100,000 ppm) in the diet and in 8 of 11 mice receiving the bread with 5 % (= 50 000 ppm) it resulted in expulsion of all fetuses,so that in these animals after the death at the 19th day of gestation in the uterus only the implantation sites were detected. Even in the mice fed 2.5 % Choline chloride, 4 of the 12 mice aborted. Moreover, the 32 surviving fetuses of the "5 % group" were well behind in development. The administration of food with a content of 1 % (= 10,000 ppm) Choline chloride did not affect the development of the offsprings.




















The feeding of Choline chloride over the entire period of gestation, in concentrations of 2.5 %, 5 % and 10 % (25,000 ppm to 100,000 ppm), resulted in expulsion of all fetuses and thus to complete abortion in the majority of animals. This "abortion effect" 'is not an expression of a specific embryotoxic toxicity but sign of a general toxicity, because not only the mice with abortion but also the animals without abortion had a significantly reduced body weight than any untreated pregnant mice. This thesis - the lack of a specific embryotoxic effect of Choline chloride - is also supported by the fact that the gavage of food with 1 % (= 10,000 ppm) Choline chloride over the entire period of gestation was well tolerated by the dams without symptoms and the foetal development was not disturbed. The only reason to determine the NOAEL to be 4160 mg/kg bw/d (2.5 % in feed) and to take this dose level for further risk assessment, was because the IUCLID software requires a numeric value and the first effects on the fetal development were seen in the next higher dose (5 % in feed), although they are not related to possible developmentally toxic effects of the compound itself but to maternal toxicity.
Choline chloride thus had under the given experimental conditions, no teratogenic effect, since the product caused only altered development in the foetuses at doses, which also had toxic effects on the dams. The study was classified as reliable with restrictions and meets the requirements for a developmental toxicity study. Choline chloride does not need to be classified as toxic to reproduction according to Regulation 1272/2008/EC.