|
Last updated 28 March 2002
Bitertanol is registered in Australia for use on beans (Phaseolus vulgaris) and various ornamentals. Phaseolus vulgaris includes the common bean, French bean, kidney bean, field bean, snap bean and string bean. Details of the registered use patterns can be found on the approved labels of registered products containing bitertanol as the active constituent. This Animal Residue Data Sheet provides information on the possible residues in feed commodities obtained from crops treated with bitertanol. 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.
Current MRLs
The Australian MRLs for bitertanol in food and animal feed commodities, as listed in Table 1 and Table 4 of the MRL Standard [as at 8 February 2002] are shown below with the proposed MRLs. The residue definition of bitertanol is the parent compound per se.
|
Code |
Food |
Proposed MRL, mg/kg |
|
Food Commodities |
||
|
VP 0061 |
Beans, except broad bean and soya bean |
0.5 |
|
FB 0275 |
Strawberry |
*0.05 |
|
Animal commodities |
||
|
MO 0105 |
Edible offal (mammalian) |
3 |
|
PE 0112 |
Eggs |
*0.01 |
|
MM 0095 |
Meat [mammalian] [in the fat] |
0.3 |
|
ML 0106 |
Milks [in the fat] |
0.2 |
|
PO 0111 |
Poultry, Edible offal of |
*0.01 |
|
PM 0110 |
Poultry meat |
*0.01 |
|
Animal feed commodities |
||
|
AL 1030 |
Bean forage |
50 |
|
AL 0061 |
Bean fodder |
50 |
Summary of maximum feeding levels and livestock dietary intakes
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 bitertanol are summarised below.
|
Species |
MFL, |
Equivalent DDIL, mg/kg bw |
Equivalent
intake of bitertanol, |
|
Cattlea |
75 |
1.88 |
840 |
|
Sheepb |
75 |
3.1 |
186 |
|
Pigb |
75 |
3.1 |
186 |
|
Poultryc |
1 |
0.075 |
0.15 |
|
a
Based on actual animal transfer study data |
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Detailed information
All feed commodities
Feed commodities that may contain residues of bitertanol are listed in the table below. Only feed items from approved or registered uses of the chemical are included. The theoretical maximum proportion of the diet that the commodity can comprise, 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 |
Maximum intake of bitertanol from commodity (mg/animal/day)e |
Theoretical maximum proportion of diet (%)f |
|
Cattle (Based on a 500 kg animal consuming 20 kg DM/day) |
|||||
|
Bean forage |
100 |
20 |
50 |
1000 |
100 |
|
Bean fodder |
100 |
20 |
50 |
1000 |
100 |
|
Beans |
100 |
20 |
0.5 |
10 |
100 |
|
Sheep (Based on a 60 kg animal consuming 2.5 kg DM/day) |
|||||
|
Bean forage |
100 |
2.5 |
50 |
125 |
100 |
|
Bean fodder |
100 |
2.5 |
50 |
125 |
100 |
|
Beans |
100 |
2.5 |
0.5 |
1.25 |
100 |
|
Pigs (Based on a 60 kg animal consuming 2.5 kg DM/day) |
|||||
|
Beans |
100 |
2.5 |
0.5 |
1.25 |
100 |
|
Poultry (Based on a 2 kg animal consuming 150 g DM/day) |
|||||
|
Beans |
100 |
0.15 |
0.5 |
0.075 |
100 |
|
a
The feed commodities that may contain residues of bitertanol, and
may form more than 20% of an animals diet. |
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Abbreviations and definitions
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. For example: a cow consumes 10 kg of grain containing 10 mg/kg of Chemical X and 10 kg of apple pomace containing 5 mg/kg of Chemical X. The total intake of Chemical X is 150 mg in 20 kg of feed. This is equivalent to 7.5 ppm in the feed [150÷20].
Attachment 1: Anticipated maximum dietary exposure
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.
Cattle
|
Feed group |
Feed commodity |
% in the diet |
Feed intake, kg/animal/daya |
MRL, mg/kg |
% DMb |
Intake of bitertanol, mg/animal/dayc |
|
Bean |
Forage |
100 |
20 |
50 |
1000 |
|
|
Fodder |
100 |
20 |
50 |
1000 |
||
|
Bean |
100 |
20 |
0.5 |
10 |
||
|
Total |
100 |
20 |
1000 |
|||
|
a
Based on assumed feed consumption of 20 kg dry matter/day |
||||||
|
Maximum anticipated dietary exposure: |
1000 mg/animal/day |
|
equivalent to: |
2 mg/kg bw |
|
equivalent to: |
50 ppm in the diet |
|
MFL
(Based on the available animal |
75 ppm in the diet |
|
equivalent DDIL: |
1.88 mg/kg bw* |
* DDIL taken from feeding study
Sheep
|
Feed group |
Feed commodity |
% in the diet |
Feed intake, kg/animal/day a |
MRL, mg/kg |
% DMb |
Intake of bitertanol, mg/animal/day c |
|
Bean |
Forage |
100 |
2.5 |
50 |
125 |
|
|
Fodder |
100 |
2.5 |
50 |
125 |
||
|
Bean |
100 |
2.5 |
0.5 |
1.25 |
||
|
Total |
100 |
2.5 |
125 |
|||
|
aBased
on assumed feed consumption of 2.5 kg dry matter/day |
||||||
|
Maximum anticipated dietary exposure: |
125 mg/animal/day |
|
equivalent to: |
2.08 mg/kg bw |
|
equivalent to: |
50 ppm in the diet |
|
MFL
(Based on the cattle feeding |
75 ppm in the diet |
|
equivalent DDIL: |
3.13 mg/kg bw |
Pigs
|
Feed group |
Feed commodity |
% in the diet |
Feed intake, kg/animal/day a |
MRL, mg/kg |
% DMb |
Intake of bitertanol, mg/animal/day c |
|
Bean |
Bean |
100 |
2.5 |
0.5 |
1.25 |
|
|
Total |
100 |
2.5 |
1.25 |
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|
aBased
on assumed feed consumption of 2.5 kg dry matter/day |
||||||
|
Maximum anticipated dietary exposure: |
1.25 mg/animal/day |
|
equivalent to: |
0.02 mg/kg bw |
|
equivalent to: |
0.5 ppm in the diet |
|
MFL
(Based on the cattle feeding |
75 ppm in the diet |
|
equivalent DDIL: |
3.13 mg/kg bw |
Poultry
|
Feed group |
Feed commodity |
% in the diet |
Feed intake, kg/animal/daya |
MRL, mg/kg |
% DMb |
Intake of bitertanol, mg/animal/dayc |
|
Bean |
Bean |
100 |
0.15 |
0.5 |
0.075 |
|
|
Total |
100 |
0.15 |
0.075 |
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|
aBased
on assumed feed consumption of 0.150 kg dry matter/day |
||||||
|
Maximum anticipated dietary exposure: |
0.075 mg/animal/day |
|
equivalent to: |
0.0375 mg/kg bw |
|
equivalent to: |
0.5 ppm in the diet |
|
MFL (Based on the available animal feeding data (Attachment 2)): |
1 ppm in the diet |
|
equivalent DDIL: |
0.075 mg/kg bw |
Attachment 2: Residue data
The residue definition of bitertanol in Australia is the parent compound per se.
Selected residue data for animal feed commodities
|
Report no. |
Country |
Crop |
Formulation |
Rate (g ai/ha) |
No sprays (interval) |
Commodity |
PHI |
Residues (mg/kg) |
|
Mobay 87140 |
USA |
Snap beans |
300 EC |
280.2 |
2 (14) |
Green vines |
0 3 |
6.89 3.11 |
|
Mobay 87215 |
USA |
Snap beans |
300 EC |
280.2 |
2 (10) |
Green vines |
15 18 |
2.66 0.51 |
|
Mobay 87237 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (14) |
Dry vines |
21 |
3.24 |
|
Mobay 87236 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (10) |
Dry vines |
42 |
0.07 |
|
Mobay 87235 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (10) |
Dry vines |
14 |
6.25 |
|
Mobay 87214 |
USA |
Snap beans |
500 WP |
280.2 |
2 (15) |
Green vines |
0 3 |
3.03 2.54 |
|
311/88006/U10 |
South Africa |
Beans |
300 EC |
125.1 |
1 |
Plants |
1 4 8 16 |
23, 40 2.5, 3.4 3.7, 3.8 0.36, 0.30 |
|
311/88006/U10 |
South Africa |
Beans |
300 EC |
250.2 |
1 |
Plants |
1 4 8 16 |
43, 39 6.0, 6.8 4.4, 5.0 0.36, 0.32 |
|
311/88059/U201 |
South Africa |
Kidney Beans |
300 EC |
252 |
1 |
Plants |
0 3 8 22 |
20 8.8 8.4, 10.4 6.0 |
|
311/88059/U201 |
South Africa |
Kidney Beans |
300 EC |
504 |
1 |
Plants |
0 3 8 22 |
24 9.9 14.3, 12.6 9.3 |
Source: Bayer Australia Ltd submission, Baycor 300 Fungicide Spray, file 329-1-619, 21/11/86. South African trials also reported in JMPR.
Residues in bean vines at 0 1 days after the last application at 250 280 g ai/ha (approximately 2´ label rate) were 3.03, 6.89, 20, 39 and 43 mg/kg. At 125 g ai/ha residues in bean plants were 23 and 40 mg/kg while at 504 g ai/ha residues in bean plants were 24 mg/kg. Residues in plants decline rapidly after application. It is estimated that bitertanol residues decline with a half life of approximately 3 days over the 0-3 DAT period.
Residues in green beans from Australian trials
|
Trial year |
1982 |
1984 |
1984 |
1985 |
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|
Study no |
16/82 |
27/84 |
28/84 |
30/85 |
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|
Formulation |
300 g/L EC |
300 g/L EC |
300 g/L EC |
300 g/L EC |
||||
|
Appln method, timing |
Hi volume, in pod |
Hand boom, late pod |
Hand boom, late pod |
Hi volume, fruiting |
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|
PHI (days) |
120 g ai/ha |
240 g ai/ha |
240 g ai/ha |
480 g ai/ha |
240 g ai/ha |
480 g ai/ha |
240 g ai/ha |
480 g ai/ha |
|
1 |
0.51 |
1.02 |
0.44 |
1.03 |
0.56 |
1.27 |
0.28 |
0.47 |
|
2 |
0.31 |
0.34 |
||||||
|
3 |
0.22 |
0.16 |
0.50 |
0.97 |
0.56 |
1.43 |
0.24 |
0.15 |
|
4 |
0.21 |
0.36 |
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|
5 |
0.22 |
0.21 |
0.20 |
1.07 |
0.86 |
0.76 |
0.06 |
0.20 |
|
7 |
0.15 |
0.57 |
0.33 |
0.27 |
0.09 |
0.18 |
||
|
10 |
0.14 |
0.26 |
0.23 |
0.20 |
ND |
0.13 |
||
|
14 |
0.08 |
0.19 |
0.24 |
0.11 |
ND |
0.12 |
||
Source: PACC meeting 79, February 1988, Item 10.9.
|
Report no. |
Country |
Crop |
Formulation |
Rate (g ai/ha) |
No sprays (interval) |
Commodity |
PHI |
Residues (mg/kg) |
|
Mobay 87140 |
USA |
Snap beans |
300 EC |
280.2 |
2 (14) |
Beans in pod |
0 3 |
0.46 0.63 |
|
Mobay 87215 |
USA |
Snap beans |
300 EC |
280.2 |
2 (10) |
Beans in pod |
15 18 |
0.19 0.23 |
|
Mobay 87237 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (14) |
Beans, dry |
21 |
0.18 |
|
Mobay 87236 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (10) |
Beans, dry |
42 |
<0.01 |
|
Mobay 87235 |
USA |
Beans, dry |
300 EC |
280.2 |
2 (10) |
Beans, dry |
14 |
0.02 |
|
Mobay 87214 |
USA |
Snap beans |
500 WP |
280.2 |
2 (15) |
Beans in pod |
0 3 |
0.80 0.28 |
|
311/88007/S172 |
South Africa |
Beans |
200 EC |
190 |
1 |
Beans |
0 3 5 7 10 14 |
0.57 0.06 0.06 0.05 0.05 <0.05 |
|
311/88006/U10 |
South Africa |
Beans |
300 EC |
125.1 |
1 |
Beans |
1 4 8 16 |
2.55 0.16 0.14 0.14 |
|
311/88006/U10 |
South Africa |
Beans |
300 EC |
250.2 |
1 |
Beans |
1 4 8 16 |
3.05 0.13 0.40 0.22 |
|
311/88059/U201 |
South Africa |
Kidney Beans |
300 EC |
252 |
1 |
Kidney beans |
0 3 8 22 |
0.12 0.1 <0.1 <0.1 |
|
311/88059/U201 |
South Africa |
Kidney Beans |
300 EC |
504 |
1 |
Kidney beans |
0 3 8 22 |
0.65 0.37 0.25 0.12 |
|
311/88869/B541 |
South Africa |
Green beans |
300 EC |
150 |
1 |
Blanched |
0 2 4 6 |
0.06 0.15 0.09 <0.05 |
|
311/88869/B541 |
South Africa |
Green beans |
300 EC |
150 |
1 |
Unblanched |
0 2 4 6 |
0.29 0.34 0.16 0.07 |
Source: Bayer Australia Ltd submission, Baycor 300 Fungicide Spray, file 329-1-619, 21/11/86. South African trials also reported in JMPR.
Residues in beans following application approximating GAP (120 190 g ai/ha or 0.8 1.3´ label rate) were, in rank order, 0.06, 0.15, 0.16, 0.22 and 0.34 mg/kg (PHI 2-4 days). Following application at 240 280 g ai/ha (1.6 1.9´ label rate) residues in beans were 0.10, 0.13, 0.16, 0.24,0.28, 0.50, 0.56 and 0.63 mg/kg (PHI 2-4 days).
Selected animal transfer data
Laying hens
Forty laying hens (10 birds per group) were fed daily rations containing bitertanol at 1, 3 and 100 ppm in the feed for 28 consecutive days.
Residues of bitertanol and 1,2,4-trizole metabolites in poultry tissues after 28 days consecutive feeding at 1, 3 or 100 ppm in feed.
|
Bitertanol residues (mg/kg)(1) |
||||
|
Sample |
Treatment day |
1 ppm |
3 ppm |
100 ppm |
|
Liver |
28 42 56 |
<0.01 |
0.21 |
1.03 0.05 0.04 |
|
Muscle |
28 42 56 |
NA |
0.01 |
0.07 0.07 <0.01 |
|
Fat |
28 42 56 |
NA |
<0.01 |
0.07 <0.01 <0.01 |
|
Eggs |
7 14 21 28 35 42 49 56 |
NA |
<0.01 <0.01 <0.01 <0.01 |
0.07 0.05 0.05 0.11 <0.01 <0.01 <0.01 <0.01 |
(1) 28 DAT samples are composite of 10 animals. 42 and 56 DAT samples are composite of 5 animals.
Bitertanol residues show no preference for accumulation in fat compared to muscle.
Source: Effect of feeding BAYCOR TM to chickens, W. H. Leimkuhler, K. S. Cain, S. L. Whitfield and V. E. Clay, Mobay Chemical Corporation Agricultural Chemicals Division, 27 January 1984.
Lactating cows milk and tissues
Nine lactating dairy cows (3 per group) were fed bitertanol by bolus capsule equivalent to 25, 75 and 250 ppm in the feed for 28 consecutive days. Capsules were prepared for each animal according to individual body weight and were administered as two half doses per day. Based on initial weights of animals the total daily doses correspond to 0.63, 1.88 and 6.25 mg/kg bw/day.
Residues of bitertanol and 1,2,4-triazole metabolites in cow tissues after 28 days consecutive feeding at 25, 75 and 250 ppm in feed.
|
Tissue |
Treatment day |
25 ppm |
75 ppm |
250 ppm |
|
Milk |
0 7 14 21 28 |
NA NA NA NA <0.01, <0.01, 0.01 |
<0.01a 0.09a 0.10a 0.13a 0.07, 0.03, 0.02 |
<0.01a 0.11a 0.19a 0.17a 0.07, 0.03, 0.02 |
|
Fatb |
28 |
0.06 |
0.18 |
1.28 |
|
Muscleb |
28 |
0.06 |
0.09 |
0.44 |
|
Liverb |
28 |
0.78 |
1.91 |
3.65 |
|
Kidneyb |
28 |
0.05 |
0.36 |
1.07 |
acomposite of 3 animals analysed
b highest residue in the three animals shown
Source: Effect of feeding BAYCOR TM to dairy cows, W. H. Leimkuhler, K. S. Cain, S. L. Whitfield and V. E. Clay, Mobay Chemical Corporation Agricultural Chemicals Division, 25 January 1984.
Three lactating dairy cows were fed a diet containing bitertanol at 150 ppm in the diet for 7 days. Full details of the dosing regime and body weights of the animals were not reported.
Residues in milk following dosing at 150 ppm in the diet for 7 days:
|
Day of study |
Skim milk |
Milk fat |
Day of study |
Skim milk |
Milk fat |
|
0 |
<0.01 |
<0.3 |
8 (+1) |
<0.01 |
1.4 |
|
1 |
<0.01 |
0.8 |
9 (+2) |
<0.01 |
0.9 |
|
2 |
<0.01 |
1.4 |
10 (+3) |
<0.01 |
0.3 |
|
3 |
<0.01 |
0.8 |
11 (+4) |
<0.01 |
<0.3 |
|
4 |
<0.01 |
1.6 |
12 (+5) |
<0.01 |
<0.3 |
|
5 |
<0.01 |
2.2 |
13 (+6) |
<0.01 |
<0.3 |
|
6 |
<0.01 |
2.0 |
14 (+7) |
<0.01 |
<0.3 |
Source: PACC meeting November 1989, item 12.5
Residues preferentially accumulate in milk fat, however no data for whole milk were reported. No record of the percentage fat in milk was reported.