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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Workers - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
58.43 mg/m³
Most sensitive endpoint:
carcinogenicity
DNEL related information
Overall assessment factor (AF):
38
Modified dose descriptor starting point:
NOAEC
Acute/short term exposure
DNEL related information

Local effects

Acute/short term exposure
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
8.29 mg/kg bw/day
Most sensitive endpoint:
carcinogenicity
DNEL related information
Overall assessment factor (AF):
150
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

Workers - Hazard for the eyes

Additional information - workers

Acute DNELs:

Worker: Production of Corn Steep Liquor is in excess of 10 t/y. According to the REACh "Guidance on information requirements and chemical safety assessment, Part B: Hazard Assessment", above 10 t/y, the establishment of acute toxicity DNEL is unnecessary in most cases, as the DNEL based on long-term exposure is normally sufficient to ensure that adverse effects do not occur. Thus, as long term DNELs are available for Corn Steep Liquor and this substance is not classified for acute toxicity via any route of exposure, separate acute DNELs were not derived.

Long-term DNELs:

DNELs are based on a 2 -year oral toxicity and carcinogenicity rat study (key study selected) entitled "Long-term toxicity/carcinogenicity study of calcium lactate in F344 rats” (Maekawa et al., 1991). This study allowed for an estimation of chronic exposure the read -across substance lactic acid. The most sensitive endpoint was selected as carcinogenicity.

Starting Dose for DNEL calculation:

1243 mg/kg bw/day (identified by registrant as the NOAEL for high-dose male rats; this represents the calculated intake of lactic acid in high-dose male rats).

Modified dose for DNEL Calculation

Worker – Inhalation = 1243 mg/kg bw/day x 1/0.38 x 6.7/10 = 2191 mg/m3(no adjustment for absorption)

Worker – Dermal = 1243 mg/kg bw/day (no adjustment for absorption). 

 

Assessment Factors (AF)

Worker – Inhalation = 2.5 (for non-metabolic species differences) x 5 for (intraspecies difference); no scaling factor required (as per REACh guidance) x 3 (quality of whole database)

Worker – Dermal = 4 x 2.5 (species differences) x 5 for (intraspecies difference); no scaling factor required (as per REACh guidance) x 3 (quality of whole database)

Absorption

Absorption by all routes was conservatively estimated to be 100%.

  

Final DNELs

Worker – Inhalation = 58.43 mg/m3

Worker – Dermal = 8.29 mg/kg bw/day

References

Maekawa et al., Fd Chem Toxic 1991;29:589 -594

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
14.4 mg/m³
Most sensitive endpoint:
carcinogenicity
DNEL related information
Overall assessment factor (AF):
75
Acute/short term exposure
DNEL related information

Local effects

Acute/short term exposure
DNEL related information

General Population - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
4.14 mg/kg bw/day
Most sensitive endpoint:
carcinogenicity
DNEL related information
Overall assessment factor (AF):
300
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

General Population - Hazard via oral route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
4.14 mg/kg bw/day
Most sensitive endpoint:
carcinogenicity
DNEL related information
Overall assessment factor (AF):
300
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

General Population - Hazard for the eyes

Additional information - General Population

DNEL calculation is performed on the read-across substance lactic acid

Acute DNEL:

General population: Production of Corn Steep Liquor is in excess of 10 t/y. According to the REACh "Guidance on information requirements and chemical safety assessment, Part B: Hazard Assessment", above 10 t/y, the establishment of acute toxicity DNEL is unnecessary in most cases, as the DNEL based on long-term exposure is normally sufficient to ensure that adverse effects do not occur. Thus, as long term DNELs are available for Corn Steep Liquor and this substance is not classified for acute toxicity via any route of exposure, separate acute DNELs were not derived.

Long-term DNELs:

DNELs are based on a 2 -year oral toxicity and carcinogenicity rat study (key study selected) entitled "Long-term toxicity/carcinogenicity study of calcium lactate in F344 rats” (Maekawa et al., 1991). This study allowed for an estimation of chronic exposure the read -across substance lactic acid. The most sensitive endpoint was selected as carcinogenicity.

Starting Dose for DNEL calculation:

1243 mg/kg bw/day (identified by registrant as the NOAEL for high-dose male rats; this represents the calculated intake of lactic acid in high-dose male rats).

Modified dose for DNEL Calculation

General Population – Inhalation = 1243 mg/kg bw/day x 1/1.15 = 1080 mg/m3 (no adjustment for absorption)

General Population – Oral = 1243 mg/kg bw/day (no adjustment for absorption)

General Population - Dermal - 1243 mg/kg bw/day (no adjustment for absorption)

Assessment Factors (AF)

General Population – Inhalation = 2.5 (for non-metabolic species differences) x 10 (for intraspecies difference); no scaling factor required (as per REACh guidance) x 3 (quality of whole database)

General Population – Oral = 4 x 2.5 (species differences) x 10 for (intraspecies difference); no scaling factor required (as per REACh guidance) x 3 (quality of whole database)

General Population - Dermal = 4 x 2.5 (species differences) x 10 for (intraspecies difference); no scaling factor required (as per REACh guidance) x 3 (quality of whole database)

 

Absorption

Absorption by all routes was conservatively estimated to be 100%.

  

Final DNELs

General Population - Inhalation = 14.4 mg/m3

General Population - Oral = 4.14 mg/kg bw/day

General Population - Dermal = 4.14 mg/kg bw/day

References

Maekawa et al., Fd Chem Toxic 1991;29:589 -594