Citronellyl formate

Toxicological Summary

Workers - Hazard via inhalation route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

4.94 mg/m³

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Oral

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

50

Dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Modified dose descriptor starting point:

NOAEC

Value:

246.8 mg/m³

Explanation for the modification of the dose descriptor starting point:

There are no relevant experimental data on repeated exposure by inhalation. For details on calculations please refer to discussion.

AF for dose response relationship:

1

Justification:

The dose response relationship is considered unremarkable, therefore no additional factor is used.

AF for differences in duration of exposure:

4

Justification:

As the NOAEL of a combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) with an exposure time of 49 days was used as point of departure an AF of 4 is considered as adequate for the exposure duration extrapolation.

AF for interspecies differences (allometric scaling):

1

Justification:

No allometric scalling is applied for inhalation as the inhalative data is standardised with reference to the respiratory rates. Respiratory rates depend directly on caloric demand, therefore inhalative study results are already extrapolated to humans on the basis of metabolic rate scaling (=allometric scaling).

AF for other interspecies differences:

2.5

Justification:

Recommended AF for other interspecies differences.

AF for intraspecies differences:

5

Justification:

The default value for the relatively homogenous group "worker" is used.

AF for the quality of the whole database:

1

Justification:

The quality of the whole data base is considered to be sufficient and uncritical.

AF for remaining uncertainties:

1

Justification:

The approach used for DNEL derivation is conservative. No further assessment factors are required.

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

DNEL related information

Local effects

Long term exposure

Hazard assessment conclusion:

no hazard identified

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

1.4 mg/kg bw/day

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Oral

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

200

Dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Modified dose descriptor starting point:

NOAEL

Value:

280 mg/kg bw/day

Explanation for the modification of the dose descriptor starting point:

There are no relevant experimental data on repeated exposure by dermal route. For details on calculations please refer to discussion.

AF for dose response relationship:

1

Justification:

The dose response relationship is considered unremarkable, therefore no additional factor is used.

AF for differences in duration of exposure:

4

Justification:

As the NOAEL of a combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) with an exposure time of 49 days was used as point of departure an AF of 4 is considered as adequate for the exposure duration extrapolation.

AF for interspecies differences (allometric scaling):

4

Justification:

The default allometric scaling factor for the differences between rats and humans is used.

AF for other interspecies differences:

2.5

Justification:

Recommended AF for other interspecies differences.

AF for intraspecies differences:

5

Justification:

The default value for the relatively homogenous group "worker" is used.

AF for the quality of the whole database:

1

Justification:

The quality of the whole data base is considered to be sufficient and uncritical.

AF for remaining uncertainties:

1

Justification:

The approach used for DNEL derivation is conservative. No further assessment factors are required.

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

Most sensitive endpoint:

acute toxicity

Route of original study:

Dermal

DNEL related information

Local effects

Long term exposure

Hazard assessment conclusion:

medium hazard (no threshold derived)

Most sensitive endpoint:

sensitisation (skin)

Acute/short term exposure

Hazard assessment conclusion:

medium hazard (no threshold derived)

Most sensitive endpoint:

sensitisation (skin)

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:

no hazard identified

Additional information - workers

General

DNEL derivation for the test substance is performed under consideration of the recommendations of ECHA. In view of the data used for evaluation, the "quality of whole database factors" and "dose-response factors" are considered to amount each to a value of 1, and are thus not shown in the calculations presented below.

 

Workers – Hazard via inhalation route

 

Long term systemic inhalation DNEL, worker

The DNEL long term, systemic (inhalation) is derived by route-to route extrapolation from the repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422).

 

Step 1: Selection of the relevant dose descriptor (starting point):

The combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) is selected for DNEL derivation as it is the relevant repeated dose study performed in accordance to OECD guideline and GLP. In this study, the NOAEL is 200 mg/kg bw/day.

 

Step 2: Modification into a correct starting point:

Using a conservative approach, a worker DNEL (long term inhalation exposure) is derived considering a two times higher absorption via inhalation than oral absorption.

 

Relevant dose descriptor (NOAEL): 200 mg/kg bw/day

Standard respiratory volume of the rat (sRVrat) for 8 hours: 0.38 m³/kg bw/d

Oral absorption of the rat / inhalation absorption of humans (ABSoral-rat / ABSinh-human): 0.5

Standard respiratory volume of humans (sRVhuman) for 8 hours: 6.7 m³

Worker respiratory volume (wRV) for 8 hours with light physical activity: 10 m³

Frequency of exposure in study: 7 days/week

Frequency of worker exposure: 5 days/week

 

Corrected inhalatory NOAEC for workers

= 200 mg/kg bw/day* 0.5 * (1 / 0.38 m³/kg bw/day) * (6.7 m³/10 m³) * (7/5)

= 246.8 mg/m³

 

Step 3: Use of assessment factors: 50

Interspecies: no allometric scaling factor is applied because an oral-to-inhalation route extrapolation is performed.

Interspecies AF, remaining differences: 2.5

Intraspecies AF (worker): 5

Exposure duration AF: 4

Remaining uncertainties AF: 1

 

In conclusion, long term systemic inhalation DNEL, workers = 4.94 mg/m3

 

Short term systemic inhalation DNEL, worker

According to ECHA Guidance on information requirements and chemical safety, Chapter R.8, Appendix R. 8-8, a DNEL for acute toxicity should be derived if an acute toxicity hazard (leading to C&L) has been identified. The test material is not classified and labelled for acute systemic toxicity, according to Regulation (EC) No 1272/2008 (CLP). Since the vapour pressure of the test item is low (4.0 Pa at 20 °C) peak exposure via inhalation route is not expected. Thus, no DNEL is required.

Short and long term local inhalation DNEL, worker

No data on respiratory irritation are available. As the substance is not classified for eye irritation according to Regulation (EC) No 1272/2008 (CLP) and its vapour pressure is low (4.0 Pa at 20 °C), no irritating effects on respiratory system are expected. No DNEL was derived.

 

Workers – Hazard via dermal route

Long term systemic dermal DNEL, worker

The DNEL long term, systemic (dermal) is derived by route-to route extrapolation from the repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422).

  

Step 1: Selection of the relevant dose descriptor (starting point):

The combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) is selected for DNEL derivation as it is the relevant repeated dose study performed in accordance to OECD guideline and GLP. In this study, the oral NOAEL is 200 mg/kg bw/day.

 

Step 2: Modification of the starting point:

The dermal uptake is considered to be 100 % of the oral uptake in the worst case.

Factor for dermal NOAEL= 100 % oral / 100 % dermal= 1

Frequency of exposure in study: 7 days/week

Frequency of worker exposure: 5 days/week

 

oral NOAEL 200 mg/kg bw/day * 1 * (7/5) = 280 mg/kg bw/day dermal NOAEL

 

Step 3: Use of assessment factors: 200

Interspecies AF, allometric scaling (rat to human): 4

Interspecies AF, remaining differences: 2.5

Intraspecies AF (worker): 5

Exposure duration AF: 4

Remaining uncertainties AF: 1

 

In conclusion, long term systemic dermal DNEL, workers = 1.4 mg/kg bw/day

 

Short term systemic dermal DNEL, worker

According to ECHA Guidance on information requirements and chemical safety, Chapter R.8, Appendix R. 8-8, a DNEL for acute toxicity should be derived if an acute toxicity hazard (leading to C&L) has been identified. The test material is not classified and labelled for acute systemic toxicity, according to Regulation (EC) No 1272/2008 (CLP). Thus, no DNEL is required.

 

Long term local dermal DNEL, worker

The substance is classified as skin sensitizer (Cat 1B, H317) and skin irritant (Cat 2, H315) in respective studies and based on the results a medium hazard is assumed for this endpoint and a qualitative risk assessment is conducted (Guidance on information requirements and chemical safety assessment Part E: Risk Characterisation, Version 3.0, May 2016).

 

Short term local dermal DNEL, worker

The substance is classified as skin sensitizer (Cat 1B, H317) and skin irritant (Cat 2, H315) in respective studies and based on the results a medium hazard is assumed for this endpoint anda qualitative risk assessment is conducted (Guidance on information requirements and chemical safety assessment Part E: Risk Characterisation, Version 3.0, May 2016).

 

Worker – Hazard for the eyes

The test item is not classified for eye irritation or severe eye damage according to Regulation (EC) No 1272/2008 (CLP). Thus, no qualitative risk assessment is required. 

 

 

References

(not included as endpoint study record)

- ECHA (2012). Guidance on information requirements and chemical safety assessment. Chapter R.8: Characterisation of dose [concentration]-response for human health. Version 2.1. November 2012.

- ECHA (2014). Guidance on information requirements and chemical safety assessment. Chapter R.7.12: Endpoint specific guidance: Guidance on Toxicokinetics. November 2014.

- ECHA (2012) Practical Guide 15: How to undertake a qualitative human health assessment and document it in a chemical safety report, November 2012.

- ECHA (2016). Guidance on information requirements and chemical safety assessment.Part E: Risk Characterisation, Version 3.0, May 2016.

General Population - Hazard via inhalation route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

0.87 mg/m³

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Oral

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

100

Dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Modified dose descriptor starting point:

NOAEC

Value:

86.9 mg/m³

Explanation for the modification of the dose descriptor starting point:

There are no relevant experimental data on repeated exposure by inhalation. For details on calculations please refer to discussion.

AF for dose response relationship:

1

Justification:

The dose response relationship is considered unremarkable, therefore no additional factor is used.

AF for differences in duration of exposure:

4

Justification:

As the NOAEL of a combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) with an exposure time of 49 days was used as point of departure an AF of 4 is considered as adequate for the exposure duration extrapolation.

AF for interspecies differences (allometric scaling):

1

Justification:

No allometric scalling is applied for inhalation as the inhalative data is standardized with reference to the respiratory rates. Respiratory rates depend directly on caloric demand, therefore inhalative study results are already extrapolated to humans on the basis of metabolic rate scaling (=allometric scaling).

AF for other interspecies differences:

2.5

Justification:

Recommended AF for other interspecies differences.

AF for intraspecies differences:

10

Justification:

The default value for the relatively homogenous group "general population" is used.

AF for the quality of the whole database:

1

Justification:

The quality of the whole data base is considered to be sufficient and uncritical.

AF for remaining uncertainties:

1

Justification:

The approach used for DNEL derivation is conservative. No further assessment factors are required.

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

DNEL related information

Local effects

Long term exposure

Hazard assessment conclusion:

no hazard identified

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

DNEL related information

General Population - Hazard via dermal route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

0.5 mg/kg bw/day

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Oral

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

400

Dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Modified dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Explanation for the modification of the dose descriptor starting point:

There are no relevant experimental data on repeated exposure by dermal route. For details on calculations please refer to discussion.

AF for dose response relationship:

1

Justification:

The dose response relationship is considered unremarkable, therefore no additional factor is used.

AF for differences in duration of exposure:

4

Justification:

As the NOAEL of a combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) with an exposure time of 49 days (was used as point of departure an AF of 4 is considered as adequate for the exposure duration extrapolation

AF for interspecies differences (allometric scaling):

4

Justification:

The default allometric scaling factor for the differences between rats and humans is used.

AF for other interspecies differences:

2.5

Justification:

Recommended AF for other interspecies differences.

AF for intraspecies differences:

10

Justification:

The default value for the relatively homogenous group "general population" is used.

AF for the quality of the whole database:

1

Justification:

The quality of the whole data base is considered to be sufficient and uncritical.

AF for remaining uncertainties:

1

Justification:

The approach used for DNEL derivation is conservative. No further assessment factors are required.

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

Most sensitive endpoint:

acute toxicity

Route of original study:

Dermal

DNEL related information

Local effects

Long term exposure

Hazard assessment conclusion:

medium hazard (no threshold derived)

Most sensitive endpoint:

sensitisation (skin)

Acute/short term exposure

Hazard assessment conclusion:

medium hazard (no threshold derived)

Most sensitive endpoint:

sensitisation (skin)

General Population - Hazard via oral route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

0.5 mg/kg bw/day

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Oral

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

400

Dose descriptor starting point:

NOAEL

Value:

200 mg/kg bw/day

Explanation for the modification of the dose descriptor starting point:

No route to route extrapolation was used as one repeated oral exposure study was available. For details on calculations please refer to discussion.

AF for dose response relationship:

1

Justification:

The dose response relationship is considered unremarkable, therefore no additional factor is used.

AF for differences in duration of exposure:

4

Justification:

As the NOAEL of a combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422) with an exposure time of 49 days was used as point of departure an AF of 4 is considered as adequate for the exposure duration extrapolation.

AF for interspecies differences (allometric scaling):

4

Justification:

The default allometric scaling factor for the differences between rats and humans is used.

AF for other interspecies differences:

2.5

Justification:

Recommended AF for other interspecies differences.

AF for intraspecies differences:

10

Justification:

The default value for the relatively homogenous group "general population" is used.

AF for the quality of the whole database:

1

Justification:

The quality of the whole data base is considered to be sufficient and uncritical.

AF for remaining uncertainties:

1

Justification:

The approach used for DNEL derivation is conservative. No further assessment factors are required.

Acute/short term exposure

Hazard assessment conclusion:

no hazard identified

DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:

no hazard identified

Additional information - General Population

General

DNEL derivation for the test substance is performed under consideration of the recommendations of ECHA. In view of the data used for evaluation, the "quality of whole database factors" and "dose-response factors" are considered to amount each to a value of 1, and are thus not shown in the calculations presented below.

 

General population – Hazard via inhalation route

Long term systemic inhalation DNEL, General population

The DNEL long term, systemic (inhalation) is derived by route-to route extrapolation from the repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422).

  

Step 1: Selection of the relevant dose descriptor (starting point):

The combined repeated dose oral toxicity study (OECD 422) is selected for DNEL derivation as it is the relevant repeated dose study performed in accordance to OECD guideline and GLP. In this study, the oral NOAEL is 200 mg/kg bw/day.

 

Step 2: Modification into a correct starting point:

Using a conservative approach, a general population DNEL (long term inhalation exposure) is derived considering a two times higher absorption via inhalation than oral absorption.

 

Relevant dose descriptor (NOAEL): 200 mg/kg bw/day

Standard respiratory volume of the rat (sRVrat) for 24 hours: 1.15 m³/kg bw/d

Oral absorption of the rat / inhalation absorption of humans (ABSoral-rat / ABSinh-human): 0.5

Frequency of exposure in study: 7 days/week

Frequency of general population exposure: 7 days/week

 

Corrected inhalatory NOAEC for general population

= 200 mg/kg bw/day * 0.5 * (1 / 1.15 m³/kg bw/day) * (7/7)

= 86.9 mg/m³

 

Step 3: Use of assessment factors: 100

Interspecies: no allometric scaling factor is applied because an oral-to-inhalation route extrapolation is performed.

Interspecies AF, remaining differences: 2.5

Intraspecies AF (general population): 10

Exposure duration AF: 4

Remaining uncertainties AF: 1

 

In conclusion, long term systemic inhalation DNEL, general population = 0.87 mg/m3

 

Short term systemic inhalation DNEL, General population

According to ECHA Guidance on information requirements and chemical safety, Chapter R.8, Appendix R. 8-8, a DNEL for acute toxicity should be derived if an acute toxicity hazard (leading to C&L) has been identified. The test material is not classified and labelled for acute systemic toxicity, according to Regulation (EC) No 1272/2008 (CLP). Since the vapour pressure of the test item is low (4.0 Pa at 20 °C) peak exposure via inhalation route is not expected. Thus, no DNEL is required.

 

Short and long term local inhalation DNEL, General population

No data on respiratory irritation are available. As the substance is not classified for eye irritation according to Regulation (EC) No 1272/2008 (CLP) and its vapour pressure is low (4.0 Pa at 20 °C), no irritating effects on respiratory system are expected. No DNEL was derived.

 

General population – Hazard via dermal route

Long term systemic dermal DNEL, General population

The DNEL long term, systemic (dermal) is derived by route-to route extrapolation from the repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422).

  

Step 1: Selection of the relevant dose descriptor (starting point):

The combined repeated dose toxicity study (OECD 422) is selected for DNEL derivation as it is the relevant repeated dose study performed in accordance to OECD guideline and GLP. In this study, the oral NOAEL is 200 mg/kg bw/day.

 

Step 2: Modification of the starting point:

The dermal uptake is considered to be 100 % of the oral uptake in the worst case.

Factor for dermal NOAEL= 100 % oral / 100 % dermal= 1

Frequency of exposure in study: 7 days/week

Frequency of general population exposure: 7 days/week

oral NOAEL 200 mg/kg bw/day * 1 * (7/7) = 200 mg/kg bw/day dermal NOAEL

 

Step 3: Use of assessment factors: 400

Interspecies AF, allometric scaling (rat to human): 4

Interspecies AF, remaining differences: 2.5

Intraspecies AF (general population): 10

Exposure duration AF: 4

Remaining uncertainties AF: 1

 

In conclusion, long term systemic dermal DNEL, general population = 0.5 mg/kg bw/day

 

Short term systemic dermal DNEL, General population

According to ECHA Guidance on information requirements and chemical safety, Chapter R.8, Appendix R. 8-8, a DNEL for acute toxicity should be derived if an acute toxicity hazard (leading to C&L) has been identified. The test material is not classified and labelled for acute systemic toxicity, according to Regulation (EC) No 1272/2008 (CLP). Thus, no DNEL is required.

 

Long term local dermal DNEL, General population

The substance is classified as skin sensitizer (Cat 1B, H317) and skin irritant (Cat 2, H315) in respective studies and based on the results a medium hazard is assumed for this endpoint and a qualitative risk assessment is conducted (Guidance on information requirements and chemical safety assessment Part E: Risk Characterisation, Version 3.0, May 2016).

 

Short term local dermal DNEL, General population

The substance is classified as skin sensitizer (Cat 1B, H317) and skin irritant (Cat 2, H315) in respective studies and based on the results a medium hazard is assumed for this endpoint anda qualitative risk assessment is conducted (Guidance on information requirements and chemical safety assessment Part E: Risk Characterisation, Version 3.0, May 2016).

 

 

General population – Hazard via oral route

Long term systemic oral DNEL, General population

The DNEL long term, systemic (oral) is derived from the combined repeated dose oral toxicity study with the reproduction/developmental toxicity screening test (OECD 422).

  

Step 1: Selection of the relevant dose descriptor (starting point):

The combined repeated dose toxicity study (OECD 422) is selected for DNEL derivation as it is the relevant repeated dose study performed in accordance to OECD guideline and GLP. In this study, the oral NOAEL is 200 mg/kg bw/day.

 

Step 2: Modification of the starting point:

No modification is used as the same exposure route is considered.

 

Step 3: Use of assessment factors: 400

Interspecies AF, allometric scaling (rat to human): 4

Interspecies AF, remaining differences: 2.5

Intraspecies AF (general population): 10

Exposure duration AF: 4

Remaining uncertainties AF: 1

 

In conclusion, long term systemic oral DNEL, general population = 0.5 mg/kg bw/day

 

Short term systemic oral DNEL, General population

According to ECHA Guidance on information requirements and chemical safety, Chapter R.8, Appendix R. 8-8, a DNEL for acute toxicity should be derived if an acute toxicity hazard (leading to C&L) has been identified. The test material is not classified and labelled for acute oral systemic toxicity, according to Regulation (EC) No 1272/2008 (CLP). Thus, no DNEL is required. 

 

General population – Hazard for the eyes

The test item is not classified for eye irritation or severe eye damage according to Regulation (EC) No 1272/2008 (CLP). Thus, no qualitative risk assessment is required. 

 

 

References

(not included as endpoint study record)

- ECHA (2012). Guidance on information requirements and chemical safety assessment. Chapter R.8: Characterisation of dose [concentration]-response for human health. Version 2.1. November 2012.

- ECHA (2014). Guidance on information requirements and chemical safety assessment.Chapter R.7.12: Endpoint specific guidance: Guidance on Toxicokinetics. November 2014.

- ECHA (2012) Practical Guide 15: How to undertake a qualitative human health assessment and document it in a chemical safety report, November 2012.

- ECHA (2016). Guidance on information requirements and chemical safety assessment.Part E: Risk Characterisation, Version 3.0, May 2016.