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Bifenthrin is registered in Australia for use on various crops. Details of the registered use patterns can be found on the approved labels of registered products containing bifenthrin as the active constituent. This Animal Residue Data Sheet provides information on the possible residues in feed commodities obtained from crops treated with bifenthrin. It also provides information on the anticipated maximum dietary exposure of animals fed treated commodities, which should not result in the violation of animal MRLs.
The Australian MRLs for bifenthrin in food and animal feed commodities, as listed in Table 1 and Table 4 of the MRL Standard (as at August 2002) are shown below. The residue definition of bifenthrin is the parent compound per se.
| Code | Food | MRL, mg/kg |
| Food Commodities | ||
| FP 0226 | Apple | *0.05 |
| FI 0326 | Avocado | T0.1 |
| FI 0327 | Banana | 0.1 |
| GC 0080 | Cereal grains | T2 |
| VL 0465 | Chervil | T0.5 |
| FC 0001 | Citrus fruits | *0.05 |
| SO 0691 | Cotton seed | 0.1 |
| VO 0440 | Egg plant | T0.5 |
| VD 0561 | Field Pea (dry) | T*0.01 |
| VC 0045 | Fruiting vegetables, cucurbits | T*0.1 |
| HS 0783 | Galangal, rhizomes | T10 |
| FB 0269 | Grapes | *0.01 |
| HH 0092 | Herbs | T10 |
| Kaffir lime leaves | T10 | |
| Lemon balm | T10 | |
| Lemon grass | T10 | |
| DT 1111 | Lemon verbena | T10 |
| VD 0545 | Lupin (dry) | T*0.02 |
| Mizuna | T10 | |
| VO 0442 | Okra | T0.5 |
| FP 0230 | Pear | 0.5 |
| VO 0051 | Peppers | T0.5 |
| VD 0070 | Pulses [except field pea (dry), Lupin (dry)] | *0.02 |
| SO 0495 | Rape seed | *0.02 |
| Rucola (rocket) | T10 | |
| FS 0012 | Stone fruit | T1.0 |
| GS 0659 | Sugarcane | *0.01 |
| HS 0794 | Tumeric, root | T10 |
| VO 0448 | Tomato | 0.5 |
| Animal commodities | ||
| MM 0095 | Meat (mammalian) [in the fat] | 2 |
| MO 0105 | Edible offal (Mammalian) | 0.5 |
| ML 0106 | Milks | 0.5 |
| PE 0112 | Eggs | *0.05 |
| PO 0111 | Poultry, Edible offal of | *0.05 |
| PM 0110 | Poultry meat [in the fat] | *0.05 |
| Animal feed commodities | ||
| AL 1020 | Alfalfa fodder [Lucerne] | 0.1 |
| AL 1021 | Alfalfa forage (green) | 0.1 |
| Canola fodder (dry) | *0.01 | |
| Canola forage (green) | 1 | |
| AL 1031 | Clover hay or fodder | *0.05 |
| Clover forage (green) | *0.05 | |
| Faba bean forage (green) | 1 | |
| Faba bean fodder (dry) | *0.02 | |
| Field pea forage (green) | 1 | |
| Field pea fodder (dry) | *0.01 | |
| AL 0545 | Lupin forage | 1 |
| Lupin fodder (dry) | *0.02 | |
| Forage (green) of cereal grains | 0.2 | |
| Navy beans fodder | 1 | |
| Navy beans forage (green) | 5 | |
| AM 0659 | Sugarcane fodder | *0.02 |
| AS 0081 | Straw and fodder (dry) of cereal grains | *0.01 |
| Pear pomace, dry | 5 | |
The Maximum Feeding Level (MFL, the feeding level at which the MRLs are based, the equivalent Daily Dietary Intake For Livestock (DDIL) and the equivalent daily intake of bifenthrin are summarised below.
| Species | MFL, ppm in diet |
Equivalent DDIL, mg/kg bw | Equivalent
intake of bifenthrin, mg/animal/day |
| Cattlea | 5.7 | 0.22 | 93 |
| Sheepb | 5.7 | 0.24 | 14.3 |
| Pigb | 5.7 | 0.24 | 14.3 |
| Poultryc | 0.5 | 0.0375 | 0.075 |
| a
Based actual dose levels in dairy cattle study (413 kg bw, 16.4
kg DM/day) b MFL is based on cattle data as no sheep or pig data available, DDIL is calculated from MFL assuming a 60 kg animal consuming 2.5 kg DM/day c Based on assumed bodyweight of 2 kg and feed consumption of 0.15 kg DM/day |
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Feed commodities that may contain residues of bifenthrin are listed in the table below. The theoretical maximum proportion of the diet that the commodity can compose, when residues are present at the MRL, without the significant risk of animal commodity MRLs being violated is also given. It should be noted that the feeding levels assumed by the APVMA when setting animal commodity MRLs are theoretical values, and they should not be taken as recommendations of appropriate rations for livestock.
| Commodity a | Assumed Maximum proportion of diet (%)b | Feed intake (kg/animal/day)c | MRL (mg/kg) d |
Maximum intake of bifenthrin from commodity (mg/animal/day)e | Theoretical maximum proportion of diet (%)f |
| Cattle (Based on a 500 kg animal consuming 20 kg DM/day) | |||||
| Alfalfa fodder [Lucerne] | 100 | 20 | 0.1 | 2 | 100 |
| Alfalfa forage (green) | 100 | 20 | 0.1 | 2 | 100 |
| Canola fodder (dry) | 100 | 20 | *0.01 | 0.2 | 100 |
| Canola forage (green) | 100 | 20 | 1 | 20 | 100 |
| Cereal grains | 100 | 20 | 0.5 (Expected residue, Footnote g) |
10 | 100 |
| Clover hay or fodder | 100 | 20 | *0.05 | 1 | 100 |
| Clover forage (green) | 100 | 20 | *0.05 | 1 | 100 |
| Faba bean forage (green) | 100 | 20 | 1 | 20 | 100 |
| Faba bean fodder (dry) | 100 | 20 | *0.02 | 0.4 | 100 |
| Field pea forage (green) | 100 | 20 | 1 | 20 | 100 |
| Field pea fodder (dry) | 100 | 20 | *0.01 | 0.2 | 100 |
| Forage (green) of cereal grains | 100 | 20 | 0.2 | 4 | 100 |
| Lupin forage | 100 | 20 | 1 | 20 | 100 |
| Lupin fodder (dry) | 100 | 20 | *0.02 | 0.4 | 100 |
| Navy beans fodder | 100 | 20 | 1 | 20 | 100 |
| Navy beans forage (green) | 100 | 20 | 5 | 100 | 100 |
| Pear pomace, dry | 20 | 4 | 0.95 (STMR-P) |
3.8 | 100 |
| Sugarcane fodder | 100 | 20 | *0.02 | 0.4 | 100 |
| Straw and fodder (dry) of cereal grains | 100 | 20 | *0.01 | 0.2 | 100 |
| Sheep (Based on a 60 kg animal consuming 2.5 kg DM/day) | |||||
| Alfalfa fodder [Lucerne] | 100 | 2.5 | 0.1 | 0.25 | 100 |
| Alfalfa forage (green) | 100 | 2.5 | 0.1 | 0.25 | 100 |
| Canola fodder (dry) | 100 | 2.5 | *0.01 | 0.025 | 100 |
| Canola forage (green) | 100 | 2.5 | 1 | 2.5 | 100 |
| Cereal grains | 100 | 2.5 | 0.5 (Expected residue, Footnote g) |
1.25 | 100 |
| Clover hay or fodder | 100 | 2.5 | *0.05 | 0.125 | 100 |
| Clover forage (green) | 100 | 2.5 | *0.05 | 0.125 | 100 |
| Faba bean forage (green) | 100 | 2.5 | 1 | 2.5 | 100 |
| Faba bean fodder (dry) | 100 | 2.5 | *0.02 | 0.05 | 100 |
| Field pea forage (green) | 100 | 2.5 | 1 | 2.5 | 100 |
| Field pea fodder (dry) | 100 | 2.5 | *0.01 | 0.025 | 100 |
| Forage (green) of cereal grains | 100 | 2.5 | 0.2 | 0.5 | 100 |
| Lupin forage | 100 | 2.5 | 1 | 2.5 | 100 |
| Lupin fodder (dry) | 100 | 2.5 | *0.02 | 0.05 | 100 |
| Navy beans fodder | 100 | 2.5 | 1 | 2.5 | 100 |
| Navy beans forage (green) | 100 | 2.5 | 5 | 12.5 | 100 |
| Pear pomace, dry | 20 | 0.5 | 0.95
(STMR-P) |
0.475 | 100 |
| Sugarcane fodder | 100 | 2.5 | *0.02 | 0.05 | 100 |
| Straw and fodder (dry) of cereal grains | 100 | 2.5 | *0.01 | 0.025 | 100 |
| Pigs (Based on a 60 kg animal consuming 2.5 kg DM/day) | |||||
| Cereal grains | 100 | 2.5 | 0.5 (Expected residue, Footnote g) |
1.25 | 100 |
| Cotton seed | 30 | 0.75 | 0.1 | 0.075 | 100 |
| Pear pomace, dry | 20 | 0.5 | 0.95
(STMR-P) |
0.475 | 100 |
| Poultry (Based on a 2 kg animal consuming 150 g DM/day) | |||||
| Cereal grains | 100 | 0.15 | 0.5 (Expected residue, Footnote g) |
0.075 | 100 |
| Cotton seed | 30 | 0.045 | 0.1 | 0.0045 | 100 |
| Pear pomace, dry | 20 | 0.03 | 0.95
(STMR-P) |
0.0285 | 100 |
| a
The feed commodities that may contain residues of bifenthrin, and
may form more than 20% of an animals diet. b The maximum % of the diet that the commodity is assumed to comprise for the purposes of setting MRLs, based on Stockfeed Information Document 1 c The equivalent amount of feed for an animal of designated weight and feed intake that is assumed for the purposes of setting MRLs d The MRL (or STMR-P where noted) for each feed commodity (correction for dry weight basis where required) e The maximum intake of bifenthrin when the commodity is fed at the maximum assumed level (Column 1) in the absence of other sources of bifenthrin. f The maximum % of the diet at which the commodity could theoretically be fed without significant risk of exceeding animal commodity MRLs. It is assumed that the residue in the feed commodity is present at the MRL or STMR-P (or dry weight equivalent) and other dietary sources of bifenthrin are absent. g Highest residue expected to occur in grain under temporary trial use. Registered uses should result in residues of bifenthrin in cereal grains of <0.02 mg/kg. |
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DM: Dry matter. The feed consumption for livestock and the residue levels in feed commodities are expressed on a dry matter basis.
DDIL: Daily Dietary Intake for Livestock. The level of dietary exposure for a specified chemical in a specified species that should not result in exceedance of the relevant animal commodity MRLs. Expressed in mg chemical/kg bodyweight.
MFL: Maximum Feeding Level. The level of dietary exposure for a specified chemical in a specified species that should not result in exceedance of the relevant animal commodity MRLs. Expressed in terms of ppm in the feed.
MRL: The concentration of a chemical residue, in units of mg/kg, that is legally permitted in or on a food or food commodity.
ppm in the feed: Parts per million in the feed. An alternate way of expressing the level of dietary exposure for a chemical. The level of chemical intake is calculated as though it were present uniformly in the total feed intake. The ppm in the feed is calculated using the following formula: DDIL (mg chemical/kg bw) _ body weight (kg) ¸ daily feed intake (kg).
STMR-P: Supervised Trial Median Residue of the processed commodity. The highest residue that livestock are likely to be exposed to in practice when fed processed commodities over a prolonged period. This is derived from the STMR of the whole commodity multiplied by the processing factor.
The following calculations outline the theoretical diet used to calculate the maximum anticipated dietary exposure, maximum feeding level (MFL) and the daily dietary intake for livestock (DDIL) for cattle, sheep, pigs and poultry.
| Feed group | Feed commodity | % in the diet | Feed intake, kg/animal/daya | MRL, mg/kg | % DMb | Intake of bifenthrin, mg/animal/dayc |
| Fodder and forage[100% maximum] | Navy bean forage | 100 | 20 | 5 | - | 100 |
| Total | 100 | 20 | 100 | |||
| aBased
on assumed feed consumption of 20 kg dry matter/day bEstimate of percentage dry matter. Applied to MRLs expressed on a fresh weight basis cBased on assumed bodyweight of 500 kg |
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| Maximum
anticipated dietary exposure: |
100 mg/animal/day |
| equivalent
to: |
0.2 mg/kg bw |
| equivalent
to: |
5 ppm in the diet |
| MFL: |
5.7 ppm in the diet |
| equivalent
DDIL: |
0.22 mg/kg bw |
MFL and DDIL are based on actual dose level, animal bodyweight and feed consumption in the dairy cattle transfer study.
| Feed group | Feed commodity | % in the diet | Feed intake, kg/animal/daya | MRL, mg/kg | % DMb | Intake of bifenthrin, mg/animal/dayc |
| Fodder and forage[100% maximum] | Navy bean forage | 100 | 2.5 | 5 | - | 12.5 |
| Total | 100 | 2.5 | - | - | 12.5 | |
| aBased
on assumed feed consumption of 2.5 kg dry matter/day bEstimate of percentage dry matter. Applied to MRLs expressed on a fresh weight basis cBased on assumed bodyweight of 60 kg |
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| Maximum
anticipated dietary exposure: |
12.5 mg/animal/day |
| equivalent
to: |
0.21 mg/kg bw |
| equivalent
to: |
5 ppm in the diet |
| MFL: |
5.7 ppm in the diet |
| equivalent
DDIL: |
0.24 mg/kg bw |
No sheep transfer data are available. The MFL is based on actual dose level, animal bodyweight and feed consumption in the dairy cattle transfer study. The DDIL is calculated from the MFL assuming a 60 kg animal consuming 2.5 kg DM per day.
| Feed group | Feed commodity | % in the diet | Feed intake, kg/animal/daya | Expected residue, mg/kg | % DMb | Intake of bifenthrin, mg/animal/dayc |
| Grain[100% maximum] | Cereal grains | 100 | 2.5 | 0.5 | - | 1.25 |
| Total | 100 | 2.5 | - | - | 1.25 | |
| aBased
on assumed feed consumption of 2.5 kg dry matter/day bEstimate of percentage dry matter. Applied to MRLs expressed on a fresh weight basis cBased on assumed bodyweight of 60 kg |
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Registered uses of bifenthrin should result in residues <0.02 mg/kg in cereal grains. The current MRL for cereal grains is T2 mg/kg to cover residues that may arise under a trial permit. The maximum expected residue in grain in the trial situation is 0.5 mg/kg. This figure has been used as the best estimate of pig dietary exposure from cereal grains.
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Maximum anticipated dietary exposure: |
1.25 mg/animal/day |
|
equivalent to: |
0.021 mg/kg bw |
|
equivalent to: |
0.5 ppm in the diet |
|
MFL: |
5.7 ppm in the diet |
|
equivalent DDIL: |
0.24 mg/kg bw |
No pig transfer data are available. The MFL is based on actual dose level, animal bodyweight and feed consumption in the dairy cattle transfer study. The DDIL is calculated from the MFL assuming a 60 kg animal consuming 2.5 kg DM per day.
| Feed group | Feed commodity | % in the diet | Feed intake, kg/animal/daya | Expected residue, mg/kg | % DMb | Intake of bifenthrin, mg/animal/dayc |
| Grain[100% maximum] | Cereal grains | 100 | 0.15 | 0.5 | - | 0.075 |
| Total | 100 | 0.15 | - | - | 0.075 | |
| aBased
on assumed feed consumption of 0.150 kg dry matter/day bEstimate of percentage dry matter. Applied to MRLs expressed on a fresh weight basis cBased on assumed bodyweight of 2 kg |
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Registered uses of bifenthrin should result in residues <0.02 mg/kg in cereal grains. The current MRL for cereal grains is T2 mg/kg to cover residues that may arise under a trial permit. The maximum expected residue in grain in the trial situation is 0.5 mg/kg. This figure has been used as the best estimate of poultry dietary exposure from cereal grains.
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Maximum anticipated dietary exposure: |
0.075 mg/animal/day |
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equivalent to: |
0.0375 mg/kg bw |
|
equivalent to: |
0.5 ppm in the diet |
|
MFL: |
0.5 ppm in the diet |
|
equivalent DDIL: |
0.0375 mg/kg bw |
The MFL and DDIL were estimated from a poultry transfer study.
The residue definition of bifenthrin in Australia is the parent compound per se.
The table below shows Australian residue data for lucerne forage and hay.
Data from trials conducted in NSW and SA were evaluated. The rates employed in lucerne trials were 1´ and 2´ the maximum label rate for native budworm control in lucerne seed crops.
| Sample, Trial Site, | Application | Days after treatment | Residues of bifenthrin (mg/kg | ||
| Year | Rate (g ai/ha) | Timing | No. | dry matter) | |
| Lucerne forage | 60 | Early flowering | 1 | 0 | 38 |
| NSW 1995 | 7 | 37 | |||
| 14 | 6.8 | ||||
| 21 | 5.8 | ||||
| 28 | 4 | ||||
| 120 | Early flowering | 1 | 0 | 44 | |
| 7 | 9.4 | ||||
| 14 | 6.0 | ||||
| 21 | 3.0 | ||||
| 28 | 1.1 | ||||
| Lucerne forage | 60 | Early flowering | 1 | -1 | <0.01 |
| SA 1995 | 7 | 6.3 | |||
| 14 | 4.3 | ||||
| 28 | 0.48 | ||||
| 120 | Early flowering | 1 | -1 | <0.01 | |
| 7 | 11.5 | ||||
| 14 | 8.3 | ||||
| 28 | 3.1 | ||||
Feeding studies in dairy cows were conducted at levels of 5, 15 and 50 ppm in the diet for 28 days (average actual dose levels were 5.7, 16.8 and 55.2 ppm in the diet, equivalent to 0.22, 0.64 and 1.75 mg/kg bw). [Source: FMC Studies PC-0023 & P-1030]
| Day | Residues of bifenthrin (mg/kg) in whole milk | ||
| 5.7 ppm | 16.8 ppm | 55.2 ppm | |
| 0 | < 0.005 | < 0.007 | 0.02 |
| 1 | 0.05 | - | 0.25 |
| 3 | 0.08 | 0.11 | 0.58 |
| 5 | 0.10 | - | 0.53 |
| 8 | - | 0.21 | 0.72 |
| 12 | 0.06 | - | 0.79 |
| 16 | - | 0.14 | 0.59 |
| 20 | 0.09 | - | 0.63 |
| 24 | - | 0.18 | 0.67 |
| 28 | 0.08 | - | 0.65 |
Limit of detection = 0.005 mg/kg; limit of quantitation = 0.02 mg/kg
| Sample | Bifenthrin (mg/kg) in tissues | ||
| 5.7 ppm | 16.8 ppm | 55.2 ppm | |
| Adductor muscle | 0.03, 0.04 | 0.08, 0.09 | 0.10, 0.23 |
| Pectoral muscle | 0.05, 0.06 | 0.16 ,0.24 | 0.33, 0.88 |
| Cardial muscle | 0.04, 0.06 | 0.12, 0.17 | 0.27, 0.41 |
| Liver | < 0.01, 0.02 | 0.02, 0.03 | 0.07, 0.09 |
| Kidney | 0.1, 0.04 | 0.18, 0.19 | 0.44, 0.49 |
| Subcutaneous fat | 0.25, 0.75 | 0.68, 0.92 | 2.00, 2.70 |
| Peritoneal fat | 0.77, 1.70 | 1.50, 2.20 | 3.30, 5.70 |
Limit of detection = 0.01 mg/kg; limit of quantitation = 0.1 mg/kg.
In a separate study lactating cows were dosed at nominal levels equivalent to 5 and 50 ppm in the diet for 28 days (average actual dose levels were 5.7 and 54.5 ppm in the diet, equivalent to 0.19 and 2.0 mg/kg bw). There were three cows per dose group. Bifenthrin residues were determined in milk fat only. [Source: FMC Study No. P-1703]
| Day | Bifenthrin (mg/kg) in milk fat | |
| 5.7 ppm | 54.5 ppm | |
| 0 | < 0.05 | < 0.05 |
| 3 | 0.72, 0.78, 0.97 | 7.8, 8.8, 9.6 |
| 8 | 0.64, 0.67, 1.60 | 7.8, 8.9, 10.2 |
| 16 | 0.54, 0.62, 1.20 | 8.0, 8.2, 10.1 |
| 24 | 0.35, 0.70, 1.10 | 7.4, 8.6, 9.4 |
| 28 | 0.48, 0.50, 0.61 | 8.0, 9.4, 10.4 |
Limit of detection =. 0.05 mg/kg; limit of quantitation = 0.2 mg/kg.
Correcting for the slightly different dose levels used in the whole milk and milk fat studies indicates that the highest observed residues are 10-15 times higher when determined in milk fat compared to whole milk.
Laying hens were dosed with acid-14C-bifenthrin for 10 days at a dose level equivalent to 31 ppm in the diet. The composition of the total radioactive residue was determined in various tissues. Residues of bifenthrin were as follows: egg yolk (day 10 eggs) 1.44 mg/kg; abdominal fat 1.0 mg/kg; adductor muscle 0.066 mg/kg; liver 0.05 mg/kg.
Laying
hens were dosed with bifenthrin for 28 days at dose levels equivalent
to 2.5, 25 and 250 ppb in the diet. At the highest dose level residues
of bifenthrin were not detected in fat (<0.01 mg/kg), liver (<0.01
mg/kg) gizzard (<0.01 mg/kg) and muscle (<0.005 mg/kg). Residues
in eggs were only observed at the highest feed level and were up to 0.004
mg/kg.