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. 2024 Oct 28;22(10):e9018. doi: 10.2903/j.efsa.2024.9018

TABLE 6.

Compositional data, intake values (calculated for chickens for fattening at 15 mg/kg complete feed), reference points and margin of exposure (MOE) for the individual components of Spanish type origanum oil classified according to assessment groups, and combined margin of exposure (MOET) for each assessment group.

Essential oil composition Exposure Hazard characterisation Risk characterisation
Assessment group FLAVIS‐No Highest conc. in the oil Highest feed conc. Intake a Cramer Class b NOAEL c MOE d MOET e
Constituent % mg/kg mg/kg bw per day mg/kg bw per day
CG 1
Methyl citronellate 09.517 0.01 0.0017 0.00015 I 3 20,253
CG 4
Lavandulyl acetate 09.612 0.06 0.0083 0.00074 I 3 4051
CG 5
Oct‐1‐en‐3‐ol 02.023 0.34 0.0503 0.00451 (I) 6.7 1485
Octan‐3‐one 07.062 0.20 0.0296 0.00265 II 0.91 343
Octan‐3‐ol 02.098 0.03 0.0047 0.00042 I 3 7187
MOET CG 5 268
CG 6
Linalool 02.042 1.34 0.2004 0.01799 (I) 117 6503
4‐Terpinenol 02.072 0.82 0.1230 0.01104 (I) 125 f 11,320
2‐(4‐Methylphenyl)propan‐2‐ol 02.042 0.03 0.0041 0.00039 I 3 7682
transp‐2‐Menthen‐1‐ol 0.02 0.0035 0.00031 I 3 9686
Spathulenol 0.02 0.0027 0.00024 I 3 12,377
MOET CG 06 1798
CG 8
d,l‐Borneol 02.016 0.46 0.0693 0.00622 (I) 15 2411
Camphor 0.22 0.0329 0.00295 II 0.91 309
Dihydrocarvone 07.128 0.04 0.0062 0.00055 II 0.91 1648
Carvenone 0.02 0.0029 0.00026 II 0.91 3557
MOET CG 08 220
CG 10
2‐Methyl‐5‐(propan‐2‐ylidene)cyclohexane‐1,4‐diol 0.12 0.0183 0.00164 I 3 1826
CG 13
Linalool oxide 13.140 0.01 0.0021 0.00019 II 0.91 4827
CG 16
1,8‐Cineole 03.001 0.28 0.0422 0.00378 (II) 100 26,428
CG 25
Thymohydroquinone 0.20 0.0300 0.00269 I 3 1114
CG 26
1‐Isopropyl‐2‐methoxy‐4‐methylbenzene 04.043 0.25 0.0375 0.00337 I 3 891
CG 31, II (Acyclic alkanes)
Myrcene 01.008 1.25 0.1869 0.01678 (I) 44 2622
CG 31, III (Cyclohexene hydrocarbons)
γ‐Terpinene 01.020 5.72 0.8580 0.07703 (I) 250 3246
α‐Terpinene 01.019 1.45 0.2178 0.01955 (I) 30 g 1534
d‐Limonene 01.045 0.39 0.0588 0.00528 (I) 250 47,361
α‐Phellandrene 01.006 0.26 0.0393 0.00353 (I) 30 g 8503
MOET CG 31, III 910
CG 31, IVe (Benzene hydrocarbons, alkyl)
p‐Cymene 01.002 8.28 1.2425 0.11154 (I) 154 1381
Abietatriene 0.03 0.0047 0.00044 I 3 7187
MOET CG 31, IVe 1158
CG 31, V (Bi‐, tricyclic, non‐aromatic hydrocarbons)
β‐Caryophyllene 01.007 3.69 0.5540 0.04973 (I) 222 4464
α‐Thujene 0.88 0.1322 0.01186 (I) 222 18,713
α‐Pinene 01.004 0.88 0.1322 0.01186 (I) 222 18,713
Camphene 01.009 0.15 0.0224 0.00201 I 3 1495
Palustradiene 0.06 0.0092 0.00082 I 3 3652
MOET CG 31, V 785
CG 32
β‐Caryophyllene epoxide 16.043 0.57 0.0852 0.00765 (III) 119 15,558
Thujones
α‐Thujone 0.19 0.0287 0.00257 (III) 8 3110
β‐Thujone 0.03 0.0047 0.00042 (III) 8 19,164
2676
a

Intake calculations for the individual components are based on the use level of 15 mg/kg in feed for chickens for fattening, the species with the highest ratio of feed intake/body weight.

b

When a NOAEL value is available or read‐across is applied, the allocation to the Cramer class is put into parentheses.

c

Values in bold refer to those components for which the NOAEL value was available, values in italics are the 5th percentile of the distribution of NOAELs of the corresponding Cramer Class, other values (plain text) are NOAELs extrapolated by using read‐across.

d

The MOE for each component is calculated as the ratio of the reference point (no observed adverse effect level, NOAEL) to the intake.

e

The combined margin of exposure (MOET) is calculated for each assessment group as the reciprocal of the sum of the reciprocals of the MOE of the individual substances.

f

An uncertainty factor of 2 was applied to the NOAEL of 250 mg/kg bw per day for terpineol (short duration of the study).

g

An uncertainty factor of 2 was applied to the NOAEL of 60 mg/kg bw per day for α‐terpinene (nature of the study).