INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY WORLD HEALTH ORGANIZATION SAFETY EVALUATION OF CERTAIN FOOD ADDITIVES AND CONTAMINANTS WHO FOOD ADDITIVES SERIES 40 Prepared by: The forty-ninth meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA) World Health Organization, Geneva 1998 ESTERS OF ALIPHATIC ACYCLIC PRIMARY ALCOHOLS WITH ALIPHATIC LINEAR SATURATED CARBOXYLIC ACIDS First draft prepared by Dr J. Gry, Institute of Toxicology, National Food Agency of Denmark Ministry of Food, Agriculture and Fisheries Soborg, Denmark 1. Evaluation 1.1 Introduction 1.2 Estimated daily per capita intake 1.3 Absorption, metabolism and elimination 1.4 Application of the Procedure for the Safety Evaluation of Flavouring Agents 1.5 Consideration of combined intakes 1.6 Conclusions 2. Relevant background information 2.1 Explanation 2.2 Intake data 2.3 Biological data 2.3.1 Absorption and metabolism 2.3.2 Toxicological studies 2.3.2.1 Acute toxicity 2.3.2.2 Short-term toxicity 2.3.2.3 Long-term toxicity 2.3.2.4 Genotoxicity 2.3.2.5 Reproductive toxicity 2.3.2.6 Developmental toxicity 3. References 1. EVALUATION 1.1 Introduction The Committee evaluated a group of esters of 67 aliphatic linear and branched-chain saturated and monounsaturated primary alcohols and aliphatic linear saturated carboxylic acids using the Procedure for the Safety Evaluation of Flavouring Agents (the "Procedure") (see Figure 1 and Table 1). One member of the group, butyl acetate, was previously evaluated at the eleventh meeting, when the Committee was unable to establish an ADI due to a lack of data (Annex 1, reference 14). Table 1. Summary of results of safety evaluations on esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids Step 1: 2-Ethylbutyl acetate is in structural Class II, the human intake threshold of which is 540 µg per day. All of the other substances in the group are in structural Class I, the human intake threshold of which is 1800 µg per day. Step 2: cis-3-/trans-2-hexenyl propionate is postponed. All of the other substances in this group are metabolized to innocuous products. No. Substance Step A3 Step A4 Comments Conclusion based Does intake exceed the Endogenous or on current levels human intake threshold?1 metabolized to of intake Intake estimates endogenous (µg/person per day) substances? 0117 Propyl formate No No safety concern USA: 0.38 Europe: 5.0 0118 Butyl formate No No safety concern USA: 0.17 Europe: 21 0119 n-Amyl formate No No safety concern USA: 110 Europe: 29 0120 Hexyl formate No No safety concern USA: 8.0 Europe: 8.7 0121 Heptyl formate No No safety concern USA: 0.10 Europe: 0.00 0122 Octyl formate No No safety concern USA: 0.95 Europe: 0.14 0123 cis-3-Hexenyl formate No No safety concern USA: 1.7 Europe: 43 0124 Isobutyl formate No No safety concern USA: 1.5 Europe: 4.7 0125 Methyl acetate No No safety concern USA: 110 Europe: 460 0126 Propyl acetate No No safety concern USA: 440 Europe: 180 0127 Butyl acetate No No safety concern USA: 170 Europe: 1200 Table 1. Continued... No. Substance Step A3 Step A4 Comments Conclusion based Does intake exceed the Endogenous or on current levels human intake threshold?1 metabolized to of intake Intake estimates endogenous (µg/person per day) substances? 0128 Hexyl acetate Yes Yes Hexanoic acid, the metabolite No safety concern USA: 160 Europe: 3200 of the component hexyl alcohol, and acetic acid are endogenous 0129 Heptyl acetate No No safety concern USA: 2.3 Europe: 56 0130 Octyl acetate No No safety concern USA: 9.5 Europe: 83 0131 Nonyl acetate No No safety concern USA: 2.5 Europe: 6.6 0132 Decyl acetate No No safety concern USA: 21 Europe: 7.3 0133 Lauryl acetate No No safety concern USA: 0.57 Europe: 9.3 0134 cis-3-Hexenyl acetate No No safety concern USA: 57 Europe: 640 0135 trans-3-Heptenyl acetate No No safety concern USA: 0.76 Europe: 0.24 0136 10-Undecen-1-yl acetate No No safety concern USA: 0.10 Europe: 0.83 0137 Isobutyl acetate No No safety concern USA: 1300 Europe: 1200 0138 2-Methylbutyl acetate No No safety concern USA: 360 Europe: 130 0140 2-Ethylbutyl acetate No No safety concern USA: 0.17 Europe: 4.0 0141 Methyl propionate No No safety concern USA: 30 Europe: 9.3 Table 1. Continued... No. Substance Step A3 Step A4 Comments Conclusion based Does intake exceed the Endogenous or on current levels human intake threshold?1 metabolized to of intake Intake estimates endogenous (µg/person per day) substances? 0142 Propyl propionate No No safety concern USA: 44 Europe: 9.6 0143 Butyl propionate No No safety concern USA: 1.1 Europe: 10 0144 Hexyl propionate No No safety concern USA: 3.0 Europe: 5.7 0145 Octyl propionate No No safety concern USA: 0.02 Europe: 0.00 0146 Decyl propionate No No safety concern USA: 0.95 Europe: 0.00 0147 cis-3- & trans-2- Hexenyl propionate Postponed, pending consideration USA: 430 Europe: 0.00 on alpha, beta-unsaturated carbonyl compounds2 0148 Isobutyl propionate No No safety concern USA: 6.5 Europe: 12 0149 Methyl butyrate No No safety concern USA: 44 Europe: 220 0150 Propyl butyrate No No safety concern USA: 38 Europe: 75 0151 Butyl butyrate No No safety concern USA: 63 Europe: 390 0152 n-Amyl butyrate No No safety concern USA: 200 Europe: 450 0153 Hexyl butyrate No No safety concern USA: 27 Europe: 110 0154 Heptyl butyrate No No safety concern USA: 3.8 Europe: 6.0 0155 Octyl butyrate No No safety concern USA: 0.38 Europe: 16 Table 1. Continued... No. Substance Step A3 Step A4 Comments Conclusion based Does intake exceed the Endogenous or on current levels human intake threshold?1 metabolized to of intake Intake estimates endogenous (µg/person per day) substances? 0156 Decyl butyrate No No safety concern USA: 0.08 Europe: 0.00 0157 cis-3-Hexenyl butyrate No No safety concern USA: 4.8 Europe: 160 0158 Isobutyl butyrate No No safety concern USA: 7.4 Europe: 47 0159 Methyl valerate No No safety concern USA: 11 Europe: 30 0160 Butyl valerate No No safety concern USA: 0.10 Europe: 3.7 0161 Propyl hexanoate No No safety concern USA: 0.17 Europe: 14 0162 Butyl hexanoate No No safety concern USA: 1.9 Europe: 15 0163 n-Amyl hexanoate No No safety concern USA: 8.8 Europe: 8.7 0164 Hexyl hexanoate No No safety concern USA: 13 Europe: 150 0165 cis-3-Hexenyl hexanoate No No safety concern USA: 1.3 Europe: 42 0166 Isobutyl hexanoate No No safety concern USA: 1.7 Europe: 6.1 0167 Methyl heptanoate No No safety concern USA: 0.10 Europe: 5.7 0168 Propyl heptanoate No No safety concern USA: 0.38 Europe: 0.14 0169 Butyl heptanoate No No safety concern USA: 4.4 Europe: 0.00 Table 1. Continued... No. Substance Step A3 Step A4 Comments Conclusion based Does intake exceed the Endogenous or on current levels human intake threshold?1 metabolized to of intake Intake estimates endogenous (µg/person per day) substances? 0170 n-Amyl heptanoate No No safety concern USA: 0.02 Europe: 0.61 0171 Octyl heptanoate No No safety concern USA: 0.38 Europe: 0.21 0172 Isobutyl heptanoate No No safety concern USA: 1.9 Europe: 0.01 0173 Methyl octanoate No No safety concern USA: 0.17 Europe: 9.7 0174 n-Amyl octanoate No No safety concern USA: 1.9 Europe: 3.4 0175 Hexyl octanoate No No safety concern USA: 0.95 Europe: 1.3 0176 Heptyl octanoate No No safety concern USA: 0.95 Europe: 0.71 0177 Octyl octanoate No No safety concern USA: 2.3 Europe: 0.03 0178 Nonyl octanoate No No safety concern USA: 0.95 Europe: 0.14 0179 Methyl nonanoate No No safety concern USA: 2.3 Europe: 0.86 0180 Methyl laurate No No safety concern USA: 0.76 Europe: 5.1 0181 Butyl laurate No No safety concern USA: 0.10 Europe: 0.00 0182 Isoamyl laurate No No safety concern USA: 0.57 Europe: 0.14 0183 Methyl myristate No No safety concern USA: 46 Europe: 62 0184 Butyl stearate No No safety concern USA: 5.5 Europe: 5.1 Table 1. Continued... 1 The human intake threshold for Class I is 1800 µg per day; 540 µg per day for Class II; and 90 µg per day for Class III 2 One of the predicted main metabolites of trans-2-hexenyl propionate is trans-2-hexenol which would be oxidized to the alpha,ß-unsaturated substance, trans-2-hexenal 1.2 Estimated daily per capita intake The total annual volume of the 67 esters in this group is approximately 19 tonnes in the USA and 65 tonnes in Europe. In the USA more than 70% of the total annual volume is accounted for by five substances, amyl butyrate, cis-3- & trans-2-hexenyl propionate, and the acetate esters of propyl alcohol, isobutyl alcohol and 2-methylbutyl alcohol. In Europe, more than 75% of the total annual volume is accounted for by seven substances, butyl butyrate, amyl butyrate and the acetate esters of methyl alcohol, butyl alcohol, hexyl alcohol, cis-3-hexenol and isobutyl alcohol. Based on the reported annual volumes in the USA and Europe, the total estimated daily per capita intakeof the 67 esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids used as flavouring agents is 3.8 mg per capita per day in the USA and 9.2 mg per capita per day in Europe. The use of 7 of the esters (heptyl formate, octyl propionate, decyl propionate, decyl butyrate, butyl heptanoate, butyl dodecanoate, cis-3- & trans-2-hexenyl propionate) has been reported in the USA but not in Europe. Esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids are principal components of alcoholic beverages and a wide variety of fruits. Quantitative data on the natural occurrence in food have been reported for 37 substances in the group. In the USA, it is indicated that intake of these substances from natural sources exceeds intake from their use as flavouring agents. 1.3 Absorption, metabolism and elimination In general, aliphatic linear and branched-chain esters of aliphatic linear saturated carboxylic acids are anticipated to be hydrolysed to their component alcohols and carboxylic acids. The metabolism of the saturated acids and alcohols is considered in the introduction to this chapter on flavouring agents. The three monounsaturated alcohols in this group of esters are all anticipated to be oxidized via their corresponding aldehydes to their carboxylic acids, which are then metabolized in the fatty acid ß- oxidation and other well-known metabolic pathways. 1.4 Application of the Procedure for the Safety Evaluation of Flavouring Agents The stepwise evaluations of the 67 esters of aliphatic acyclic primary alcohols and linear saturated aliphatic carboxylic acids used as flavouring substances are summarized in Table 1. Step 1. The assignment of the structural class is the first step in the sequence. All but one of the 67 esters of aliphatic acyclic primary alcohols and linear saturated aliphatic carboxylic acids were classified in structural Class I. 2-Ethylbutyl acetate contains a sterically hindered functional group and therefore is in Class II. Step 2. At this step evaluation of one substance, cis-3- and trans-2-hexenyl propionate, was postponed, pending consideration of alpha,ß-unsaturated carbonyl compounds. The available data indicate that the esters in this group would be hydrolysed in humans to their component alcohols and carboxylic acids. The aliphatic acyclic primary alcohols are oxidized to their corresponding carboxylic acids, which are either conjugated and excreted in the urine, or undergo ß-oxidation and cleavage. The aliphatic linear saturated carboxylic acids are endogenous in humans. At current levels of per capita intake these esters would not be expected to saturate the metabolic pathways. Therefore, the response to Step 2 for each of the remaining 66 esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids is "yes". Step A3. The human intake threshold for structural Class I is 1800 µg/person per day. Sixty-four (64) of the 65 Class I esters in this group have USA and European daily per capita intake levels less than 1800 µg/person per day (see Table 1). Only hexyl acetate has an intake greater than 1800 µg/person per day. 2-Ethylbutyl acetate is a Class II substance for which intake levels in the USA and Europe are below the intake threshold of 540 µg/person per day. Step A4. This step must be considered only for hexyl acetate, the only substance in this group with an estimated intake level that exceeds the Class I threshold. The component hexyl alcohol is oxidized to hexanoic acid which is endogenous as an intermediary metabolite in the fatty acid pathway and acetate is a component of the tricarboxylic acid cycle. In the opinion of the Committee the endogenous levels of these two metabolites would not give rise to perturbations outside the physiological range. Therefore, hexyl acetate was also determined to be of no safety concern based on its structural class and known metabolism. Based on results of the safety evaluation sequence, 66 esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids evaluated do not pose a safety concern when used at current levels of intake as flavouring agents. One substance, cis-3- & trans-2-hexenyl propionate was postponed, pending consideration on alpha,ß-unsaturated carbonyl compounds. 1.5 Consideration of combined intakes In the unlikely event that all foods containing all the 66 esters evaluated were consumed simultaneously the estimated daily per capita intake in the USA and Europe would exceed the human intake threshold for substances in class I. All the flavouring agents in this group of esters are expected to be metabolized via well known biochemical pathways to innocuous metabolic and/or endogenous substances and in the opinion of the Committee the endogenous levels of these metabolites would not give rise to perturbations outside the physiological range. Accordingly, even a combined theoretical intake would be of no safety concern. 1.6 Conclusions The Committee concluded that the substances in this group would not present safety concerns at the current levels of intake. No toxicity data were required for the application of the Procedure for this group of esters. The Committee noted that the available toxicity data were consistent with the results of the safety evaluation using the Procedure. 2. RELEVANT BACKGROUND INFORMATION 2.1 Explanation Ten linear saturated primary alcohols in a homologous series from C1 to C12 are components of 51 esters in this group of 67 esters (see Table 2). Seven esters contain four different aliphatic linear unsaturated primary alcohols, five of which include cis-3-hexen-1-ol. The remaining nine esters contain four different saturated branched-chain primary alcohols, six of which include isobutyl alcohol. Twelve aliphatic linear saturated carboxylic acids in a homologous series from C1 to C18 are acid components of the 67 esters. There is a significant amount of structural uniformity among the alcohol and carboxylic acid components of the 67 esters. In the USA, the esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids are generally used as flavouring substances up to average maximum levels of 200 mg/kg. Higher levels of use (up to 3000 mg/kg) are permitted in food categories such as chewing gum and hard candy. In Europe the upper use levels for these flavouring substances are generally 1 to 30 mg/kg foods and in special food categories like candy and alcoholic beverages up to 300 mg/kg foods (CE, 1992; SCF, 1995). 2.2 Intake data The annual volumes of the 67 esters of this group in Europe (IOFI, 1995) and in the USA (NAS, 1987) are given in Table 2. Table 2. Most recent reported annual usage in Europe and USA Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Propyl formate USA 2.0 0.38 0.01 Europe 35 5.0 0.08 Butyl formate USA 0.9 0.17 0.00 Europe 150 21 0.34 n-Amyl formate USA 570 110 1.8 Europe 200 29 0.48 Hexyl formate USA 42 8.0 0.13 Europe 61 8.7 0.15 Heptyl formate USA 0.5 0.10 0.00 Europe 0.0 0.00 0.00 Octyl formate USA 5.0 0.95 0.02 Europe 1.0 0.14 0.00 cis-3-Hexenyl formate USA 9.0 1.7 0.03 Europe 300 43 0.71 Isobutyl formate USA 8.0 1.5 0.03 Europe 33 4.7 0.08 Methyl acetate USA 600 110 1.9 Europe 3300 460 7.7 Propyl acetate USA 2300 440 7.4 Europe 1300 180 3.1 Butyl acetate USA 870 170 2.8 Europe 8400 1200 20 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Hexyl acetate USA 840 160 2.7 Europe 23000 3200 54 Heptyl acetate USA 12 2.3 0.04 Europe 390 56 0.93 Octyl acetate USA 50 9.5 0.16 Europe 590 83 1.4 Nonyl acetate USA 13 2.5 0.04 Europe 46 6.6 0.11 Decyl acetate USA 110 21 0.35 Europe 51 7.3 0.12 Lauryl acetate USA 3.0 0.57 0.01 Europe 65 9.3 0.15 cis-3-Hexenyl acetate USA 300 57 0.95 Europe 4500 640 11 trans-3-Heptenyl acetate USA 4.0 0.76 0.01 Europe 1.7 0.24 0.00 10-Undecen-1-yl acetate USA 0.5 0.10 0.00 Europe 5.8 0.83 0.01 Isobutyl acetate USA 6600 1300 21 Europe 8100 1200 19 2-Methylbutyl acetate USA 1900 360 6.0 Europe 900 130 2.1 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day 2-Ethylbutyl acetate USA 0.9 0.17 0.00 Europe 28 4.0 0.07 Methyl propionate USA 160 30 0.51 Europe 65 9.3 0.15 Propyl propionate USA 230 44 0.73 Europe 67 9.6 0.16 Butyl propionate USA 6.0 1.1 0.02 Europe 72 10 0.17 Hexyl propionate USA 16 3.0 0.05 Europe 40 5.7 0.10 Octyl propionate USA 0.1 0.02 0.00 Europe 0.0 0.00 0.00 Decyl propionate USA 5.0 0.95 0.02 Europe 0.0 0.00 0.00 cis-3- & trans-2- Hexenyl propionate USA 2300 430 7.2 Europe 0.0 0.00 0.00 Isobutyl propionate USA 34 6.5 0.11 Europe 86 12 0.20 Methyl butyrate USA 230 44 0.73 Europe 1500 220 3.6 Propyl butyrate USA 200 38 0.63 Europe 520 75 1.2 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Butyl butyrate USA 330 63 1.1 Europe 2700 390 6.5 n-Amyl butyrate USA 1000 200 3.3 Europe 3100 450 7.5 Hexyl butyrate USA 140 27 0.44 Europe 750 110 1.8 Heptyl butyrate USA 20 3.8 0.06 Europe 42 6.0 0.10 Octyl butyrate USA 2.0 0.38 0.01 Europe 112 16 0.27 Decyl butyrate USA 0.4 0.08 0.00 Europe 0.0 0.00 0.00 cis-3-Hexenyl butyrate USA 25 4.8 0.08 Europe 1100 160 2.7 Isobutyl butyrate USA 39 7.4 0.12 Europe 330 47 0.78 Methyl valerate USA 60 11 0.19 Europe 210 30 0.50 Butyl valerate USA 0.5 0.10 0.00 Europe 26 3.7 0.06 Propyl hexanoate USA 0.9 0.17 0.00 Europe 96 14 0.23 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Butyl hexanoate USA 10 1.9 0.03 Europe 100 15 0.24 n-Amyl hexanoate USA 46 8.8 0.15 Europe 61 8.7 0.15 Hexyl hexanoate USA 70 13 0.22 Europe 1000 150 2.4 cis-3-Hexenyl hexanoate USA 7.0 1.3 0.02 Europe 290 42 0.69 Isobutyl hexanoate USA 9.0 1.7 0.03 Europe 43 6.1 0.10 Methyl heptanoate USA 0.5 0.10 0.00 Europe 40 5.7 0.10 Propyl heptanoate USA 2.0 0.38 0.01 Europe 1.0 0.14 0.00 Butyl heptanoate USA 23 4.4 0.07 Europe 0.0 0.00 0.00 n-Amyl heptanoate USA 0.1 0.02 0.00 Europe 4.3 0.61 0.01 Octyl heptanoate USA 2.0 0.38 0.01 Europe 1.5 0.21 0.00 Isobutyl heptanoate USA 10 1.9 0.03 Europe 0.1 0.01 0.0002 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Methyl octanoate USA 0.9 0.17 0.003 Europe 68 9.7 0.16 n-Amyl octanoate USA 10 1.9 0.03 Europe 24 3.4 0.06 Hexyl octanoate USA 5.0 0.95 0.02 Europe 9.0 1.3 0.02 Heptyl octanoate USA 5.0 0.95 0.02 Europe 5.0 0.71 0.01 Octyl octanoate USA 12 2.3 0.04 Europe 0.2 0.03 0.00 Nonyl octanoate USA 5.0 0.95 0.02 Europe 1.0 0.14 0.00 Methyl nonanoate USA 12 2.3 0.04 Europe 6.0 0.86 0.01 Methyl laurate USA 4.0 0.76 0.01 Europe 36 5.1 0.09 Butyl laurate USA 0.5 0.10 0.00 Europe 0.0 0.00 0.00 Isoamyl laurate USA 3.0 0.57 0.01 Europe 1.0 0.14 0.00 Methyl myristate USA 240 46 0.76 Europe 440 62 1.0 Table 2. Continued... Substance Most recent Per capita intake2 annual volume1 (kg) µg/day µg/kg bw per day Butyl stearate USA 29 5.5 0.09 Europe 36 5.1 0.09 Total USA 20000 3800 63 Europe 65000 9200 150 1 USA: National Academy of Science (NAS, 1987) Evaluating the safety of food chemicals. Washington DC. Respondants to the annual NAS survey were requested to report annual poundages of < 1.0 lbs to two digits past the decimal point. Europe: International Organization of the Flavor Industry (IOFI; 1995) European inquiry on volume of use. Private communication to FEMA. 2 Intake calculated as follows: [[(annual volume, kg) x (1 x 109 µg/kg)]/[population x 0.6 x 365 days]], where population (10%, "eaters only") = 24 x 106 for the USA and 32 x 106 for Europe; 0.6 represents the assumption that only 60% of the flavor volume was reported in the survey (NAS, 1987; IOFI, 1995). Intake (µg/kg bw/d) calculated as follows: [(µg/d)/body weight], where body weight = 60 kg. Slight variations may occur from rounding off. 2.3 Biological data 2.3.1 Absorption and metabolism Generally, linear and branched-chain alkyl esters are hydrolysed to their component alcohols and carboxylic acids in the intestinal tract, blood and most tissues throughout the body, as described in the introduction to this chapter on flavouring agents. For this group of esters this is further supported by a series of in vitro hydrolysis studies on butyl acetate and structurally related esters as reported in Table 3. Following hydrolysis the component alcohols and carboxylic acids are metabolized as considered above (section 1.3) and in the introduction to this chapter on flavouring agents. Table 3. Hydrolysis data for esters of aliphatic acyclic primary alcohols with aliphatic linear saturated carboxylic acids Ester Artificial Artificial Rat liver Rat small % Hydrolysis % Hydrolysis gastric juice1 pancreatic preparation1 intestinal after 2 hours after 4 hours t0.5 (min) juice1 t0.5 (min) t0.5 (sec) mucosa1 t0.5 (sec) Butyl acetate 318 66.0 491 108 232, 723 412, 923 Ethyl acetate8 not reported not reported not reported not reported 1004 not reported Ethyl butyrate8 490 5.67 not reported not reported 152, 1005 not reported Ethyl hexanoate8 293 3.47 0.1 0.5 not reported not reported Ethyl heptanoate8 770 9.78 0.2 0.6 102, 1003 192 Ethyl nonanoate8 177 5.92 not reported not reported 372, 1005 612 Ethyl laurate8 640 6.10 not reported not reported 122, 1005 232 Ethyl decanoate8 not reported not reported not reported not reported 806,7 not reported Isopropyl butyrate8 not reported not reported not reported not reported 404,6 not reported Isoamyl acetate8 not reported not reported not reported not reported 206, 1004 not reported Isoamyl butyrate8 660 11.3 0.5 0.1 122, 1003 222 Isoamyl hexanoate8 146 37.8 not reported not reported not reported not reported Allyl hexanoate 1120 1.98 4.0 0.1 1007 not reported Citronellyl acetate not reported not reported not reported not reported 1007 not reported 1 Longland et al., 1977 2 In artificial gastric juice. Gangolli & Shilling, 1968 3 In artificial pancreatic juice. Gangolli & Shilling, 1968 4 In whole homogenate of pig jejunum. Grundschober, 1977 5 In artificial pancreatic juice after only 1 hour. Gangolli & Shilling, 1968 6 By pancreatin. Leegwater & van Straten, 1974 7 By pancreatin. Grundschober, 1977 8 Structurally related ester 2.3.2 Toxicological studies 2.3.2.1 Acute toxicity Oral acute toxicity studies have been reported for 51 of the 67 esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids. The very low oral acute toxicity of this group of esters is demonstrated by oral LD50 values greater than 1850 mg/kg bw (e.g., Smyth et al., 1954). 2.3.2.2 Short-term toxicity Results of short-term toxicity studies for 6 of the 67 esters and for some structurally related esters and selected hydrolysis products are summarized in Table 4. Available short-term toxicity studies on the esters and on some of their component alcohols are described in more detail below. a) Methyl octanoate Methyl octanoate was diluted in cotton-seed oil and incorporated into the diet of groups of 15 male and 15 female FDRL rats for 90 days. The dosage levels were 3.2 and 3.6 mg/kg bw per day for males and females, respectively. Observations included food consumption, body weight, haematology, blood chemical determinations, liver and kidney weights and histological examination. No treatment-related adverse effects were reported (Oser et al., 1965). b) Methyl butyrate, octanoate and dodecanoate In a limited 12-week study with only one dose level, groups of up to 10 male and up to 10 female USC strain-rats were given a daily oral dose of 100 mg methyl butyrate, methyl octanoate, methyl dodecanoate or the structurally-related esters methyl hexanoate, methyl decanoate and methyl tetradecanoate as part of a fat-free diet. The study was designed to evaluate the influence of aliphatic esters on endogenous levels of lipids and cholesterol in rats maintained on fat-free diets. A statistically significant decrease in weight gain occurred in males treated with methyl octanoate. A statistically significant increase was observed in the liver cholesterol level of males given methyl laurate, but was not accompanied by an increase in total plasma cholesterol when compared with controls. No microscopic examination was reported (Alfin-Slater et al., 1965). c) Amyl butyrate, and structurally-related ethyl esters Groups of 10 male and 10 female Osborne-Mendel rats were maintained on diets containing either amyl butyrate or the structurally related esters ethyl formate or ethyl pentanoate at concentrations of 1000, 2500 or 10 000 mg/kg (equivalent to 50, 250 or 500 mg/kg bw per day) for 16-17 weeks. Additionally, Table 4. Short-term toxicity studies for esters of aliphatic acyclic primary alcohols with aliphatic linear saturated carboxylic acids and structurally-related substances Substance Species, sex Route Time NOEL1 Reference (days) (mg/kg bw per day) Ethyl formate Rat, m & f Oral 119 >500 Hagan et al., 1967 Ethyl acetate2 Rat, m & f Oral 371-392 >43 Johannsen & Purchase, 1969 Butyl acetate Rat Oral 180 >0.5 Petrovskaya & Bul'bin, 1969 Octyl acetate Rat, m & f Gavage 91 weeks >10004 Daughtrey et al., 1989a Methyl butyrate Rat, m & f Oral 84 >3003,5 Alfin-Slater et al., 1965 Amyl butyrate Rat Oral 112 >500 Hagan et al., 1967 Ethyl pentanoate2 Rat, m & f Oral 119 >500 Hagan et al., 1967 Methyl hexanoate2 Rat, m & f Oral 84 >3003,5 Alfin-Slater et al., 1965 Ethyl heptanoate2 Rat, m & f Oral 90 >500 Hagan et al., 1967 Methyl octanoate Rat, m & f Oral 84 >300 Alfin-Slater et al., 1965 Methyl octanoate Rat, m & f Oral 90 >3.63 Oser et al., 1965 Ethyl nonanoate2 Rat, m & f Oral 112 >500 Hagan et al., 1967 Ethyl nonanoate2 Rat, m & f Oral 112 >10003 FDA, 1954 Methyl decanoate2 Rat, m & f Oral 84 >3003,5 Alfin-Slater et al., 1965 Methyl laurate Rat, m & f Oral 84 >3003,5 Alfin-Slater et al., 1965 Methyl myristate2 Rat, m & f Oral 84 >300 Alfin-Slater et al., 1965 Isobutyl isobutyrate2 Rats, m & f Gavage 126 >1000 Drake et al., 1978 3-Methylbutyl alcohol2 Rat, m & f Gavage 119 >1000 Carpanini et al., 1973 2-Methyl-1-propanol2 Rat, m & f Oral 90 >1450 BASF, 1992 Hexyl alcohol2 Rat, m & f Oral 90 5776 Eibert, 1992 cis-3-Hexenol2 Rat, m & f Oral 98 120-150 Gaunt et al., 1969 1 A NOEL reported in this table as "greater than" (>) indicates that no adverse effects were observed at the highest dose level in the study, and therefore an actual NOEL was not obtained. 2 A structurally related substance to the group 3 Only one dose level 4 Increased liver weights in high-dose (1000 mg/kg bw) and intermediate-dose (500 mg/kg bw) groups and mild nephropathy in the high-dose males were judged by the authors to be of minimal toxicological significance. 5 No histopathology reported 6 No statistical analysis of data 7 Only 2 males and 2 females per dose. ethyl heptanoate was tested at concentrations of 1000 and 10 000 mg/kg diet for 13 weeks, and ethyl nonanoate was tested for 16 weeks at 10 000 mg/kg diet in groups of 5 males and 5 females. There were no effects on growth or haematology in any of the groups, and no macroscopic abnormalities at any dose level. Microscopic examination was performed on tissues from the 10 000 mg/kg groups which revealed no changes (Hagan et al., 1967). d) Butyl acetate Butyl acetate was orally administered to 40 white rats at dose levels of 0, 0.005, 0.05 and 0.5 mg/kg bw per day for six months. Animals in the control group, and eight animals in the high-dose group underwent pathomorphological examination at the end of the study. No changes in the internal organs of the animals were reported (Petrovskaya & Bul'bin, 1969). e) Octyl acetate Groups of 20 male and 20 female Sprague-Dawley rats received undiluted octyl acetate by gavage at doses of 100, 500 or 1000 mg/kg bw per day, 5 days per week, for 13 weeks. Control rats received distilled water at a dose of 1000 mg/kg bw per day. After 45 days of dosing, five animals per group were sacrificed and necropsied. There were no statistically significant differences in mean haematology values between the test and control animals. Serum chemistry values showed no evidence of any treatment-related effects. Gross necropsy showed no indication of any significant treatment-related effects. After 13 weeks, the remaining animals were sacrificed and necropsied. Body weights were slightly lower for high-dose male and female rats as compared to controls, but were generally not statistically significant. This was therefore considered by the authors to be a borderline treatment-related effect. Similarly, mean food consumption values for high-dose males and females were slightly lower than controls but, in general, were not statistically significant. This finding paralleled the changes in body weight. In the high-dose group, there was an increase in the relative liver and kidney weights in males and females. An increase in the relative liver weight was also evident in the mid-dose group in both sexes. All other organ weights were normal. The increased liver weights of rats were not associated with liver pathology or hepatotoxicity as reflected by microscopic examination and serum enzyme parameters, respectively. The authors attributed the effect to a compensatory response of the liver to an increased metabolic load from the exogenous octyl acetate and not a reflection of true hepatotoxicity. This type of compensatory response to exogenous substances was reported previously by Golberg (Golberg, 1966). The increased liver weights in the high-dose and intermediate-dose animals were judged by the authors to be of minimal toxicological significance. Mild tubular nephropathy was reported in the kidneys of high-dose males only. The specific findings consisted of increased incidence of dilated renal tubules in the cortical-medullary zone, containing granular casts and regenerative hyper-plasia in proximal convoluted tubules. This effect has been observed with aliphatic hydrocarbons in male rats and has been found to be associated with a minimal change in kidney function (Alden et al., 1984; Halder et al., 1984; Phillips & Cockrell, 1984; Phillips & Egan, 1984a,b). Therefore, the finding of nephropathy in the high-dose group of male rats was not believed by the authors to have significant toxicological implications for humans (Daughtrey et al., 1989a). f) Hexyl alcohol Two groups of 10 male and 10 female rats were fed hexyl alcohol for 13 weeks at dietary levels of 0.25 or 0.50%; a third group was fed 1% for weeks 1-10 and 2%, 4% and 6% for weeks 11, 12 and 13, respectively. Decreased food consumption was observed in females at the high-dose level, but body weights for all animals were normal. No significant haematological changes or differences in urine analyses were observed for the test or control groups. Gross pathology and microscopic evaluation were performed and revealed no treatment-related effects. The 1% level was reported to be equivalent to an intake of 577 mg/kg bw per day (Eibert, 1992). Three groups of 2 male and 2 female pure bred beagle dogs were fed hexyl alcohol for 13 weeks at levels of 0.5%, 1% or 1000 mg/kg bw per day (high-dose group) via gelatin capsules. A fourth group of 4 males and 4 females served as controls. Body weight, organ weight and food consumption for the treated animals did not differ from controls. All animals in the high-dose group displayed gross signs of toxicity intermittently after treatment, including salivation, excitation, ataxia, tremors and anaesthesia. The animals generally returned to normal within 4 hours of treatment. One female dog in the high-dose group died on the first day of treatment and was replaced by another female. Three of the four remaining animals in the high-dose group died during the study. No signs of toxicity were observed in the other test animals. Haematology, serum chemistry and urinalysis showed no significant difference as compared to controls. Animals in the high-dose group exhibited gastrointestinal inflammation and congestion of other visceral organs. Some gastric irritation was observed in the mid-dose group. Both males treated at the 1000 mg/kg bw per day level exhibited significant testicular atrophy. Effects on the testes and other reproductive tissue have been observed with other aliphatic alcohols at high-dose levels (Lington & Bevan, 1994). A finding of nodules on the lung surface of some animals was reported to be non- treatment-related. The NOEL was 1% in the diet, equal to 230 to 695 mg/kg bw per day (Eibert, 1992). g) cis-3-Hexenol Groups of 15 male and 15 female weaning rats were given drinking-water containing 0, 310, 1250 or 5000 mg/litre cis-3-hexenol for 98 days. A statistically significant reduction in water intake was reported in male rats in the high-dose group only. Tissues from all rats in the high-dose group and from 50% of the controls were examined microscopically. Statistically significant increases in relative kidney and adrenal gland weights were observed in males only at the 5000 mg/litre level, but were not accompanied by any evidence of histopathology. No other treatment-related abnormalities were reported. The NOEL was 1250 mg/litre, which corresponds to an intake level of 150 mg/kg bw per day (Gaunt et al., 1969). h) 2-Methyl-1-propanol (isobutyl alcohol) Groups of 10 male and 10 female Wistar rats were given 2-methyl-1- propanol in their drinking-water for 3 months. The test substance was administered at concentrations of 0, 1000, 4000 or 16 000 mg/kg diet, which was reported to correspond to approximate dose levels of 0, 60, 340 or 1450 mg/kg bw per day. Food and drinking-water consumption, body weight gain, haematology and clinical chemistry parameters revealed no treatment-related adverse effects. Gross pathology and histopathological examinations were normal. The authors concluded that results of this study demonstrated a lack of toxicity associated with administra-tion of 2- methyl-1-propanol in the drinking-water of rats, and that the NOEL was 1450 mg/kg bw per day the top dose (BASF, 1992). i) 3-Methylbutyl alcohol (isoamyl alcohol) 3-Methylbutyl alcohol was administered to groups of 15 male and 15 female Ash/CSE rats in corn oil by gavage, providing daily dose levels of 0, 150, 500 or 1000 mg/kg bw per day for 17 weeks. Examination of haematology, serum analyses, urinalysis, renal concentration tests and organ weights revealed no treatment-related effects. The animals were examined for macroscopic abnormalities, and the major organs were weighed. Microscopic examination was performed on the major organs and several tissues of the control and high-dose animals. No treatment- related abnormalities were observed (Carpanini et al., 1973). 2.3.2.3 Long-term toxicity Butyl stearate was administered to groups of 16 male rats at dietary concentrations of 0.01, 0.05, 0.25, 1.25 or 6.25% for 2 years. Two additional groups of male rats were fed a control diet. No adverse effects on growth or survival were observed. Haematology studies did not reveal any significant changes. At the end of one year, necropsies were performed on 3 animals from each group and revealed no treatment-related effects. Gross pathology and detailed histopathology studies on the control groups, and animals in the 1.25 and 6.25% groups (equivalent to 625 and 3125 mg/kg bw per day) revealed no treatment-related effects (Smith, 1953). 2.3.2.4 Genotoxicity Genotoxicity studies have been performed in vitro using the following esters of aliphatic acyclic primary alcohols and aliphatic linear saturated carboxylic acids: methyl acetate, butyl acetate, butyl stearate and the structurally related isoamyl formate (Table 5) and demonstrates that these substances are not genotoxic. Blood samples from male Swedish industrial workers, 13 of whom were exposed to butyl acetate at a median concentration of 12 mg/m3 and 8 of whom were exposed to methyl acetate at a median concentration of 14 mg/m3, were cultured for 72 hours and examined for sister chromatid exchanges (SCE). There was no difference in the frequencies of SCE between the exposed group and the matched reference group (Haglung et al., 1980). 2.3.2.5 Reproductive toxicity a) Butyl acetate In a limited reproductive toxicity study, 48 adult white rats were given a 0.1 ml "oil"solution containing 2 mg butyl acetate by gavage on alternating days for 8 months. The animals were given total doses of 24, 84 and 208 mg prior to the first, second and third generations, respectively. The first offspring also received 15 mg before mating. The administration of butyl acetate produced no statistically significant changes on the number of pregnant females, the number of born offspring, the number of viable offspring, the birth weight of the offspring, or the weight of the offspring after 7 and 21 days (Sporn et al., 1963). b) Butyl stearate Groups of 20 male and 20 female rats received diets providing 6.25% butyl stearate (equivalent to 3125 mg/kg bw per day) for 10 weeks prior to mating. A group of 12 male and 12 female rats of the same age were fed a control diet for 10 weeks prior to mating. No adverse effects on fertility, litter size or survival of offspring were observed, but significantly reduced growth during preweaning and postweaning periods was reported. Litters were weaned 21 days post-partum, and their weights determined. Twenty-four male and 24 female weanlings from each group were fed the test diet for 12 days. After 21 days, the rats were sacrificed and necropsied. No gross pathological changes were reported (Smith, 1953). 2.3.2.6 Developmental toxicity Octyl acetate In a teratogenicity study, groups of pregnant Sprague-Dawley rats were given octyl acetate by gavage on gestation days 6-15 providing dose levels of 0, 100, 500 or 1000 mg/kg bw per day. Statistically significant reductions in body weight gain and food consumption were observed in dams in the mid- and high-dose groups. No statistically significant effects on embryo-fetal lethality or fetal growth were observed for any treatment group. In the high-dose group only, the incidence of litters with at least one malformed fetus and the mean percentage of the litter malformed was significantly elevated (P<0.05). These observations occurred only at a dose level that was maternally toxic. The results demonstrate that octyl acetate does not exhibit developmental toxicity in rats under the study conditions (Daughtrey et al., 1989b). Table 5. Mutagenicity/genotoxicity studies for esters of saturated aliphatic acyclic primary alcohols with linear aliphatic acyclic acids Substance name Test system Test object Concentration of Results Reference in vitro substance Isoamyl formate Rec assay B. subtilis up to 18 µg/disk Negative Oda et al., 1978 Rec assay B. subtilis 20 µl/disk in DMSO Negative1 Yoo, 1986 Chromosomal aberration Chinese hamster fibroblast up to 2 mg/ml in DMSO Negative2 Ishidate et al., 1984 test cells Ames test S. typhimurium TA92, TA1535, up to 10 mg/plate in DMSO Negative1 Ishidate et al., 1984 TA100, TA1537, TA94, TA98, TA2637 Methyl acetate Ames test S. typhimurium TA97, TA98, TA102, TA104, TA1535,TA1538 up to 10 mg/plate Negative1 Zeiger et al., 1992 Butyl acetate Chromosomal aberration Chinese hamster fibroblast test cells 2 mg/ml in DMSO Negative2 Ishidate et al., 1984 Ames test S. typhimurium TA97, TA98, TA102, TA104, TA1535,TA1538 up to 10 mg/plate in DMSO Negative1 Zeiger et al., 1992 Ames test S. typhimurium TA92, TA94, up to 10 mg/plate in DMSO Negative1 Ishidate et al., 1984 TA98, TA100, TA153,TA1535, TA2637 Modified Ames test S. typhimurium TA98, TA100, 1-5000 µg/plate Negative1 Shimizu et al., 1985 TA1535,TA1537, TA1538 E. coli WP2 uvrA Butyl stearate Reversion assay TA 97, TA98, TA100, TA102, 100-5000 µg/plate in Negative1 Hachiya, 1987 TA1537, WP2/pKM102 acetone with Tween 80 1 Both with and without S-9 activation 2 Without S-9 activation 3. 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See Also: Toxicological Abbreviations