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PESTICIDE RESIDUE COMPLIANCE AND SETTING OF PRE HARVEST INTERVALS IN THE FRESH PRODUCE EXPORT PROCESS Global Minor Use Summit Rome , December 2007 Roberto H. González Professor of Entomology University of Chile [email protected]

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PESTICIDE RESIDUE COMPLIANCE AND SETTING OF PRE HARVEST

INTERVALS IN THE FRESH PRODUCE EXPORT PROCESS

Global Minor Use Summit

Rome , December 2007

Roberto H. González Professor of EntomologyUniversity of Chile [email protected]

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Supervised trials.

• Two fold purposes:A) .-Assisting in MRL settings: B) .-Determining pre-harvest intervals in specific

pesticide/crop combinations to set withholding periods to meet specific maximun residue limits.

Supervised trials should be conducted in the country concerned, according to local agricultural conditions and national GAPs.

Extrapolation of residue data could be considered in selected minor crops.

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Variability of residue levels (concentration) on/in different food items of the same crop is an

inevitable condition due to

• a great variety of factors affecting the deposition of pesticides during application on a crop or soil surface and

• the different rates of dissipation processes affecting residues levels in/on the different parts of a plant or plants of the same field.

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DISSIPATION CURVEPe

stic

ide

Res

idue

(mg/

kg)

Preharvest interval (days)

Residue tolerance = 4mg/kgPreharvest interval = 5 days

2 3 4 5 6 7 8 9 10

0 1

2

3

4

5

6

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MRLPHI

Days after application (DAA)

LD

ND

Res

idue

limits

(mg/

kg)

MRL: Max. Residue limit

PHI: Pre harvest interval

LD: Limit of detection

ND: non detectable levelChemical (a.i., formulation), biological and climatic factors, cropphenology

Factors affecting residue decline:

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Factors influencing residue dissipation rates

1.-Formulations.2.-Application factors.3.-Crop and environmental factors.4.-Residue decline factors.

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1-Formulations-Residue trials should be conducted with the

formulation to be marketed (or one of similar type and composition).

-Minor changes are observed among the following pairs: WP-SC; WG-CS; EW-SP

-Major changes: EC and all others (particularly with WP and micro granular formulations).

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The pesticide formulation factor.

Interval days

0 7 14 21 30

100

90

80

70

60

50

40

30

20

0

Pest

icid

eR

esid

ue(%

) Example: tebuconazole in tomatoesApplic. rate 0.25 kg a.i/ha

Waterdispersible

granular (WG)

Wettablepowder (WP)

Formulations used

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0 1 2 3 4

100

90

80

70

60

50

40

30

20

0

Pest

icid

eR

esid

ue(%

)

Interval days

Pirimiphos-methylLettuce

Aplic.rate 280 ppm

Formulations usedECSC

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Degradación de clorpirifos 48 EC y 75 WG en uva de mesa cv. Superior. Ovalle, IV R. Temporada 2003-2004.

2,27

0,26

1,74

0,04 0,02

0,07

0,820,92

y = 3,5527e-0,0995x

R2 = 0,9917

y = 3,9385e-0,1429x

R2 = 0,925

0

0,5

1

1,5

2

2,5

0 5 10 15 20 25 30 35 40

DDA

ppm

75WG48ECExponencial (75WG)Exponencial (48EC)

DAA

Expon.(75WG)Expon,(48EC)

Chlorpyrifos: 48 EC and 75 WG, table grapes, Ovalle, Chile. 2003-2004 Season

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• 2-Application factors: dose, sprayer, number of applications, use of coadyuvants, etc.

• 3-Crop and environmental factors: canopy, crop phenology, and plant growth rate, distance of planting (number of plants/ha), weather conditions

• 4- Dissipation factors: evaporation (heat), wind, rates of pesticide absortion (contact vs. systemic), bio-chemical dissipation factors, etc.

• Soil dissipation factors include moisture at the time of application, irrigation systems, rainfall, etc.

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Disipación de residuos de Golden Prime EW (tebuconazole + kresoxim-metil) en uva de mesa cv . Crimson Seedless. Los Andes, V Región. Temporada 2006-2007.

1,49

1,82

0,91

0,60,5

0,7

0,35

0,090,03

y = 1,6059e-0,0191x

R2 = 0,8969

y = 0,5693e-0,0694x

R2 = 0,962

0

0,2

0,4

0,6

0,8

1

1,2

1,4

1,6

1,8

2

0 7 14 21 28 35 42 49 56 63 70 77

DDA

mg/

kg (p

pm)

TebuconazoleKresoxim-metilExponencial (Tebuconazole)Exponencial (Kresoxim-metil)

Residue decline of tebuconazole+kresoxim-methyl at a high dosage perhectare in table grapes.

Los Andes, Chile. 2006-2007 season .Tebuconazole, persistent fungicide.

DAA

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Disipación de residuos de Golden Prime SC (Tebuconazole + Kresoxim-metil) en uva de mesa cv . Crimson Seedless. Los Andes, V Región. Temporada 2006-2007.

0,62

0,7

0,39

0,250,21

0,28

0,2

0,070,03

y = 0,6522e-0,0185x

R2 = 0,9247

y = 0,2619e-0,0505x

R2 = 0,9712

0

0,1

0,2

0,3

0,4

0,5

0,6

0,7

0,8

0 7 14 21 28 35 42 49 56 63 70 77

DDA

mg/

kg (p

pm)

TebuconazoleKresoxim-metilExponencial (Tebuconazole)Exponencial (Kresoxim-metil)

Residue declination of tebuconazole+kresoxim-methyl at lower dosage perhectare in table grapes.

Los Andes, Chile. 2006-2007 season.

DAA

Exp.Exp.

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Disipación de residuos de imidacloprid en uva de mesa var. Crimson. Los Andes, 5ª Región. Temporada 2005-2006.

y = 1,7606e-0,0364x

R2 = 0,9038

0

0,5

1

1,5

2

2,5

0 10 20 30 40 50 60DDA

mg/

Kg

(ppm

) ppm

Exponencial (ppm)

DAA

EXPONENTIAL (ppm)

Persistent insecticide imidacloprid, table grapes, Los Andes, Chile. 2005-2006 season.

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Comparability of residue data.• -Recurrent discrepancies among trials conducted in

minor crops.• -Pesticide use patterns (dosages and number of

applications). Example mancozeb in potatoes: 5 to 10 applications, 1.5 versus 2.5-3 kg. a.i/hectare.

• -The principle of zoning appears to be used by many national regulatory authorities but trials from outside of their geographic areas would not often be considered as applicable.

• -GAP definition originally set only for pesticide residue purposes has been widely broadened to include a number of other components which do not properly fit whiting the original concept.

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Sampling methods for supervised trials.

• -The best information about the residue behaviour of the pesticide under study would be obtained by the analysis of the entire treated crop.

• -Since this is not practicable, representative samples have to be taken.

• -Valid analytical results can only be obtained if the samples have been properly collected from different plant sites, labelled, dispatched and stored before analysis.

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• Sampling points: all samples must be representative to enable the analytical result to be applied to the entire experimental unit.

• -The greater the number of plants sampled (fruits, foliage, roots, etc), the more representative the sample will be; however, there is a maximum recommended for each plant group (see below)

• -Damaged plant parts (by weather conditions, pests, diseases, birds) should be discarded;

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Sampling of bulb, root and tubervegetables

: 12 bulbs from 12 plants.

Garlic, shallots

: 12 plantsLeeks, bulb onions

: 12 roots (not lessthan a 2 Kg.sample)

Other rootcrops

: 12 tubers (not lessthan a 2 Kg. sample)

Potatoes

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Sampling of fruits

1 Kg.Tree nuts (walnuts, almonds)

12 nutsCoconut

24 fruits units (2 fingers each fromtop)

Bananas

1 Kg from several plot areas.Strawberries, gooseberries.

Same as aboveMisc.fruits, e.g. avocado, guavas, mango, pomegranate, persimmons, kiwifruit, litchi.

12 fruits from several places on 4 individual trees (not less than 2 Kg)

Citrus fruits, pome fruits, largestone fruits

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Sampling of other vegetables

12 earsSweet corn

10 fruits from 10 separateplants

Melons, water melons

12 fruits from 12 plants(sample not less than 2 Kg)

Gherkins, courgettes, squash

12 fruits from 12 separateplants

Cucumber

12 plantsLarge brassica crops(cabbage)

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Sampling of other vegetables

1 KgDried beans, lentils, pulses, etc

1 Kg (fresh green)Beans, peas (fresh)

12 headsGlobe artichoke

12 sticks from 12 separate plantsAsparragus

12 plantsLettuce, endive

24 fruits from small fruitingvarietes, 12 fruits from large sizevarieties. From 12 plants in allcases

Tomatoes, peppers

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Sampling methods

• -At random• -Systematically, e.g., field crops collect

samples in a diagonal “X” pattern• -Samples from fruit trees should be

collected from 3-6 trees, clipping fruits off from inside and outside canopy.

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Sampling at normal harvest time.

• Take samples so as to be representative of typical harvesting practice;

• Avoid taking diseased or undersized cropparts or commodities at a stage when theywould not normally be harvested;

• Take bush or tree fruit samples from allsegments of the plant,high and low,exposedand protected by foliage.

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Warnings• -Avoid taking samples at the beginning or at the

extreme end of plot.• -Take and bag the required weight or units and do

not subsample until the samples are in a clean table or better in the lab facilities.

• -Samples can be transported in an ice box and stored at -20°C until they are sent to the lab.

• Vegetables: take samples from all over the plot (bulb, root and tuber vegetables), excluding at least 1 meter at the edges of the plot and the end of the rows. Adhering soil may have to be removed.

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•-Do not trim except for the removal of obviously decomposed or withered leaves•-Label sample bags: crop, variety, date, or a code number (to indicate treatment, application methods, coverage, climatic events, etc).

Warnings, cont´d.

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Residue data extrapolation• -Most specialty minor crops do not have large

enough production scales for pesticide manufacturers to invest in residue trial studies.

• -It is therefore convenient to extrapolate data obtained from other closely related crops to avoiding possible duplication of supervised trials. Data should be obtained as possible from other crops pertaining to the same group.

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Can residue results be extrapolated to another crop?

• Provided that supervised trials are conducted on a representative commodity (of a particular crop group such as bulb vegetables, fruiting vegetables, flower heads such brassicas, brussel sprouts, etc) and in fairly close phenological stages, it could be possible to extrapolate results.

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Examples…a) citrus groups: for highly pesticides (OP´s,

carbamates), lemon fruits retain more residues than other family fruits.

b) Berry groups: blueberries have a different pattern of the residue retention and dissipation than other small fruits.

c) Data from strawberries can be extrapolated to blackberries.

d) Cauliflower to broccolie) Lettuce, depending on cultivars.f) Fresh herbs and spices: a pragmatic solution is to

apply results set for similar major crops: extrapolation from other leaf crops (lettuce)

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• Application: Grape bunch closure. December, 2000.• Teldor 50 WP: 1.2 kg commercial product/ha (600 g i.a/ha),

1200L/ha

Disipación de residuos de fenhexamid (*) en uva de mesa. Buin. R.M 2000-2001

y = 0,6294e-0,0544x

R2 = 0,9847

00,10,20,30,40,50,60,7

0 10 20 30 40 50 60

DDA

ppm ppm

Exponencial (ppm)

Residue dissipation of the fungicide fenhexamid in table grapes, Buin, Chile. 2000-2001

DAA

Exponential (ppm)

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Disipación de residuos de dicofol en uva de mesa, Padre Hurtado. R.M 1993

y = -0,0389Ln(x) + 0,9842R2 = 0,9785

0

0,2

0,4

0,6

0,8

1

1,2

0 5 10 15 20 25 30

DDA

ppm ppm

Logarítmica (ppm)

Extended persistence of dicofol residues in table grapes.

Log. (ppm)

DAA

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Abamectin in nectarines (Supervised trials in two close locations).

Exponential(A.J)Exponential(Col)

DAA

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Residue decline of azinphos methyl 50 WP(100g c.p/100L) in peachesand nectarines.

DAA

Peaches

Nectarines

Exponential(peach)

Exponential(nect.)

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Selected references

• Codex Alimentarius Commission. 2000-Pesticide Residues in Food: Methods of analysis and sampling. Vol.2ª, Part. 1, 91 p.

• FAO. 1997. FAO Manual on the submissionand evaluation of pesticide residues data forthe estimation of maximun residue levels in food and feed, Rome, 158 p.

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• FAO 2007. Requests and Comments on the proposals for “bulb vegetables” and “fruiting vegetables”, Codex Alimentarius Commission, CL 2007/36-PR. Sept.2007,25p.