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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Carcinogenicity

Currently viewing:

Administrative data

Description of key information

In a long term (two year) repeated dose toxicity study with sodium ferrocyanide in rats, the NOAEL was determined to be ≥ 630 and ≥ 450 mg/kg bw/day for females and males, respectively, based on the absence of effects seen at the highest concentration (5000 ppm in the food). This result is read across to potassium ferricyanide (the read across hypothesis is attached in section 13).

Key value for chemical safety assessment

Carcinogenicity: via oral route

Link to relevant study records
Reference
Endpoint:
carcinogenicity: oral
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Justification for type of information:
Based on presence of identical metal-cyanide complex species, sodium ferrocyanide and potassium ferricyanide can be regarded as analogues, which implies that data from sodium ferrocyanide can be read across to tpotassium ferricyanide. The read across hypothesis is attached in 'Attached justification'.
Reason / purpose for cross-reference:
read-across source
Clinical signs:
no effects observed
Mortality:
no mortality observed
Description (incidence):
Findings were generally similar in both the control and treated groups. The percentage mortality of the control rats for both sexes was higher than that of the three treatment groups at the end of the study.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
Body weight of male and female rats in the control and treatment groups were similar throughout the course of the 2-y study. Female rats given 5000 ppm had a slightly lower mean body weight compared to control rats during the latter of the study, resulting in statistically significance during some weeks, 41-49 and 57-61 and week 92, but the weights were all within 7% of the control values for these periods. This is not considered to be toxicologically relevant.
Interim I and II study: Comparable trends.
Food consumption and compound intake (if feeding study):
no effects observed
Description (incidence and severity):
Food consumption differed during the study, sometimes being less compared to controls, sometimes being more compared to controls. In some weeks this was statistically significant, but these differences were not considered to be related to treatment.
Interim I and II study: comparable trends.

The calculated intake (mg/kg bw/d) over the whole study period expressed for m/f:
2-y study; Interim I; Interim II;
50 ppm 4.4/6.2; 5.4/6.8; 4.7/6.8
500 ppm 45.0/62.5; 51.8/69.8; 46.8/63.8
5000 ppm 450.7/630.1; 519.5/692.5; 461.8/672.5
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
effects observed, treatment-related
Description (incidence and severity):
The pattern of water consumption by male and female rats in the control and 50 and 500 ppm treatment groups was similar throughout the study. Male and female rats administered 5000 ppm drank more than control animals during the first nine months of the study. During the last year of the study water quantities were comparable between 5000 ppm group and controls. While the difference seen in the first year of the study must be attributed to treatment with sodium ferrocyanide there is no indication that this is an adverse effect (see also Urinalysis results).
Interim I and II study: Comparable trends, however, the high water intakes seen in rats given 5000 ppm substance during the earlier part of the 2-y study were not repeated in the corresponding periods of the interim studies.
Ophthalmological findings:
not examined
Description (incidence and severity):
not required
Haematological findings:
no effects observed
Description (incidence and severity):
Changes observed in treated animals were not dose-related or common to both sexes on any single occasion, and were not found consistently on different occasions. Therefore none of the effects seen are considered to be a consequence of treatment.
Clinical biochemistry findings:
not examined
Description (incidence and severity):
No adverse effects were observed on weight, macroscopically or microscopically of/on organs nor on urinalysis, therefore adverse effects on clinical chemistry are not expected
Urinalysis findings:
no effects observed
Description (incidence and severity):
Some differences were seen between the results of renal function tests for treated rats compared with control rats. No permanent disturbance of the renal system was apparent. Kidney functions were normal during the study, therefore, the increased water intake of 5000 ppm treated male and female rats in the first part of the 2-y study is not expected to be an adverse effect of the substance.
A trend of increased protein excretion in the urine of both control and treated rats was found. This is a characteristic of ageing rats, which severity or onset was not accelerated by the substance.
Behaviour (functional findings):
not examined
Description (incidence and severity):
not required
Organ weight findings including organ / body weight ratios:
no effects observed
Description (incidence and severity):
Although there was some suggestion of increased caecum weight in male rats given 5000 ppm substance in the interim studies, this increase was not seen in the corresponding group in the 2-y study. Other differences were seen (increased spleen weight, decreased intestinal weight both at 50 ppm in male rats, increased pituitary glands in female rats at 50 ppm), but never consistent over sexes or dose dependent. It was thus concluded that the increased organ weights were not a toxicological relevant adverse effect.
Gross pathological findings:
no effects observed
Histopathological findings: non-neoplastic:
no effects observed
Description (incidence and severity):
Occasionally a single histopathological finding was found with a higher prevalence in one or more groups (lung, liver). However, no clear dose trend is found, no consistent pattern is seen in the male and female groups, therefore it is unlikely that these differences can be attributed to the treatment. In addition, periartritis was seen, but not statistically significant, and this is commonly found in old rats. An increased number of fibrous polyps was seen in the uteri of high dose females, however this is commonly found in old female rats. Since no clear dose response is seen, this was considered not to be related to treatment.
Histopathological findings: neoplastic:
no effects observed
Description (incidence and severity):
No dose related effect was seen in tumours of the pituitary, pancreas and thyroid, which are relatively common in aged rats. Basal cell carcinoma, lipoma, sarcoma, fiborsarcoma and squamous cell carcinoma were found either in the skin or subcutaneous tissues of several animals. However, these kind of tumours have frequently been reported in control rats and therefore, it is unlikely they result from treatment.
Key result
Dose descriptor:
NOAEL
Effect level:
630 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
female
Basis for effect level:
other: No dose-related carcinogenicity was observed up to the highest dose level tested.
Key result
Dose descriptor:
NOAEL
Effect level:
>= 450 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male
Basis for effect level:
other: No dose-related carcinogenicity was observed up to the highest dose level tested.

 Summary of tumour incidence in male rats fed sodium ferrocyanide in the diet at levels of o (control), 50, 500 or 5000 ppm for up to 105 weeks

 

Control

50 ppm

500 ppm

5000 ppm

Total animals/group

48

47

48

48

Total primary tumors

17

16

29

17

Total animals with tumors

15

12

22

14

Total animals with multiple tumors

2

3

5

2

Total benign

13

14

22

10

Total malignant

4

2

7

7

Total malignant with metastasis

2

0

3

2

 

Summary of tumour incidence in female rats fed sodium ferrocyanide in the diet at levels of o (control), 50, 500 or 5000 ppm for up to 107 weeks

 

Control

50 ppm

500 ppm

5000 ppm

Total animals/group

48

48

48

48

Total primary tumors

41

41

34

37

Total animals with tumors

36

33

29

27

Total animals with multiple tumors

4

8

5

7

Total benign

34

35

27

26

Total malignant

7

6

7

11

Total malignant with metastasis

1

0

4

2

 

 

Conclusions:
In a long term (two year) toxicity study with rats performed mainly according to OECD 453, supplemented with two interim studies (49-51 weeks and 80-82 weeks respectively), male and females rats (48/dose) were daily exposed to sodium ferrocyanide, which was mixed in the diet. From these data, the NOAEL was determined to be ≥ 630 and ≥ 450 mg/kg bw/day for females and males, respectively, based on the absence of effects seen at the highest concentration (5000 ppm in the food). This result is read across to potassium ferricyanide.
Executive summary:

In a long term (two year) toxicity study with rats, supplemented with two interim studies (49-51 weeks and 80-82 weeks respectively), male and females rats (48/sexe) were daily exposed to sodium ferrocyanide, which was mixed in the food. During the studies, body weight and food and water intake was monitored at regular intervals. Furthermore, blood and urine samples were examined for several relevant parameters. At the end of the study, rats were killed and organs and tissues were examined macro- and microscopically. Rats exposed to the highest concentration (5000 ppm in food) showed elevated water consumption in the first nine months. The sodium ferrocyanide in the diet did not adversely affect growth or general health of the rats in the three treatment groups. No dose-related variations were found in the haematology or urine analyses. Neither were dose-related differences found in the weight of the organs, or in the (non-neoplastic and neoplastic) histopathology of organs or tissues between the exposed groups or differences with the non-exposed groups. From these data, the NOAEL was determined to be ≥ 630 and ≥ 450 mg/kg bw/day for females and males, respectively, based on the absence of effects seen at the highest concentration (5000 ppm in the food). The results are read across to potassium ferricyanide.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
450 mg/kg bw/day
Study duration:
chronic
Species:
rat
Quality of whole database:
A reliable study is used (Klimisch 2).

Carcinogenicity: via inhalation route

Endpoint conclusion
Endpoint conclusion:
no study available

Carcinogenicity: via dermal route

Endpoint conclusion
Endpoint conclusion:
no study available

Justification for classification or non-classification

Based on the available data, potassium ferricyanide is not need to be classified for carcinogenicity according to CLP Regulation (No) EC 1272/2008.

Additional information

In a long term (two year) toxicity study rats, supplemented with two interim studies (49-51 weeks and 80-82 weeks respectively), male and females rats (48/sex) were daily exposed to sodium ferrocyanide, which was mixed in the food. During the studies, body weight and food and water intake was monitored at regular intervals. Furthermore, blood and urine samples were examined for several relevant parameters. At the end of the study, rats were killed and organs and tissues were examined macro- and microscopically. Rats exposed to the highest concentration (5000 ppm in food) showed elevated water consumption in the first nine months. The sodium ferrocyanide in the diet did not adversely affect growth or general health of the rats in the three treatment groups. No dose-related variations were found in the haematology or urine analyses. Neither were dose-related differences found in the weight of the organs, or in the (non-neoplastic and neoplastic) histopathology of organs or tissues between the exposed groups or differences with the non-exposed groups. From these data, the NOAEL was determined to be ≥ 630 and ≥ 450 mg/kg bw/day for females and males, respectively, based on the absence of effects seen at the highest concentration (5000 ppm in the food). This result is read across to potassium ferricyanide.