Derive the multiplying factor for aquatic-toxic substances under CLP Annex I Table 4.1.3. Works for acute L(E)C50 and chronic NOEC, with the rapidly-degradable shift.
Everything you need is in the aquatic toxicity data for the substance, not the mixture.
Note the M-factor may already be stated outright in Section 3 or in the Annex VI harmonised entry. If so, use that value directly; this tool is for deriving it when only the raw toxicity numbers are given.
Enter the toxicity value as a positive number in milligrams per litre.
One tool covers both acute L(E)C50 and chronic NOEC derivations. Same formula, different starting band.
A single checkbox applies the one-decade shift for rapidly degradable substances on the chronic side.
The result tells you which Table 4.1.3 band your value falls into, so the verdict is auditable.
For each order of magnitude beyond the highest band, the M-factor multiplies by 10. The acute column applies to L(E)C50 and to chronic NOEC of substances that are not rapidly degradable. The chronic column applies to NOEC of rapidly degradable substances.
| L(E)C50 / NOEC band (mg/L) | Acute & chronic (not rapidly degradable) | Chronic (rapidly degradable) |
|---|---|---|
| 0.1 to 1 | 1 | — |
| 0.01 to 0.1 | 10 | 1 |
| 0.001 to 0.01 | 100 | 10 |
| 0.0001 to 0.001 | 1000 | 100 |
| further decades | ×10 per decade | ×10 per decade |
Disclaimer: Provided as an aid for understanding CLP Annex I Table 4.1.3. Always verify M-factor derivations against the current regulatory text and your supplier-provided data, and consult a qualified chemical safety adviser when in doubt.