PESTICIDE RESIDUES IN FOOD - 1982 Sponsored jointly by FAO and WHO EVALUATIONS 1982 Data and recommendations of the joint meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues Rome, 23 November - 2 December 1982 Food and Agriculture Organization of the United Nations Rome 1983 PERMETHRINExplanation Permethrin was evaluated at the 1979, 1980 and 1981 Meetings (FAO/WHO 1980, 1981 and 1982).1 Desirable information left outstanding from the 1981 re-evaluation included results of studies from residues in lettuce following approved use patterns. The 1982 CCPR asked the JMPR to reconsider the recommendation of 20 mg/kg for the maximum residue level (MRL) of permethrin on lettuce. These results are now available as well as new data on residues permitting a first review of permethrin on several crops for which no MRL recommendation has been made. RESIDUES IN FOOD AND THEIR EVALUATION USE PATTERN Preharvest Almonds - Permethrin has been used in California for the control of the navel orange-worm, Amyelois transitella. It is effective when sprayed "high-volume" at 0.1 lb a.i./100 US gallons/acre, yielding a treatment rate of 0.33-0.44 kg a.i./ha. "Low volume" applications of 0.44 kg a.i./ha are also effective, i.e. in 200-500 l water/ha by ground application or in 50-100 l water/ha by aerial application. Up to five applications per season may be necessary. Asparagus - At rates of 0.05-0.1 kg a.i./ha, permethrin is effective against a complex of cutworms, Agrotis spp., and against the asparagus beetle, Crioceris asparagi. Repeat applications may be necessary every 5-7 days. 1 See Annex 2 for FAO and WHO documentation. Horseradish - Permethrin is effective when used as a root dip before transplanting (at 0.1% a.i,) and as a subsequent spray at 0.1-0.2 kg a.i./ha. The principal pest controlled is diamond back moth, Plutella maculipennis, against which several sprays may be needed. A preharvest withholding interval of several weeks can usually be observed. Grapes - In canada, multiple spray applications are used at rates up to 0.15 kg a.i./ha (0.6 kg Ambush 25WP/ha or 0.25 kg Ambush 25WP/1000 l) to within 21 days of harvest for control of grape berry moth and leafhopper. Olives - Permethrin is effective against olive moth, Prays olea, and olive fly, Dacus oleae. The former is an early season pest, occurring before fruit formation. The latter is a later season pest and applications to control this pest are most likely to influence the permethrin residue levels found in the olives. Sunflower seed - At 0.05-0.1 kg a.i./ha, permethrin is effective against cutworms, (Agrotis spp., Euxoa spp. and Spodoptera spp.) and against the sunflower seed weevil, Desmoris constrictus. The higher rate of 0.1-0.2 kg a.i./ha is required against the sunflower head moth, Homoeosoma electellum. Several applications per season may be necessary for control of this pest complex. A preharvest withholding interval of four weeks can usually be observed. RESIDUES RESULTING FROM SUPERVISED TRIALS Preharvest Almonds - Data are available from a total of eleven residue trials conducted in California, U.S in the period 1979-81. The trials encompassed both ground and aerial applications. Permethrin was applied at a standard rate of 0.1 lb/100 US gallons of spray at 300-400 US gallons of spray/acre during ground applications, or at 0.4 lb a.i./acre (0,44 kg a.i./ha) during aerial applications. Permethrin levels in the nuts harvested during the three weeks following the last application were normally below 0.05 mg/kg, except in one trial, in which levels up to 0.38 mg/kg were recorded, but where the possibility of contamination cannot be excluded (Table 1) (Pearson 1982; Ussary 1980a, 1981a). Asparagus - Four residue trials were conducted in 1979-81 in three separate areas of the U.S., in which a 24% EC formulation was applied by ground equipment at 0.11 or 0.22 kg a.i./ha on up to six occasions. Asparagus spears were harvested 1-3 days later. Permethrin levels in these spears were consistently below 1 mg/kg (Table 2) (Fitzpatrick 1982a; Ussary 1980b). Table 1. Permethrin Residues in Almond Nuts, U.S., 1979-81 Interval between Application Spray last application Permethrin residue levels Rate Volume Number of How and harvest (mg/kg) in nuts 1 (kg a.i./ha) (l water/ha) Applications Applied (days) 0.39 3150 3 Ground 27 0.02 0.39 3150 2 Ground 44 0.07 0.39 3150 1 Ground 99 0.02 0.44 3600 3 Ground 0 0.07 0.44 3600 3 Ground 7 0.04 0.44 3600 3 Ground 14 0.04 0.44 3600 3 Ground 21 0.04 0.44 3600 3 Ground 0 0.38 0.44 3600 3 Ground 8 0.08 0.44 3600 3 Ground 14 0.09 0.44 3600 3 Ground 21 0.13 0.44 3600 2 Ground 6 0.24 0.44 3600 2 Ground 14 0.25 0.44 270 2 Aerial 7 <0.05 0.44 270 2 Aerial 14 <0.05 0.44 450 5 Ground 7 0.02 0.44 3600 5 Ground 7 0.01 0.44 3600 5 Ground 0 0.03 0.44 3600 5 Ground 1 0.02 0.44 3600 5 Ground 4 0.01 0.44 3600 5 Ground 8 0.02 0.44 3600 5 Ground 15 0.01 0.44 3600 5 Ground 22 <0.01 Table 1. (con't) Interval between Application Spray last application Permethrin residue levels Rate Volume Number of How and harvest (mg/kg) in nuts 1 (kg a.i./ha) (l water/ha) Applications Applied (days) 0.44 2700 5 Ground 8 <0.01 0.33 2700 5 Ground 7 0.01 0.33 2700 5 Ground 12 0.05 0.44 270 6 Aerial 7 0.01 0.44 270 5 Aerial 6 0.01 1 24% EC formulation used. All results corrected for % recovery. Table 2. Permethrin Residues on Asparagus, U.S. Interval between Residues of Location and Rate of Spray volume Number of last application permethrin 1 Year application (l water/ha) applications and harvest [days) (mg/kg) (kg a.i./ha) Michigan 0.11 180 4 3 0.44 1979 California 0.22 230 1 1 0.11 1981 3 0.06 6 1 0.82 3 0.21 Michigan 0.22 270 4 1 0.43 1981 3 0.05 Washington 0.22 650 1 1 0.61 State 3 0.10 1981 2 1 0.69 3 0.11 6 1 0.32 3 0.14 1 24% EC formulation used. Results corrected for % recovery. Horseradish - Seven trials were conducted in the U.S. in 1979, in which roots were dipped in a 0.1% a.i. emulsion for 30 minutes 4-17 days before transplanting. Three foliar sprays of 0.22 kg a.i./ha were applied subsequently. In all cases, a 24% EC formulation was used. The resulting permethrin levels in the roots were consistently below 0.5 mg/kg (Table 3) (Ussary 1981b). Leeks - Data resulting from trials on leeks in the Netherlands were reviewed by the 1979 Meeting. Permethrin was applied "high volume" at 0.005% either once or twice. Residue levels in leeks harvested 6-7 days after the last application were in the range of up to 0.31 mg/kg, with a mean of eight results of 0.12 mg/kg. At the time, the 1979 Meeting also took note of permethrin residue levels in spring onions in deciding that an MRL value of 5 mg/kg would be appropriate. The 1982 Meeting of the Codex Committee on Pesticide Residues requested that the Joint Meeting re-examine the data. No new residue information is available for review. The available data on leeks taken in isolation show values consistently below 0.5 mg/kg. Lettuce - Considerable data were available for review by the 1979 Meeting from trials in Germany, Netherlands, U.K. and U.S. Further data are now available from trials in Denmark, U.K. and U.S., yielding a total of more than 400 pieces of individual data in all. The total available data are summarized in Table 4 (Fujie 1976,1979; Swaine and Sapiets 1979a, b; Swaine et al 1980a, b, c, 1981; Ussary 1975-77, 1978, 1980c). Additional data from trials in U.S. are given more fully in Tables 5 and 6. Grapes - At the 1982 CCPR, the Canadian delegation noted that the proposal of 1 mg/kg was not adequate to cover the use of permethrin on grapes in Canada. Residue data from use pattern applications in trials in five sites in Canada confirmed that residues up to 2 mg/kg can occur (Table 7). Olives - Two trials were conducted in Spain in 1976. Permethrin was applied three time at a rate of 0.25 or 0.5 g a.i./tree on each occasion. These rates are equivalent to approximately 0.025 and 0.05 kg a.i./ha. Olives were harvested immediately before the last application and then during the following three weeks. Permethrin levels in olives declined relatively slowly. However, the values were consistently below 1 mg/kg (Table 8) (Burke and Hulm 1979). Sunflower seed - A 24% EC formulation was used in 12 trials in the U.S, in 1978-80. Applications were by air in eight of the trials and by ground in the other four. Samples of mature seeds were harvested 13-44 days after last application when permethrin levels were below 1 mg/kg in all but one instance (1.6 mg/kg) (Table 9) (Fitzpatrick 1982b; Ussary 1982b). Table 3. Permethrin Residues in Horseradish Roots, U.S., 1981 Lowest Highest Rate of Interval between residue residue Mean application 1 Number of last spraying and determined determined residue (kg a.i./ha) applications harvest (days) (mg/kg) (mg/kg) (mg/kg) 4 0.22 2 3 23-26 0.073 0.31 0.29 (3) 3 34 <0.01 0.15 0.056 (3) 3 40 - - 0.074 (1) 0.44 3 3 23 - _ 0.45 (1) 1 24% EC formulation used. 2 The horseradish sets were dipped for 30 minutes in a 0.1% emulsion of permethrin 4-17 days before planting. 3 The horseradish sets were dipped for 30 minutes in a 0.2% emulsion of permethrin 7 days before planting. 4 All results corrected for % recovery. Figures in parentheses are the numbers of results upon which the means are based. Table 4. Permethrin Residues on Lettuce Spray Interval Lowest Highest Country and Formulations Rate of volume Number of between last residue residue Mean Year used application (l water/ applications spraying and determined determined residue (kg a.i./ha) ha) harvest (days) (mg/kg) (mg/kg) (mg/kg) 1 Denmark 25% EC 0.15 1 1 6.8 (1) 1980 3 7.9 (1) (indoor) 5 6.7 (1) 7 6.7 (1) 14 4.5 (1) 0.375 1 1 14 (1) 3 11 (1) 5 9.7 (1) 7 6.7 (1) 14 6.3 (1) Germany 25% EC 0.03 600 3 0 0.58 1.4 0.88 (3) 1977 1 0.84 1.9 1.3 (3) (outdoor) 4 0.42 1.8 0.98 (3) 7 0.22 0.45 0.35 (3) 10 0.19 0.28 0.24 (3) 14 0.03 0.08 0.06 (2) Holland 25% EC 0.05-0.075 1000-1500 1 0 3.8 4.4 4.1 (3) 1977 7 1.9 2.8 2.0 (3) (indoor) 17 1.1 1.6 1.3 (3) 21-22 <0.01 1.5 0.66 (11) 28 0.31 0.45 0.39 (3) 35 0.17 0.20 0.18 (3) Table 4. (con't) Spray Interval Lowest Highest Country and Formulations Rate of volume Number of between last residue residue Mean Year used application (l water/ applications spraying and determined determined residue (kg a.i./ha) ha) harvest (days) (mg/kg) (mg/kg) (mg/kg) 1 UK 1.25% EC 0.10-0.12 2500-300 1 0-3 0.26 4.3 2.1 (5) 1978 0.22-0.24 " 1 0-3 0.80 5.4 3.6 (5) (outdoor) UK 25% EC 0.05 520 1 0 2.5 (1) 1979 1 3.3 (1) (indoor.) 0.10 520 1 0 2.3 (1) 1 3.3 (1) UK 25% EC 0.05 700 2 0 0.27 1.3 0.68 (5) 1980 1 0.03 0.90 0.50 (4) (outdoor) 3 0.01 0.54 0.39 (4) 7 0.01 0.32 0.14 (4) 0.10 700 2 0 0.22 2.8 1.5 (5) 1 0.36 5.1 2.0 (4) 3 0.11 1.8 0.84 (4) 7 0.01 1.2 0.52 (4) 1.25% EC 0.05 1250 2 0 0.20 1.4 0.54 (5) 1 0.13 1.8 0.62 (4) 3 0.01 1.4 0.51 (4) 7 0.01 0.23 0.12 (4) 0.10 1250 2 0 0.34 1.9 0.95 (5) 1 0.05 3.1 0.98 (4) 3 0.01 1.4 0.51 (4) 7 0.01 0.90 0.38 (4) Table 4. (con't) Spray Interval Lowest Highest Country and Formulations Rate of volume Number of between last residue residue Mean Year used application (l water/ applications spraying and determined determined residue (kg a.i./ha) ha) harvest (days) (mg/kg) (mg/kg) (mg/kg) 1 UK 25% EC 0.05 1 0 0.77 (1) 1980 3 0.35 (1) 7 0.18 (1) 0.10 1 0 0.90 (1) 3 0.66 (1) 7 0.40 (1) USA 25% EC 0.05 160-560 2-6 1 0.14 0.18 0.16 (3) 1975-9 40% EC for ground 3 0.02 0.22 0.12 (5) (outdoor) spraying 7 <0.01 0.13 0.06 (5) or 13-14 <0.01 0.04 0.02 (5) 27-90 0.150-140 2 during 2-10 0-1 <0.01 5.7 0.77 (21) aerial 3-4 <0.01 3.5 0.55 (14) spraying 7 <0.01 1.2 0.24 (15) 0-14 <0.01 0.25 0.06 (8) 210-280 2 2-15 0-1 0.10 17 3.5 (64) 2-4 0.06 16 3.8 (47) 5-7 <0.01 6.8 1.5 (25) 13-14 <0.01 0.36 0.15 (10) 1 Figures in parentheses are the numbers of results upon which the means are based. All results are corrected for % recovery. 2 Indicates effective use rates. Table 5. Permethrin Residues in Lettuce, U.S. Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes California 24% EC 2 540 3 0.15 0.26 1976 7 <0.02 0.04 New York 24% EC 2 450 1 0.44 0.91 1975 3 0.33 1.1 6 0.28 0.61 8 0.36 0.19 Arizona 24% EC 6 270 0 0.25 1975 1 0.18 3 0.19 0.47 0.06 7 0.13 0.25 0.54 Trimmed 14 0.02 0.06 0.08 heads California 24% E C 2 450 1 0.69 1975 3 0.07 0.03 0.27 7 <0.01 0.02 0.08 13 <0.01 <0.01 <0.01 California 24% EC 8 270 1 0.04,0.04 0.19 1976 3 0.07,0.10 0.46 7 0.03,0.06 0.10 Table 5. (con't) Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes California 24% EC 4 450 0 0.36 1975 1 0.18 0.53 0.73 3 0.02 0.02 0.06 7 0.04 0.15 0.07 14 0.04 0.25 0.33 Arizona 24% EC 6 510 0 0.38 3 1976 1 0.15 2 0.46 3 7 0.17 2 0.26 3 Trimmed 14 0.03 2 0.12 3 heads California 24% EC 2 270 0 0.46 1976 and 1 0.13 0.13 540 3 0.02 0.15 7 0.04 0.02 14 <0.01 0.02 Arizona 24% EC 4 270 1 0.16 0.33 0.48 1976 3 0.09 0.23 0.27 7 0.07 0.14 0.22 14 0.02 0.04 0.07 Arizona 24 % EC 3 270 1 0.14 0.45 0.71 1975 3 0.22 0.29 0.50 7 0.05 0.19 0.34 14 0.02 0.12 0.35 Table 5. (con't) Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes California 24% EC 9 270 0 0.11 1976 1 0.10 0.34 4 <0.05 0.24 7 <0.05 0.15 10 <0.05 0.21 Arizona 24% EC 10 160 0 0.20 0.39 1977 1 0.30 0.38 3 0.20 0.24 Trimmed 7 0.20 0.36 heads California 24% EC 5 190 0 <0.05 1977 1 <0.05 3 <0.05 7 <0.05 Texas 24% EC 4 70 0 <0.05 1977 1 <0.05 3 <0.05 7 <0.05 Arizona 24% EC 9 60 0 0.30 1977 1 0.10 3 0.30 7 nd Table 5. (con't) Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes Arizona 24% EC 10 225 1 3.9 1978 Arizona 24% EC 10 225 1 6.2 1978 California 24% EC 8 270 1 0.55 1978 Arizona 24% EC 10 90 0 8.7 1979 3 8.0 7 6.8 California 24% EC 8 180 1 1.5 - Untrimmed 1979 heads California 24% EC 10 90 0 2.4 1979 3 0.66 7 0.92 24%EC 12 90 0 1.3 3 1.5 7 1.0 California 24% EC 10 270 1 4.4 1979 and 560 Table 5. (con't) Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes California 24% EC 9 180 1 2.1 1979 California 24% EC 8 560 1 3.3 1979 Florida 24% EC 11 270 1 1.3 3.3 1978 New York 24% EC 10 90 1 1.9 1979 Arizona 40% EC 15 45 0 8.6,10, 1978 11, 11 Arizona 40% EC 15 90 0 15, 17 1978 3 16, 16 California 40% EC 15 90 0 1.3,1.5 1978 3 1.1,0.79 California 40% EC 15 320 0 14,9.7 1978 3 11,8.8 California 40% EC 15 45 0 1.7,2.2 1979 3 0.33,0.40 California 40% EC 15 135 0 8.1,5.8 1978 3 5.3,7.0 Table 5. (con't) Interval from Spray last application Permethrin residue (mg/kg) 1 Location Number of volume to and year Formulation applications (l water/ha) harvest (days) 0.5-0.55 kg/ha 0.1-0.11 kg/ha 0.2-0.22kg/ha Notes California 40% EC 15 320 0 5.2,6.4 1978 3 4.7,3.8 California 40% EC 15 150 0 5.1,6.7 1978 3 3.4,3.0 Arizona 40% EC 15 270 0 6.5,9.9 Untrimmed 1976 3 7.2,7.0 heads California 40% EC 15 230 0 4.9,12 1976 3 8.3,6.4 Arizona 40% EC 15 320 0 1.7,2.3 1976 3 2.6,2.1 1 Results corrected for % recovery. 2 0.14 kg a.i./ha rate. 3 0.28 kg a.i./ha rate. Table 6. Permethrin Residues in Lettuce, U.S. Rate of Interval between Permethrin residues (mg/kg) in application last application (g a.i./ha) and harvest (days) Wrapper Leaves Trimmed Heads 200 3 10 0.27 7 9.0 0.22 14 5.4 0.07 275 7 4.5 0.26 14 3.1 0.12 200 1 47 0.71 3 9.2 0.50 7 9.6 0.34 14 6.3 0.35 200 1 31 0.19 3 21 0.46 7 19 0.10 200 1 13 0.73 3 8.8 0.06 7 6.8 0.07 14 8.3 0.33 200 1 11 0.69 3 18 0.27 7 8.9 0.08 13 2.8 <0.01 220 0 6.2 0.39 1 5.4 0.38 3 4.9 0.24 7 4.6 0.36 110 1 3.0 0.30 110 0 3.9 <0.01 1 3.6 <0.01 3 2.7 <0.01 Table 6. (con't) Rate of Interval between Permethrin residues (mg/kg) in application last application (g a.i./ha) and harvest (days) Wrapper Leaves Trimmed Heads 110 0 2.5 <0.01 1 2.7 <0.01 3 2.3 <0.01 7 1.2 <0.01 220 1 5.5 0.10 3 3.8 0.30 Other crops - Data from Finland (Table 10) on oilseed rape, tomato, cucumber and currants confirmed the estimates of maximum residue levels for these crops. It was noted however, that residues on currants could exceed the limit under discussion by the Codex Committee. FATE OF RESIDUES On Processing and Cooking Data on the fate of residues on processing of sunflower seeds are from a trial in the U.S. in which a sunflower field was treated aerially five times with permethrin at the rate of 0.22 kg a.i./ha. The seeds were harvested for processing into hulls, solvent extracted meal and crude oil. The crude oil was further processed into refined, bleached, deodorized oil, soapstock and deodorizer distillates. These commodities were analysed for residues of permethrin (Table 11). Residues in hulls were only marginally higher than residues in whole seed, and residues in crude oil are somewhat lower. Refining further reduced the level of residues in oil (Ussary 1982). Data on the effects of washing are from a study in the UK in which lettuce was sprayed with a 25% EC formulation of permethrin at 0.1 kg a.i./ha. Heads of lettuce harvested three days later were quartered, the opposite quarters being bulked; half of the lettuce remained unwashed whereas the other half was washed with cold water before analysis. Residue analysis for permthrin demonstrated that the effect of washing was to reduce the mean of a three-day old weathered residue from 0.66 mg/kg to 0.24 mg/kg, i.e. to less than 50% (Swaine et al 1980a). Table 7. Permethrin Residues in Grapes, Canada Application Rate Interval Residues (mg/kg) 1 Location (kg a.i./ha) No. Formulation (days) cis trans total Stoney Creek, Ontario 0.07 5 25 WP 21 0.04 0.29 34 0.16 0.26 0.42 40 0.22 0.29 0.51 6 34 0.12 0.14 0.26 0.14 0.17 0.31 7 0 1.88;2.90 1 1.93;1.90 3 2.99;1.90 5 1.92;1.20 7 0.70;1.30 14 0.78;0.97 21 1.15;0.34 0.10 7 25 WP 0 1.98;1.87 1 2.28;2.90 3 3.03;2.00 5 2.37;1.20 7 1.65;1.33 14 1.67;1.14 21 1.18;0.97 Table 7. (con't) Application Rate Interval Residues (mg/kg) 1 Location (kg a.i./ha) No. Formulation (days) cis trans total Stoney Creek, Ontario 0.14 5 25 WP 21 0.10 0.59 28 0.09 0.45 34 0.61 0.83 1.44 40 0.36 0.44 0.08 6 34 0.17 0.21 0.38 0.31 0.32 0.63 7 0 2.17;3.90 1 2.15;3.92 3 3.90;0.99 5 2.77;1.22 7 1.98;1.35 14 1.96;1.92 21 1.98;1.18 Untreated <0.01-0.05 Vineland, Ontario 0.14 1 25 WP 0 0.92 1 0.49 3 0.41 7 0.13 14 0.13 21 0.17 Untreated 0.01 Table 7. (con't) Application Rate Interval Residues (mg/kg) 1 Location (kg a.i./ha) No. Formulation (days) cis trans total Jordan, Ontario 0.14 1 25WP 7 0.6 14 0.5 21 0.38 Untreated 0.06-0.08 Oliver, British Columbia 0.20 1 25 WP 35 0.41 untreated <0.01 Summerland, British Columbia 0.20 1 25 WP 38 0.36 59 0.25 untreated <0.01 1 Residue levels were corrected for recovery. Table 8 Permethrin Residues in Olives, Spain, 1976 1 Application Interval between Lowest Highest Mean rate 2 Number of last spraying residue residue residue (g a.i./tree) applications and harvest determined determined (mg/kg) (days) (mg/kg) (mg/lg) 0.25 2 (1 hour before 0.28(1) final spray) 3 0 0.26 0.61 0.44(2) 3 0.25(1) 7 0.16 0.26 0.21(2) 14 0.25 0.42 0.34(2) 21 0.19 0.30 0.25(2) 0.5 2 (1 hour before 0.66(1) final spray) 3 0 0.51 0.72 0.62(2) 3 0.59(1) 7 0.46 0.63 0.55(2) 14 0.46 0.71 0.59(2) 21 0.46 0.63 0.55(2) 1 All results are corrected for % recovery. Figures in parentheses are numbers of results on which means are based. 2 25% EC formulation used. Data on the fate of permethrin residues on cooking are from a study in which apples and tomatoes (whole commodity) were accurately fortified with permethrin at 1 mg/kg and 0.1 mg/kg respectively. Triplicate samples of each crop were analysed for residues of permethrin both before and after cooking. For apples, the cooking process involved baking the whole fruit for 45 minutes at 165°C. For tomatoes, it involved frying the sliced commodity for 2-3 minutes in a small amount of vegetable oil. Both the tomato and oil were recovered for analysis. Residues of permethrin on apples and tomatoes, as individual cis and trans isomers before and after cooking, are shown in Tables 12 and 13. Results indicate that permethrin levels do not alter during baking or frying. The ratios of the cis and trans isomers remained essentially constant during the apple baking. The measured residues on fried tomatoes indicate a very small isomer ratio change towards cis enrichment, which is not significant (Swaine and Rippington 1982). Table 9. Permethrin Residues in Sunflower Seeds, U.S., 1978-80 1 Spray Interval between Method of Application volume Number of last application Permethrin Location application rate (l water/ applications and harvest residues (kg a.i./ha) ha) (days) (mg/kg) Colorado ground 0.11 230 2 13 <0.05 0.22 230 <0.05 South Dakota aerial 0.11 4 28 <0.05 Texas aerial 0.22 18 4 25 1.6 Minnesota aerial 0.22 4 28 0.02 Minnesota aerial 0.22 4 28 0.95 Texas aerial 0.11 18 5 20 0.31 Texas ground 0.11 36 2 28 0.56 0.22 36 0.56 North Dakota aerial 0.11 45 3 46 <0.05 Texas aerial 0.11 18 2 43 0.24 Colorado ground 0.11 180 1 44 <0.05 0.22 180 <0.05 Colorado aerial 0.11 45 2 44 <0.05 0.22 45 <0.05 Nebraska aerial 0.22 27 5 28 0.58 1 Results are corrected for % recovery. 24% EC formulation used. Table 10 Permethrin Residues in Crops, Finland Application Interval from Interval from rate last application last application Residue Crop (a.i.) to harvest (days) to analysis (days) (mg/kg) Oilseed rape 0.25 kg/ha 89 149 seeds nd 0.1 (sprayed) Oilseed rape 0.15 kg/ha 87 215 seeds nd 0.1 (sprayed) Tomato 13 mg/plant 4 4 0.4 (sprayed) (plastic greenhouse) " " 7 7 0.5 Cucumber " 4 4 0.1 Black currant 0.07 g/bush 29 30 2.7 (sprayed) " " 14 14 4.3 " " 7 7 3.2 Red currant 0.18 g/bush 29 30 7.7 (sprayed) " 0.15 g/bush 14 14 6.5 (sprayed) " 0.18 g/bush 7 7 7.1 (sprayed) Table 11. Permethrin Residues in Sunflower Seed Process Fractions 1 Process Fractions Permethrin Residues (mg/kg) Whole Seed 0.58 Hulls 0.85 Meal 0.04 Crude Oil 0.41 Refined, bleached, deodorized oil 0.34 Deodorizer distillates 0.56 Soapstock 0.14 1 Values corrected for % recoveries. Table 12. The Effect of Baking Apples on Permethrin Residues 1 Sample Permethrin residues (mg/kg) cis isomer trans isomer cis:trans isomer total Uncooked I 0.433 0.641 40.3:59.7 1.07 " II 0.390 0.586 40:60 0.98 " III 0.465 0.708 39.6:60.4 1.17 Uncooked mean 0.429 0.645 40:60 1.07 Baked I 0.399 0.618 39.2:60.8 1.02 " II 0.384 0.579 39.9:60.1 0.96 " III 0.401 0.608 39.4:60.6 1.02 Baked mean 0.395 0.602 40:60 1.0 1 Fortified at 1.0 mg/kg. Table 13. The Effect of Frying Tomatoes on Permethrin Residues Sample Permethrin residues (mg/kg) cis isomer trans isomer cis:trans isomer total Uncooked I 0.039 0.058 40.2:59.8 0.10 II 0.035 0.051 40.7:59.3 0.09 III 0.036 0.054 40:60 0.09 Uncooked mean 0.037 0.054 40:60 0.09 Fried I 0.038 0.051 42.7:57.3 0.09 II 0.036 0.047 43.4:56.6 0.08 III 0.040 0.057 41.2:58.8 0.10 Fried mean 0.038 0.051 42:58 0.09 1 Fortified at 0.1 mg/kg. NATIONAL MAXIMUM RESIDUE LIMITS In addition to the national MRLs reported to earlier Meetings, additional ones have been established in the U.S. The full list is given in Table 14. Table 14. Maximum Residue Limits, U.S. Crop mg/kg Cottonseed 0.5 Broccoli 1.0 Brussels sprouts 1.0 Cabbage 6.0 Celery 5.0 Cauliflower 1.0 Lettuce (head) 20.0 Pears 0.05 Potatoes 0.05 Cattle, fat 0.5 Cattle, meat 0.05 Cattle, meat by-products 0.3 Eggs 0.05 Goats, fat 0.5 Goats, meat 0.05 Goats, meat by-products 0.3 Table 14. (con't) Crop mg/kg Pigs, fat 0.5 Pigs, meat 0.05 Pigs, meat by-products 3.0 Horses, fat 0.5 Horses, meat 0.05 Horses, meat by-products 0.3 Milk fat (reflecting 0.25 mg/kg in whole milk) 1.25 Poultry, fat 0.05 Poultry, meat 0.05 Poultry, meat by-products 0.05 Sheep, fat 0.5 Sheep, meat 0.05 Sheep, meat by-products 0.3 APPRAISAL The use pattern for permethrin on lettuce varies among countries. For example, the U.S. has established a preharvest withholding interval of one day on lettuce. New Zealand has set two days for greenhouse fruit and vegetables. Belgium has set two days for lettuce grown under glass and seven days for the outdoor crop. France has adopted 15 days and The Netherlands 21 days. The data reviewed by the 1979 Meeting from trials in The Netherlands indicated a maximum residue of 1.5 mg/kg 21 days after application at effective use rates. The Netherlands has established an MRL of 2 mg/kg. No residues data were available for review from Belgium, where the approved application rate is 0.025-0.0375 kg a.i./ha. However, the data from Denmark, Germany, The Netherlands and the U.K. support the view that permethrin levels in lettuce in Belgium would be below 2 mg/kg and Belgium has established an MRL of 1 mg/kg. In the U.K., rates up to 0.05 kg a.i./ha are used, and the data would suggest that a [illegible text] 2 mg/kg would cover most eventualities. The use pattern registered in the U.S. is for rates of 0.055-0.11 g a.i./ha against cabbage looper, Trichopulsia ni, and for rates of 0.11-0.22 kg a.i./ha against beet army-worm, Laphygma exigua, and corn earworm, Heliothis armigera. The registrations incorporate a one-day preharvest interval. These rates are generally higher than those usually required in western Europe, where rates up to 0.05 kg a.i./ha will usually suffice. Viewed overall, the available data show no marked differences in residue levels between the U.S. and western Europe for equivalent use rates and intervals. If the view is taken that the MRL should encompass all residue data obtained from the recommended use rates, then values as high as 17 mg/kg need to be noted. The U.S. has established an MRL of 20 mg/kg. However, the highest levels were recorded from untrimmed lettuce heads and in only two other trials out of 38 in the U.S. did residues exceed 10 mg/kg. The Meeting agreed that in estimating a maximum residue level a small percentage of the data could be rejected, particularly if such data represented the most severe use patterns, including a programme of 15 applications and a one-day preharvest interval. Data presented to the 1979 Meeting showed that permethrin residues in lettuce are present mainly in the wrapper leaves rather than the hearts. In the U.S., the lower values tended to be achieved where some degree of field trimming had taken place and the higher ones where it had not. A similar pattern was seen in more recent U.K. trials, in which residue levels in wrapper leaves were generally higher than in hearts. This was most marked in a variety in which the outer leaves were very broad and open and therefore received a higher spray deposit. However, the exposed nature of the leaves also leads to more rapid losses by photochemical degradation and/or wash-off by weathering, with the result that a more rapid decline in whole lettuce residues was observed. The area/weight ratio of large and small lettuce heads appeared to influence the distribution of residues more than any difference between EC formulations. Residues on the hearts of small lettuce were significantly higher than those on larger samples. Examination of the individual lettuce heads making up one sample lot showed that the maximum residue on individual whole lettuce may be up to 50% higher than the mean value. The type of lettuce did not appear to influence this variability. The Meeting proposed a reduction of the estimated maximum residue level from 20 mg/kg to 10 mg/kg. It was recognized that residues resulting from the severe use patterns needed to be confirmed under commercial growing conditions and the Meeting proposed selective surveys for this purpose (see FAO/WHO 1980a, 2.10 "Need for selective residue surveys"). Residue data from trials on almonds, asparagus, horseradish, olives and sunflower seed enabled the Meeting to estimate maximum residue levels of permethrin for these commodities. Data from Canada indicated that under Canadian use patterns residues on grapes would exceed the current CCPR proposal of 1 mg/kg and a revised maximum residue level was estimated. The residue data on leeks examined at the 1979 JMPR were reviewed and, without the prospect of a group MRL for bulb vegetables, the Meeting proposed a level for leeks based exclusively on the available data. Data from Finland confirmed the estimates of maximum residue levels for cucumber, rapeseed and tomato, but indicated that residues on currants could exceed the limit under discussion in CCPR. Data on the fate of permethrin during processing and cooking confirmed the general stability of permethrin residues. RECOMMENDATIONS The Meeting recommended that the levels listed below are suitable for establishing (temporary) maximum residue limits. The levels refer to the sum of cis and trans isomers of permethrin. Commodity MRL (mg/kg) Almonds 0.1 Asparagus 1 Grapes 2 (1) Horseradish 0.5 Leeks 0.5 (5) Lettuce 10(20) Olives 1 Sunflower seed 1 Sunflower seed oil (crude and refined) 1 FURTHER WORK OR INFORMATION Desirable Selective surveys of residues in lettuce known to have been treated under practical growing conditions with use patterns which include up to 15 applications and a one-day preharvest interval. Sampling and sample preparation should follow the recommendations of CCPR (IUPAC) (see 1982 JMPR Report, para 2.4), REFERENCES Burke, S. and Hulm, Y. Permethrin residues in olives. ICI Plant 1979 Protection Division data. (Unpublished) Fitzpatrick, R.D. Permethrin residues on asparagus. ICI Americas Inc. 1982a Agricultural Chemicals Division Report No. TMU0840/B. (Unpublished) 1982b Permethrin and permethrin metabolite residues on sunflower seed and stover. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0880/B. (Unpublished) Fujie, G.H. Determination of FMC 33297 residues in/on lettuce. FMC 1976 Corporation Agricultural Chemical Group Report No. W-0122. (Unpublished) Fujie, G.H. Determination of FMC 33297 residues on lettuce. FMC 1979 Corporation Agricultural Chemical Group Report No. W-0239. (Unpublished) Pearson, F.J. Permethrin and permethrin metabolite residues in 1982 almonds. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0901/B. (Unpublished) Swaine, H. and Rippington, D. Permethrin residues in apples and 1982 tomatoes: effect of cooking on residues. ICI Plant Protection Division Residue Data Report No. PP557B044. (Unpublished) Swaine, H. and Sapiets, A. Permethrin residues in crop samples 1979a analysed during 1977-78: Leaf, root and forage crops. ICI Plant Protection Division Report No. RJ0081A. (Unpublished) Swaine, H. and Sapiets, A. Permethrin residues in crop samples 1979b analysed during 1977-78: Garden and household products. ICI Plant Protection Division Report No. RJ0082A. (Unpublished) Swaine, H., Froggatt, D.A., Burke, S. and Robbins, A.J. Permethrin 1980a residues in lettuce, U.K., 1980. ICI Plant Protection Division Residue Data Report No. 404/PP557-B032. (Unpublished) Swaine, H., Froggatt, D., French, D.A., Farrelly, E. and Robbins, A. 1980b Permethrin residues in lettuce, UK, 1980. ICI Plant Protection Division Residue Data Report No-402/PP557B031. (Unpublished) Swaine, H., Sapiets, A. and Robertson, S. Permethrin residues in 1980c lettuce, UK, 1979. ICI Plant Protection Division Residues Data Report No. 357/PP557B026. (Unpublished) Swaine, H., Sapiets, A. and Robertson, S. Permethrin residues in 1981 lettuce under glass, Denmark, 1980. ICI Plant Protection Division Residues Data Report No. PP557B0040. (Unpublished) Ussary, J.P. Permethrin residues in lettuce. Ten ICI Americas Inc. 1975-77 Agricultural Chemicals Division Reports. (Unpublished) 1978 Permethrin residues on lettuce. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0404/B. (Unpublished) 1980a Permethrin residues on almonds. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0482/B. (Unpublished) 1980b Permethrin residues in asparagus. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0478/B. (Unpublished) 1980c Permethrin residues in untrimmed lettuce. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0510/B. (Unpublished) 1981a Permethrin residues in almonds after aerial applications. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0571/B. (Unpublished) 1981b Permethrin and permethrin metabolite residues on horseradish roots. ICI Americas Inc. Agricultural Chemicals Division Report No. TMU0687/B. (Unpublished) 1982 Permethrin and permethrin metabolite residues in sunflower seed processing fractions. ICI Americas Inc. Agricultural Chemicals Division Report No.TMU0897/B. (Unpublished)
See Also: Toxicological Abbreviations Permethrin (EHC 94, 1990) Permethrin (HSG 33, 1989) Permethrin (ICSC) PERMETHRIN (JECFA Evaluation) Permethrin (Pesticide residues in food: 1979 evaluations) Permethrin (Pesticide residues in food: 1980 evaluations) Permethrin (Pesticide residues in food: 1981 evaluations) Permethrin (Pesticide residues in food: 1983 evaluations) Permethrin (Pesticide residues in food: 1984 evaluations) Permethrin (Pesticide residues in food: 1987 evaluations Part II Toxicology) Permethrin (JMPR Evaluations 1999 Part II Toxicological) Permethrin (UKPID) Permethrin (IARC Summary & Evaluation, Volume 53, 1991)