Residues and Contaminants in Fresh Fruit from Conventional Cultivation, 2016
Ein Bericht aus unserem Laboralltag
Ellen Scherbaum, Kathi Hacker, Alexander Lemke
In 2016 a total of 853 samples of fresh fruit from conventional culti-vation were analyzed by CVUA Stuttgart for residues of over 700 different pesticides, pesticide metabolites, and contaminants. In all, 820 of these samples (96 %) contained residues from a total of 188 different pesticide substances (compared to 179 substances in 2015; 192 in 2014; 193 in 2013; 197 in 2012; and 184 in 2011). A total of 5,481 residues were found (according to the legal definition; see also Annex 4). There were exceedances of the maximum resi-due level (MRL) in 59 fruit samples (6.9 %). The rate of violations was similar to that of the previous year (5.2 % in 2015; 11 % in 2014; 4.8 % in 2013; 4.5 % in 2012; and 3.6 % in 2011). The rate of ex-ceedances for chlorate lay at 2.1 % of the samples (1.6 % in 2015; 6.9 % in 2014), whereby eight of these samples (0.9 %) were only slightly over the limit (< 0.02 mg/kg). Fortunately, the rate from 2015 remained steady, and is significantly lower than that for vegetables.
Expansion of the investigative spectrum for all samples:
The QuPPe-method (see also http://quppe.eu), was again used in 2016 to routinely investigate all samples for very polar substances that couldn’t be detected with the QuEChERS multi-residue method. Typical agents in this group include the fungicides fosetyl and phosphonic acid, which are often used in fruit cultivation, the herbicide chlorate, and the contaminant perchlorate (see Info Boxes on chlorate, phosphonic acid, and perchlorate).
Detailed results:
Table 1 gives an overview of all 853 fruit samples by country of origin.
Fresh Fruit |
Domestic Samples
|
Other EU Countries
|
Third Countries
|
Unknown Origin
|
Total Samples
|
---|---|---|---|---|---|
No. of Samples |
291
|
277
|
269
|
16
|
853
|
With residues |
280 (96 %)
|
266 (96 %)
|
259 (96 %)
|
15 (94 %)
|
820 (96 %)
|
Exceedances of MRL |
11 (3.8 %)
|
15 (5.4 %)
|
31 (12 %)
|
2
|
59 (6.9 %)
|
Ave. quantity of pesticide (mg/kg) |
3.1
|
2.7
|
3.0
|
1.6
|
2.9
|
Ave. quantity of pesticide, excluding fosetyl (sum) (mg/kg)* |
0.37
|
0.72
|
0.82
|
0.53
|
0.63
|
Ave. quantity of pesticide, excluding fosetyl (sum), surface treatment agents, and bromide (mg/kg)* |
0.37
|
0.46
|
0.47
|
0.37
|
0.43
|
Ave. no. substances per sample |
7.1
|
6.1
|
6.1
|
5.3
|
6.4
|
The samples came from 39 different countries, with most originating in Germany (291), Spain (169), Italy (80), South Africa (47), Turkey (43) and Brazil (25). The highest rates of MRL exceedances were in samples from Turkey (19 %) and Brazil (20 %).
In 2016, almost all of fruit samples (96 % of 820) contained residues. According to the official definition of residues (see Annex 4), 188 different pesticide substances were detected; when all metabolites and contaminants are included, this comprises 247 individual substances. An average of 6.4 different substances was detected per sample. Excluding fosetyl (sum), bromide, and the surface treatment agents thiabendazole, imazalil and ortho-phenylphenol, which are often found on the peel of citrus fruits and to some extent on stone and exotic fruits, the average amount of pesticide residues was 0.43 mg/kg.
Table 2 provides an overview of the analytical results for the differ-ent fruit categories.
Type of Fruit |
No. of Samples
|
Samples with Residues
|
Samples with Multiple Residues
|
Samples > MRL
|
No. Findings
> MRL |
Substances exceeding the MRL* |
---|---|---|---|---|---|---|
Berry |
261
|
257 (99 %)
|
251 (96 %)
|
19 (7.3 %)
|
23
|
Fosetyl, sum (5x); Chlorate (4x); Spinosad (2x); Ametoctradin (2x); Vinclozolin; Dimethoate, sum; Chlorpropham; Fenazaquin; Captan; Folpet; Procymidone; Tebufenozide; Methoxyfenozide; Trimethylsulfonium cation |
Pome fruit |
150
|
148 (99 %)
|
146 (97 %)
|
2 (1.3 %)
|
2
|
Chlormequat; Diphenylamine |
Stone fruit |
161
|
159 (99 %)
|
155 (96 %)
|
13 (8.1 %)
|
15
|
Chlorate (6x); Fosetyl, sum (5x); Acetamiprid; Dimethoate, sum; Carbendazim, sum; Procymidone |
Citrus fuit |
106
|
106 (100 %)
|
105 (99 %)
|
6 (5.7 %)
|
6
|
Chlorate (4x); Dicloran; Lambda-Cyhalothrin |
Exotic fruit |
175
|
150 (86 %)
|
113 (65 %)
|
19 (11 %)
|
22
|
Fosetyl, sum (7x); Chlorate (4x); Acetamiprid (2x); Prochloraz, sum (2x); Ethephon; Chlorpyrifos; Diuron; Difenoconazole; Flutriafol; Cyfluthrin; Cyprodinil |
Total |
853
|
820 (96 %)
|
770 (90 %)
|
59 (6.9 %)
|
|
Presentation of Results for Specific Types of Fruit
Berries contained an average of 7.5 different substances and 0.6 mg pesticide per kg (average quantity of pesticide excluding fosetyl (sum), surface treatment agents and bromide) (Table 3). These sensitive fruits are vulnerable to mold, especially in damp weather.
Two samples of currants from Germany were especially notable in 2016. One sample contained four substances (captan, difenoconazole, folpet, and tebufenozide), and the other, seven (dimethoate (sum), fenazaquin, folpet, procymidone, tebufenozide, triflumuron, and vinclozolin), that were higher than the MRL; a total of 19 and 25 different substances were detected in the samples, respectively. Both samples came from the same producer. Fortunately, such highly contaminated samples are absolute exceptions.
Type of Fruit |
No. of Samples
|
Samples with Residues
|
Samples with Multiple Residues
|
Samples > MRL
|
Substances exceeding the MRL** |
---|---|---|---|---|---|
Blackberry |
4*
|
4
|
4
|
|
|
Strawberry |
78
|
77 (99 %)
|
76 (97 %)
|
6 (7.7 %)
|
Chlorate (3x); Spinosad (2x); Chlorpropham |
Blueberry |
18
|
17 (94 %)
|
16 (89 %)
|
3 (17 %)
|
Fosetyl, sum (3x) |
Raspberry |
15
|
15 (100 %)
|
15 (100 %)
|
|
|
Currant |
34
|
32 (94 %)
|
31 (91 %)
|
4 (12 %)
|
Ametoctradin; Dimethoate, sum; Fenazaquin; Fosetyl, sum; Methoxyfenozide; Procymidone; Tebufenozide; Vinclozolin |
Jostaberry |
1
|
1
|
1
|
|
|
Cranberry |
2
|
2
|
0
|
|
|
Gooseberry |
10
|
10 (100 %)
|
10 (100 %)
|
2 (20 %)
|
Ametoctradin; Fosetyl, sum |
Table Grape |
99
|
99 (100 %)
|
98 (99 %)
|
4 (4 %)
|
Captan; Chlorate; Folpet; Trimethylsulfonium cation |
Total Berries |
261
|
257 (99 %)
|
251 (96 %)
|
19 (7.3 %)
|
Pome fruits contained an average of 8.3 different substances and 0.31 mg pesticide per kg (average quantity of pesticide excluding fosetyl (sum), surface treatment agents and bromide). The number of different substances per sample was slightly higher than with berries; the amount of residues, however, was only half as high (see Table 4).
Type of Fruit |
No. of Samples
|
Samples with Multiple Residues
|
Samples with Multiple Residues
|
Samples > MRL
|
Substances exceeding the MRL |
---|---|---|---|---|---|
Apple |
95
|
93 (98 %)
|
93 (98 %)
|
1 (1.1 %)
|
Diphenylamine |
Pear |
54
|
54 (100 %)
|
52 (96 %)
|
1 (1.9 %)
|
Chlormequat |
Quince |
1*
|
1
|
1
|
|
|
Sum Stone Fruits |
150
|
148 (99 %)
|
146 (97 %)
|
2 (1.3%)
|
One sample of Turkish pears contained chlorpyrifos in the amount of 0.20 mg/kg. The European Food Safety Authority (EFSA) published new toxicological reference values in April 2014, deriving an acute reference dose (ARfD) for Chlorpyrifos of 0.005 mg/kg bodyweight [4]. Applying EFSA’s EU-based PRIMo-Model for young children, consumption of the above-mentioned pear sample with its chlorpyrifos residues of 0.20 mg/kg would mean an intake amount of 0.0182 mg/kg bodyweight (variability factor 7). That would exhaust the ARfD by 364 %, although the MRL of 0.5 mg/kg was not exceeded. As a result, the sample was judged to be unsafe.
Info box
Acute Reference Dose (ARfD)
For the evaluation of pesticides that have a high, acute toxicity and that can cause health damage after just a single or short-term intake, the Acceptable Daily Intake (ADI) value is appropriate to only a limited extent. Since the ADI is derived from long-term studies, it is possibly inadequate as a measure of acute risk from residues in food. Therefore, in addition to the ADI value, a further exposure limit has been established, the so-called acute reference dose (ARfD). The World Health Organization defined the ARfD as the amount of a substance one can consume over the period of one day or in one meal without resulting in any discernible health risk. Other than for the ADI, the ARfD value is not determined for every pesticide, but only for such substances that, when taken in sufficient quantities, could cause damage to one’s health even after just one exposure.
EFSA calculation model Pesticide Residue Intake Model “PRIMo” - rev.2_0
Stone fruits contained an average of 6.3 different substances and 0.26 mg pesticide per kg (average quantity of pesticide excluding fosetyl (sum), surface treatment agents and bromide); see Table 5.
Type of Fruit | No. of Samples | Samples with Residues Rückständen | Samples with Multiple Residues | Samples > MRL | Substances exceeding the MRL** |
---|---|---|---|---|---|
Apricot | 25 | 24 (96 %) | 24 (96 %) | 2 (8 %) | Carbendazim, sum; Fosetyl, sum |
Avocado | 3 | 3* | 2 | ||
Mirabelle | 3 | 3 | 3 | ||
Nectarine | 20 | 20 (100 %) | 20 (100 %) | 1 (5 %) | Fosetyl, sum |
Peach | 17 | 17 (100 %) | 17 (100 %) | 1 (5.9 %) | Chlorate |
Plim | 61 | 60 (98 %) | 58 (95 %) | 3 (4.9 %) | Acetamiprid; Chlorate; Fosetyl, sum |
Sweet Cherry | 32 | 32 (100 %) | 31 (97 %) | 6 (19 %) | Chlorate (4x); Fosetyl, sum (2x); Dimethoate, sum; Procymidone |
TOTAL Stone Fruits |
161 | 159 (99 %) | 155 (96 %) | 13 (8.1 %) |
One sample of German cherries contained dimethoate (sum of omethoate and dimethoate), in the amount of 0.82 mg/kg sample. The MRL is 0.2 mg/kg. Applying EFSA’s EU-based PRIMo-Model for young children exhausts the ARfD by 276 % [3]. This sample was also determined to be unsafe.
Citrus fruit contained an average of seven different substances and 0.48 mg pesticide per kg (average quantity of pesticide excluding fosetyl (sum), surface treatment agents and bromide); see Table 6.
Type of Fruit |
No. of Samples
|
Samples with Residues
|
Samples with Multiple Residues
|
Samples > MRL
|
Substances exceeding the MRL |
---|---|---|---|---|---|
Clementine |
18
|
18 (100 %)
|
18 (100 %)
|
|
|
Grapefruit |
24
|
24 (100 %)
|
24 (100 %)
|
1 (4.2 %)
|
Chlorate |
Kumquat |
2
|
2*
|
1
|
1 (50 %)
|
Lambda-Cyhalothrin |
Lime |
13
|
13 (100 %)
|
13 (100 %)
|
2 (15 %)
|
Chlorate (2x) |
Mandarine |
1
|
1
|
1
|
|
|
Orange |
14
|
14 (100 %)
|
14 (100 %)
|
|
|
Pomelo |
8
|
8 (100 %)
|
8 (100 %)
|
1 (13 %)
|
Dicloran |
Satsumas |
3
|
3
|
3
|
|
|
Ugli |
1
|
1
|
1
|
|
|
Lemon |
22
|
22 (100 %)
|
22 (100 %)
|
1 (4.5 %)
|
Chlorate |
Total Citrus Fruits |
106
|
106 (100 %)
|
105 (99 %)
|
6 (5.7 %)
|
Chlorate was the culprit in four cases of MRL exceedances in citrus fruits. A sample of kumquat from Spain contained the insecticide lambda-cyhalothrin in excessive amounts, and one sample of Chinese pomelo contained too much dicloran. According to reports, the fungicide dicloran is used in China to protect the peel of fruits from damage and spots.
Exotic Fruits had the highest rate of violations of all the fruit groups, at 11 %. Of the 175 analyzed samples, 19 contained residues above the MRL in 2016. Pomegranates from Turkey and passionfruit from Colombia were especially conspicuous. The MRL for fosetyl (sum) in exotic fruits is comparatively low, at 2.0 mg/kg; a total of seven samples were above this limit (see Table 7).
Type of Fruit |
No. of Sample
|
Samples with Residues
|
Samples with Multiple Residues
|
Samples > MRL
|
Substances exceeding the MRL** |
---|---|---|---|---|---|
Pineapple |
17
|
17 (100 %)
|
17 (100 %)
|
4 (15 %)
|
Chlorate; Chlorpyrifos; Diuron; Prochloraz, sum |
Bananea |
6
|
6 (100 %)
|
5 (83 %)
|
|
|
Cherimoya |
1*
|
1
|
0
|
|
|
Date |
1
|
1
|
0
|
|
|
Fig |
11
|
5 (46 %)
|
0
|
|
|
Pomegranate |
17
|
17 (100 %)
|
15 (88 %)
|
5 (29 %)
|
Acetamiprid (2x); Fosetyl, sum (2x); Cyfluthrin; Cyprodinil; Prochloraz, sum |
Khaki |
20
|
14 (70 %)
|
9 (45 %)
|
2 (10 %)
|
Chlorate (2x) |
Prickly Pear |
2
|
1
|
0
|
|
|
Cape gooseberry |
1
|
1
|
1
|
|
|
Carambola |
3
|
3
|
3
|
|
|
Kiwi |
27
|
26 (96 %)
|
19 (70 %)
|
|
|
Litchi |
4
|
1
|
1
|
|
|
Mango |
24
|
22 (92 %)
|
17 (71 %)
|
3 (13 %)
|
Ethephon; Flutriafol; Fosetyl, sum |
Maracuja |
6
|
6 (100 %)
|
6 (100 %)
|
4 (67 %)
|
Fosetyl, sum (3x); Chlorate; Difenoconazole |
Nashi pear |
2
|
2
|
2
|
|
|
Papaya |
7
|
6 (86 %)
|
5 (71 %)
|
1 (14 %)
|
Fosetyl, Summe |
Pitahaya |
1
|
1
|
1
|
|
|
Rhubarb |
15
|
10 (67 %)
|
2 (13 %)
|
|
|
Total Exotic fruit |
175
|
150 (86 %)
|
113 (65 %)
|
19 (11 %)
|
Multiple Residues
Residues from multiple pesticides were also detected in a large number of fruit samples in 2016: 770 samples (90 %) had multiple residues (89 % in 2015; 95 % in 2014; 85 % in 2013; 83 % in 2012). Illustration 1 depicts the multiple residues in various types of fruit in 2016.
The residue findings are strongly dependent on the type of sample and their country of origin. Since the particular focus and risk-oriented questions are different each year, the results from one year cannot be seen as representative of the general situation.
Illustration 1: Multiple residues in various types of fruit (CVUAS, 2016)
Nevertheless, certain trends can be noted, especially when the residue situation is observed over a period of several years. Illustrations 2 and 3 show a comparison of 5 years.
The number of analyzed substances has been continually adjusted and expanded over the past five years. While an average of about 600 pesticides were analyzed in 2012, this number rose to 648 substances in 2016 (pursuant to the legal residue definitions; see Annex 4).
Illustration 2: Average number of different pesticide substances per sample in various types of fruit (CVUAS 2012-2016; residue definitions according to legal stand in 2016)
Expansion of the analyses and a reduction in the residue amounts as a result of post-harvest treatments (washing, waxing, etc.) have had an opposite effect on the number of pesticides that are detectable. As Illustration 2 shows, a slight increase in the number of detectable substances can be observed for the years 2012 to 2016.
Exotic fruit has the best record, with an average of 2.8 substances per sample over the five years. Stone fruits lie in the middle, at 5.7 per sample. Berries and citrus fruits contained an average of 6.7 and 6.5 respectively, and pome fruit had the highest average, at 7.3 substances per sample over the years, increasing from 6.1 in 2012 to 8.3 in 2016. When making comparisons of the number of pesticide substances used, one must consider that the individual cultures are grown in different climate zones, and are thus exposed to different degrees of pressure from pests. It is therefore necessary to take individual, often different measures of plant protection.
Illustration 3: Average amount of pesticide residues (excluding surface treatment agents, bromide and fosetyl (sum)) in different types of fruit (CVUAS 2012-2016; residue definitions are according to legal stand in 2016)
Illustration 3 shows the average amount of pesticide residues (excluding surface treatment agents, bromide and fosetyl (sum)). The exotic fruits have the best record over the five years here as well, with an average of 0.25 mg/kg of fruit. This year, however, there was a significant jump, mainly as a result of four extremely high findings of prochloraz in a pomegranate from Turkey, a mango from Peru and two pineapples from Ghana, where this fungicide is assumed to be used in post-harvest treatments. Without these four findings the average amount of pesticide in exotic fruit for 2016 would be 0.31 mg/kg. With an average of 0.60 mg/kg, the berries were again the fruit with the highest amount of pesticides in 2016, compared to the other fruit groups.
Substances with special features:
1. Chlorate
The presence of chlorate residues in plant-based foods can have causes other than its application as an herbicide (see Info Box). In fruit, however, chlorate findings play a very minor role in comparison to vegetables (see Illustration 4).
Illustration 4: Chlorate findings above the MRL (> 0.01 mg/kg): a comparison of conven-tional fruit and vegetables
Info Box
Chlorate
Chlorates are effective as both herbicides and biocides. Since 2008, however, chlorate is no longer authorized for use as a pesticide in the EU. Sodium chlorate may also no longer be used in biocide products.
The definition for „pesticide residues“ in Regulation (EC) Nr. 396/2005 also encompasses residues from pesticidal substances in food (including substances no longer authorized) that have pathways other than from the use of plant protectors (so-called dual-use substances). Chlorate, as a substance that is no longer authorized, is thereby covered by the EU-wide valid default MRL of 0.01 mg/kg, in accordance with Reg. (EC) Nr. 396/2005. The presence of chlorate in food can result not only from its use as a pesticide, but also due to environmental pollution (contaminated rain- or irrigation water and soil), or as a residual of food production techniques, including methods used in farming, processing, preparation, or treatment. The application of biocides, from which chlorate can result, is another possible source of contamination. In general, chlorate can be formed as a by-product of the disinfection of drinking/ industrial water with chlorine gas, hypochlorite, or chlorine dioxide. However, no limit value for chlorate in drinking water has been established by the drinking water ordinance. Chlorate inhibits, reversibly, the intake of iodine into the thyroid gland and can cause unwanted health effects, especially in sensitive people such as children, pregnant women, or people with thyroid dysfunction. In addition to affecting thyroid function, chlorate can also damage the erythrocytes (formation of methaemoglobin, haemolysis).
The member states are carrying out a monitoring program to determine the degree of food and drinking water contamination , in order to provide data for a toxicological evaluation by the European Food Safety Authority (EFSA). Specific residue MRLs will then be established based on this information.
2. Phosphonic Acid
The investigations into fosetyl (sum of fosetyl and phosphonic acid) were continued in 2016. Phosphonic acid residues can result from the usage of the fungicidal plant protectors fosetyl and phosphonic acid (allowed in Germany in fruit and vegetable farming, such as lettuce, cucumbers, tomatoes, strawberries, etc.), as well as from the earlier usage of plant strengtheners (so-called leaf fertilizers). With the EU-wide categorization of phosphonic acid as a fungicide, these applications are no longer possible. A legal maximum has been determined for the sum of fosetyl and phosphonic acid, as well as their salts. Fully 56 % (481 samples) of all the analyzed fruit samples were detected with phosphonic acid, calculated as fosetyl (sum) in amounts up to 86.2 mg/kg. Violations occurred in 17 samples (2 %) due to exceedances of the maximum for fosetyl, sum (see Annex 1). The average rate of pesticide per sample is strongly influenced by the comparatively high average amount of fosetyl residues. Therefore, Table 1 presents the average rates of pesticides per sample both with and without fosetyl (sum).
Info Box
Phosphonic Acid and Fosetyl
Both fosetyl and phosphonic acid are fungicides that are permitted for use in the EU, and fall under the applications area of Reg. (EC) No. 396/2005, regardless of their path of entry.
In addition to the use of a fungicide, another feasible means of exposure could have been via leaf fertilizers that contained phosphonates (salts of phosphonic acid). The “new” categorization of phosphonic acids as a fungicide precludes this application, however. There are some indications that plants retain the phosphonic acids, and only eliminate them over a period of some years.
In Germany the only fruits for which the use of fosetyl and phosphonic acids (as phosphonates) is permitted are strawberries, blackberries and grapes. An evaluation of the German-grown fruit samples from 2014 to 2016 shows no reduction in the amounts detected, not even in apples, for which no authorization exists.
Illustration 5: Phosphonic acid in samples from Germany; average amount from all ana-lyzed samples
As Illustration 5 also shows, the amount of phosphonic acid used in table grapes was much greater in 2016, as the wet weather necessitated special protection from fungal diseases.
3. Perchlorate
Perchlorates are the salts of perchloric acid. They are generally soluble in water, and exist permanently in the environment. Their occurrence is either anthropogenic (caused by humans) or natural, existing in mineral deposits. Perchlorate is also formed as a result of oxidative processes in the atmosphere, and deposits itself onto dust particles. The industrial use of perchlorates is extensive and diverse: they are used in the metal processing industry, in paper finishing, as a diuretic, as an oxidant, as well as an explosive and incendiary device. A further mode of entry could be the use of Chile saltpeter as fertilizer. This fertilizer is extracted mainly from natural deposits found in the Atacama Desert. Perchlorate is concentrated in such dry areas because it can’t get into the water cycle where it could be slowly degraded by microorganisms [5]. In the European Union perchlorates are currently neither authorized for use as a plant protectant nor as a biocide. Perchlorate findings, therefore, fall under the regulations for contaminants, which contain a general minimization imperative for foreign substances in food, as a preventative measure for protection of consumers [6].
Approximately six to eight percent of all conventional fruit samples (2,732 samples were analyzed from 2013 to 2016) contained perchlorate, albeit in very small concentrations. Only 0.3 % of the samples from 2016 had amounts greater than 0.1 mg/kg: one sample of cherries from Turkey contained 0.98 mg/kg, a grapefruit sample from Spain had 0.19 mg/kg, and a sample of table grapes from Chile had 0.12 mg/kg perchlorate.
Illustration 6: Percentage of conventional fruit samples contaminated with perchlorate, by amount of perchlorate (CVUAS 2013–2016)
Unauthorized Use of Pesticides
Samples coming from Germany are also tested as to whether the detected substances are authorized both for use in general, and for the specific culture. The most frequent discrepancies were in currants (7 samples) and apples (6 samples). One sample of currants was detected with 8 unauthorized substances, including procymidone, triflumuron, and vinclozolin, which are banned for all cultures.
Werden die Höchstmengen eingehalten, so sind diese Waren verkehrsfähig. Der Sachverhalt wird jedoch von den für den Pflanzenschutz zuständigen Stellen weiter verfolgt.
If the MRLs are adhered to, these goods are marketable. The situation will be followed, nevertheless, by those responsible for monitoring plant protection measures. Findings of fosetyl, sum, (including phosphonic acid) were an issue last year, as this substance is only permitted for use in strawberries, blackberries and grapes, but was also detected in other types of fruit. In 2016 fosetyl, sum, was detected in 116 samples from Germany for which no authorization has been given (see Table 8).
Type of Fruit | No. of Detections |
---|---|
Raspberry | 8 |
Currant | 16 |
Gooseberry | 6 |
Blueberry | 4 |
Apple | 57 |
Pear | 12 |
Apricot | 1 |
Plum | 4 |
Sweet Cherry | 7 |
Rhubarb | 1 |
These findings from 2016 were not yet judged as „unauthorized applications“, because these substances remain in the plants and could be the result of an earlier application of „leaf fertilizer“, etc. (see also Info Box).
Residues from unauthorized substances detected in fruit samples from Germany are presented in Table 9.
Type of Fruit |
No. of Samples from Germany
|
Samples w/ Unauthorized Substances
|
Unauthorized Substances* |
---|---|---|---|
Berry |
126
|
12 (10 %)
|
Difenoconazole (4x); Folpet (4x); Captan (3x); Tebufenozide (2x); Ametoctradin (2x); Vinclozolin; Dimethoate, sum; Fenoxycarb; Triflumuron; Cyflufenamid; Dithianon; Fenazaquin; Procymidon; Methoxyfenozide; Abamectin, sum; Fluopyram |
Pome fruit |
96
|
6 (6 %)
|
Folpet (5x); Fenoxycarb |
Stone fruit |
55
|
4 (7 %)
|
Captan (3x); Procymidone |
Citrus fruit |
0
|
0
|
|
Exotic fruit** |
14
|
0
|
|
Sum |
291
|
22 (7.6 %)
|
Info Box
Indication Authorization (§ 12 (1) Plant Protection Law)
The indication authorization has been valid for all pesticides since 1 July, 2001. It states that the substances in question are authorized, but may be utilized only within the scope of application stipulated in the Federal Office of Consumer Protection and Food Safety‘s (BVL) authorization database (Food Safety‘s (BVL) authorization database).
Furthermore, the responsible authorities of the German states can, in accordance with § 22 of the plant protection law, determine certain conditions under which permission can be given in individual cases for the use of authorized pesticides in other areas. The Landwirtschaftliches Technologiezentrum Augustenberg (Agricultural Technology Center Augustenberg) is the responsible authority In Baden-Württemberg (http://www.ltz-bw.de/pb/,Lde/Startseite/Arbeitsfelder/Zulassungen+_+Genehmigungen). This permission is only valid for the applicant operator and the specified cultivated area.
Annex 1 lists the MRL exceedances in conventionally produced fresh fruits; Annexes 2 and 3 show the frequency distribution of the detected substances.
Photo credits:
CVUA Stuttgart, pesticide laboratory
References:
[2] Entscheidung der Kommission vom 10. November 2008 über die Nichtaufnahme von Chlorat in Anhang I der RL 91/414/EWG des Rates und die Aufhebung der Zulassungen für Pflanzenschutzmittel mit diesem Stoff (ABl. L307/7 vom 18.11.2008)
[3] Conclusion on the peer review of the pesticide risk assessment of confirmatory data submitted for the active substance dimethoate: EFSA Journal 2013;11(7):3233
[4] Conclusion on the peer review of the pesticide human health risk assessment of the active substance chlorpyrifos, EFSA Journal 2014;12(4):3640
[5] Bericht des Umweltbundesamtes vom 18.09.2012 über das Vorkommen und die Verwendung von Perchloraten sowie deren wesentliche Eintragspfade in Lebensmittel
[6] Statement as regards the presence of perchlorate in food on 10 March 2015 (updated 23 June 2015)
Annexes
Substances | HöchstmengenüberschreitungFruits with MRL Exceedancesen bei |
---|---|
Acetamiprid |
Pomegranate (Turkey, not specified); Plum (Turkey) |
Ametoctradin |
Gooseberry (Germany); Currant (Germany) |
Captan |
Grapes (Germany) |
Carbendazim, sum |
Apricot (Turkey) |
Chlorate |
Strawberry (Spain 2x, Italy); Grapefruit (USA); Plum (Chile); Passion fruit (South Africa); Cherry (Turkey 2x, Italy 2x); Kaki (South Africa, not specified); Peach (Spain); Pineapple (Costa Rica); Lemon (Spain); Lime (Brazil 2x); Grapes (Brazil) |
Chlormequat |
Pear (Spain) |
Chlorpropham |
Strawberry (Italy) |
Chlorpyrifos |
Pineapple (Costa Rica) |
Cyfluthrin |
Pomegranate (not specified) |
Cyprodinil |
Pomegranate (South Africa) |
Dicloran |
Pomelo (China) |
Difenoconazole |
Passion fruit (Colombia) |
Dimethoate, sum |
Currant (Germany); Cherry (Germany) |
Diphenylamine |
Apple (Greece) |
Diuron |
Pineapple (Ghana) |
Ethephon |
Mango (Peru) |
Fenazaquin |
Currant (Germany) |
Flutriafol |
Mango (Brazil) |
Folpet |
Grapes (Germany) |
Fosetyl, sum |
Pomegranate (Turkey 2x); Passion fruit (Colombia 2x, South Africa); Blueberry (Morocco, Germany, Argentina); Nectarine (Chile); Papaya (Brazil); Cherry (Turkey, Italy); Apricot (Italy); Currant (Germany); Gooseberry (Germany); Plum (Germany); Mango (Spain) |
lambda-Cyhalothrin |
Kumquat (Spain) |
Methoxyfenozide |
Currant (Germany) |
Prochloraz, sum |
Pomegranate (Turkey); Pineapple (Ghana) |
Procymidone |
Currant (Germany); Cherry (Germany) |
Spinosad |
Strawberry (Spain, Italy) |
Tebufenozide |
Currant (Germany) |
Trimethylsulfonium cation |
Grapes (Chile) |
Vinclozolin |
Currant (Germany) |
Annex 2: Frequency of detection of the most important substances* for fresh fruit, by type of fruit, as percentage all analyzed samples (CVUAS, 2016nlage 2: Nachweishäufigkeit der wichtigsten Wirkstoffe* für Frischobst, sowie aufgeschlüsselt nach Obstart, in Prozent der untersuchten Proben (CVUAS 2016)
Pesticides and Metabolites |
Number of Findings
|
mg/kg
|
|||||||
---|---|---|---|---|---|---|---|---|---|
< 0.01
|
< 0.05
|
< 0.2
|
< 1
|
< 5
|
< 20
|
≥ 20
|
Max.
|
||
Fosetyl, sum |
481
|
0
|
1
|
69
|
135
|
230
|
28
|
18
|
86.2
|
Fludioxonil |
256
|
94
|
48
|
51
|
48
|
14
|
1
|
0
|
14.2
|
Cyprodinil |
238
|
112
|
44
|
48
|
30
|
4
|
0
|
0
|
1.2
|
Boscalid |
212
|
82
|
62
|
38
|
27
|
3
|
0
|
0
|
1.8
|
Trifloxystrobin |
177
|
79
|
69
|
23
|
5
|
1
|
0
|
0
|
1.5
|
Captan |
140
|
30
|
50
|
45
|
13
|
2
|
0
|
0
|
1.7
|
Myclobutanil |
139
|
85
|
41
|
12
|
1
|
0
|
0
|
0
|
0.2
|
Chlorantraniliprole |
131
|
103
|
27
|
1
|
0
|
0
|
0
|
0
|
0.09
|
Pyraclostrobin |
126
|
69
|
40
|
14
|
3
|
0
|
0
|
0
|
0.3
|
Tebuconazole |
121
|
68
|
29
|
18
|
6
|
0
|
0
|
0
|
0.68
|
Chlorpyrifos |
118
|
79
|
27
|
8
|
4
|
0
|
0
|
0
|
0.3
|
Fluopyram |
111
|
51
|
36
|
20
|
3
|
1
|
0
|
0
|
1.3
|
Imazalil |
105
|
14
|
7
|
13
|
25
|
46
|
0
|
0
|
4.5
|
Acetamiprid |
103
|
50
|
35
|
18
|
0
|
0
|
0
|
0
|
0.15
|
Dithianon |
103
|
17
|
43
|
34
|
8
|
1
|
0
|
0
|
1.2
|
Pyrimethanil |
103
|
45
|
16
|
10
|
21
|
11
|
0
|
0
|
5.2
|
Imidacloprid |
99
|
65
|
29
|
2
|
3
|
0
|
0
|
0
|
0.45
|
Thiacloprid |
99
|
58
|
31
|
9
|
1
|
0
|
0
|
0
|
0.36
|
Pirimicarb, sum |
98
|
55
|
28
|
15
|
0
|
0
|
0
|
0
|
0.18
|
Cyprodinil metabolite CGA 304075 |
93
|
56
|
20
|
14
|
3
|
0
|
0
|
0
|
0.24
|
Fenhexamid |
89
|
24
|
17
|
21
|
22
|
5
|
0
|
0
|
4.1
|
Difenoconazole |
86
|
62
|
18
|
5
|
1
|
0
|
0
|
0
|
0.1
|
Spinosad |
82
|
46
|
22
|
11
|
3
|
0
|
0
|
0
|
0.49
|
Penconazole |
77
|
62
|
13
|
2
|
0
|
0
|
0
|
0
|
0.062
|
Thiabendazole |
75
|
22
|
10
|
13
|
22
|
8
|
0
|
0
|
3.2
|
lambda-Cyhalothrin |
72
|
42
|
24
|
6
|
0
|
0
|
0
|
0
|
0.095
|
Iprodione |
71
|
36
|
11
|
8
|
11
|
5
|
0
|
0
|
2.4
|
Azoxystrobin |
69
|
39
|
10
|
16
|
4
|
0
|
0
|
0
|
0.58
|
Carbendazim, sum |
69
|
50
|
15
|
3
|
1
|
0
|
0
|
0
|
0.26
|
Spirotetramat, sum |
66
|
26
|
28
|
10
|
2
|
0
|
0
|
0
|
0.33
|
Dodine |
57
|
52
|
2
|
3
|
0
|
0
|
0
|
0
|
0.093
|
Dimethomorph |
54
|
30
|
10
|
5
|
9
|
0
|
0
|
0
|
0.68
|
Acetamiprid metabolite IM-2-1 |
49
|
46
|
3
|
0
|
0
|
0
|
0
|
0
|
0.017
|
Cypermethrin |
49
|
19
|
20
|
8
|
2
|
0
|
0
|
0
|
0.36
|
Indoxacarb |
47
|
37
|
8
|
2
|
0
|
0
|
0
|
0
|
0.13
|
Prochloraz, sum |
47
|
12
|
2
|
14
|
12
|
7
|
0
|
0
|
7.3
|
Pendimethalin |
46
|
45
|
1
|
0
|
0
|
0
|
0
|
0
|
0.017
|
Ethephon |
45
|
3
|
17
|
16
|
7
|
2
|
0
|
0
|
1.4
|
Methoxyfenozide |
45
|
22
|
16
|
6
|
1
|
0
|
0
|
0
|
0.28
|
Thiabendazole-5-hydroxy |
43
|
26
|
16
|
1
|
0
|
0
|
0
|
0
|
0.092
|
Deltamethrin |
42
|
29
|
13
|
0
|
0
|
0
|
0
|
0
|
0.04
|
Folpet |
42
|
24
|
8
|
8
|
2
|
0
|
0
|
0
|
0.43
|
Pyriproxyfen |
42
|
16
|
20
|
6
|
0
|
0
|
0
|
0
|
0.11
|
Quinoxyfen |
38
|
17
|
11
|
10
|
0
|
0
|
0
|
0
|
0.18
|
Chlorate |
37
|
18
|
15
|
4
|
0
|
0
|
0
|
0
|
0.12
|
Metrafenone |
37
|
17
|
4
|
6
|
8
|
2
|
0
|
0
|
2
|
Chlorpyrifos-methyl |
36
|
20
|
10
|
5
|
1
|
0
|
0
|
0
|
0.24
|
Pirimicarb-desamido |
34
|
34
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Fenoxycarb |
33
|
27
|
6
|
0
|
0
|
0
|
0
|
0
|
0.03
|
Propiconazole |
33
|
13
|
6
|
1
|
8
|
5
|
0
|
0
|
2.4
|
Fenpyroximate |
29
|
19
|
9
|
1
|
0
|
0
|
0
|
0
|
0.12
|
Fenbuconazole |
28
|
13
|
14
|
1
|
0
|
0
|
0
|
0
|
0.1
|
Spirodiclofen |
28
|
21
|
7
|
0
|
0
|
0
|
0
|
0
|
0.029
|
Tebufenozide |
28
|
21
|
6
|
1
|
0
|
0
|
0
|
0
|
0.11
|
Dithiocarbamates |
26
|
0
|
4
|
17
|
5
|
0
|
0
|
0
|
0.99
|
Hexythiazox |
26
|
18
|
7
|
1
|
0
|
0
|
0
|
0
|
0.082
|
Etofenprox |
25
|
9
|
6
|
4
|
6
|
0
|
0
|
0
|
0.47
|
Glufosinate, sum |
25
|
5
|
17
|
3
|
0
|
0
|
0
|
0
|
0.18
|
2,4-D |
24
|
14
|
1
|
8
|
1
|
0
|
0
|
0
|
0.46
|
Bromide |
23
|
0
|
0
|
0
|
0
|
22
|
1
|
0
|
10.7
|
Ethephon metabolite HEPA |
23
|
1
|
12
|
10
|
0
|
0
|
0
|
0
|
0.17
|
Flonicamid, sum |
22
|
17
|
4
|
1
|
0
|
0
|
0
|
0
|
0.2
|
Metalaxyl (-M) |
22
|
14
|
6
|
1
|
1
|
0
|
0
|
0
|
0.22
|
Kresoxim-methyl |
21
|
17
|
4
|
0
|
0
|
0
|
0
|
0
|
0.028
|
Forchlorfenuron |
19
|
19
|
0
|
0
|
0
|
0
|
0
|
0
|
0.004
|
Tetraconazole |
19
|
9
|
8
|
2
|
0
|
0
|
0
|
0
|
0.18
|
BAC (n=8, 10, 12, 14, 16, 18) |
18
|
1
|
16
|
1
|
0
|
0
|
0
|
0
|
0.099
|
Etoxazole |
18
|
13
|
5
|
0
|
0
|
0
|
0
|
0
|
0.026
|
Gibberellic acid |
18
|
4
|
10
|
3
|
1
|
0
|
0
|
0
|
0.62
|
o-Phenylphenol |
18
|
0
|
5
|
3
|
7
|
3
|
0
|
0
|
3.3
|
Buprofezin |
17
|
7
|
6
|
4
|
0
|
0
|
0
|
0
|
0.19
|
Clothianidin |
17
|
10
|
7
|
0
|
0
|
0
|
0
|
0
|
0.026
|
Triadimefon, sum |
17
|
4
|
2
|
6
|
5
|
0
|
0
|
0
|
0.95
|
Trimethylsulfonium cation |
17
|
10
|
6
|
1
|
0
|
0
|
0
|
0
|
0.067
|
Abamectin, sum |
16
|
14
|
1
|
1
|
0
|
0
|
0
|
0
|
0.062
|
Bifenthrin |
16
|
7
|
8
|
1
|
0
|
0
|
0
|
0
|
0.055
|
Cyproconazole |
16
|
11
|
5
|
0
|
0
|
0
|
0
|
0
|
0.039
|
Tebufenpyrad |
16
|
8
|
6
|
2
|
0
|
0
|
0
|
0
|
0.06
|
Boscalid metabolite M 510F01 |
15
|
9
|
6
|
0
|
0
|
0
|
0
|
0
|
0.022
|
Thiophanate-methyl |
15
|
9
|
2
|
2
|
1
|
1
|
0
|
0
|
1
|
Ametoctradin |
14
|
7
|
5
|
2
|
0
|
0
|
0
|
0
|
0.13
|
Phosmet, sum |
14
|
6
|
6
|
2
|
0
|
0
|
0
|
0
|
0.1
|
Cyflufenamid |
13
|
9
|
4
|
0
|
0
|
0
|
0
|
0
|
0.03
|
DDAC (n=8, 10, 12) |
13
|
0
|
13
|
0
|
0
|
0
|
0
|
0
|
0.041
|
Emamectin B1a/B1b |
13
|
12
|
1
|
0
|
0
|
0
|
0
|
0
|
0.012
|
Ethirimol |
13
|
9
|
4
|
0
|
0
|
0
|
0
|
0
|
0.021
|
Famoxadone |
13
|
5
|
4
|
4
|
0
|
0
|
0
|
0
|
0.078
|
Fluopicolide |
13
|
7
|
2
|
4
|
0
|
0
|
0
|
0
|
0.17
|
Mandipropamid |
13
|
7
|
3
|
2
|
1
|
0
|
0
|
0
|
0.51
|
Thiamethoxam |
13
|
8
|
5
|
0
|
0
|
0
|
0
|
0
|
0.04
|
Cyazofamid |
11
|
2
|
3
|
5
|
1
|
0
|
0
|
0
|
0.21
|
Cyfluthrin |
11
|
7
|
2
|
2
|
0
|
0
|
0
|
0
|
0.15
|
Dimethoate, sum |
11
|
9
|
1
|
0
|
1
|
0
|
0
|
0
|
0.86
|
Proquinazid |
11
|
10
|
1
|
0
|
0
|
0
|
0
|
0
|
0.019
|
Spinetoram |
11
|
11
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Iprodion metabolite RP 30228 |
10
|
5
|
5
|
0
|
0
|
0
|
0
|
0
|
0.027
|
Diazinon |
9
|
6
|
3
|
0
|
0
|
0
|
0
|
0
|
0.049
|
Novaluron |
9
|
9
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Spiroxamine |
9
|
4
|
2
|
3
|
0
|
0
|
0
|
0
|
0.084
|
Fenpropimorph |
8
|
8
|
0
|
0
|
0
|
0
|
0
|
0
|
0.009
|
Metalaxyl metabolite CGA 94689 |
8
|
7
|
1
|
0
|
0
|
0
|
0
|
0
|
0.013
|
Piperonyl butoxide |
8
|
5
|
1
|
1
|
1
|
0
|
0
|
0
|
0.35
|
Pyridaben |
8
|
5
|
2
|
1
|
0
|
0
|
0
|
0
|
0.056
|
Bupirimate |
7
|
5
|
1
|
1
|
0
|
0
|
0
|
0
|
0.11
|
Chlormequat |
7
|
5
|
1
|
0
|
1
|
0
|
0
|
0
|
0.83
|
Propyzamide |
7
|
7
|
0
|
0
|
0
|
0
|
0
|
0
|
0.007
|
Cyantraniliprole |
6
|
3
|
2
|
1
|
0
|
0
|
0
|
0
|
0.062
|
DEET |
6
|
6
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Icaridin |
6
|
6
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Paclobutrazol |
6
|
6
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Procymidone |
6
|
4
|
1
|
0
|
1
|
0
|
0
|
0
|
0.5
|
Triclopyr |
6
|
6
|
0
|
0
|
0
|
0
|
0
|
0
|
0.008
|
Chlorpropham |
5
|
4
|
1
|
0
|
0
|
0
|
0
|
0
|
0.018
|
Clofentezine |
5
|
2
|
1
|
1
|
1
|
0
|
0
|
0
|
0.35
|
Fluazinam |
5
|
4
|
1
|
0
|
0
|
0
|
0
|
0
|
0.011
|
Methiocarb, sum |
5
|
5
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Bifenazat, sum |
4
|
1
|
2
|
1
|
0
|
0
|
0
|
0
|
0.073
|
Chlorothalonil |
4
|
0
|
3
|
1
|
0
|
0
|
0
|
0
|
0.059
|
Dicloran |
4
|
3
|
1
|
0
|
0
|
0
|
0
|
0
|
0.021
|
Diflubenzuron |
4
|
2
|
1
|
1
|
0
|
0
|
0
|
0
|
0.18
|
Fenbutatin oxide |
4
|
1
|
2
|
0
|
1
|
0
|
0
|
0
|
0.2
|
Fenpyrazamine |
4
|
2
|
0
|
1
|
1
|
0
|
0
|
0
|
0.79
|
Iprovalicarb |
4
|
4
|
0
|
0
|
0
|
0
|
0
|
0
|
0.004
|
Metalaxyl metabolite CGA 108905 |
4
|
4
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Pirimicarb-desamido-desmethyl |
4
|
4
|
0
|
0
|
0
|
0
|
0
|
0
|
0.007
|
tau-Fluvalinate |
4
|
3
|
1
|
0
|
0
|
0
|
0
|
0
|
0.026
|
Tetradifon |
4
|
4
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
1-Naphthylacetic acid |
3
|
3
|
0
|
0
|
0
|
0
|
0
|
0
|
0.008
|
Carbaryl |
3
|
3
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Dinocap, sum |
3
|
3
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Diphenylamine |
3
|
1
|
1
|
0
|
1
|
0
|
0
|
0
|
0.7
|
Zoxamide |
3
|
0
|
1
|
2
|
0
|
0
|
0
|
0
|
0.11
|
Flutriafol |
3
|
1
|
1
|
1
|
0
|
0
|
0
|
0
|
0.068
|
Malathion, sum |
3
|
1
|
2
|
0
|
0
|
0
|
0
|
0
|
0.028
|
Nicotine |
3
|
2
|
1
|
0
|
0
|
0
|
0
|
0
|
0.012
|
Prohexadione |
3
|
2
|
1
|
0
|
0
|
0
|
0
|
0
|
0.01
|
PTU |
3
|
1
|
2
|
0
|
0
|
0
|
0
|
0
|
0.02
|
Pyrethrins |
3
|
1
|
1
|
1
|
0
|
0
|
0
|
0
|
0.053
|
Spiromesifen |
3
|
1
|
2
|
0
|
0
|
0
|
0
|
0
|
0.039
|
Triflumizole, sum |
3
|
1
|
2
|
0
|
0
|
0
|
0
|
0
|
0.011
|
Triflumuron |
3
|
0
|
2
|
1
|
0
|
0
|
0
|
0
|
0.053
|
Benalaxyl |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Bromopropylate |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Chlorfenapyr |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.004
|
Chloridazon-desphenyl |
2
|
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0.01
|
Diuron |
2
|
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0.028
|
Endosulfan, sum |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.009
|
Fluxapyroxad |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Formetanate |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Mepanipyrim |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Methidathion |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Pirimicarb, desmethyl-formamido |
2
|
2
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Propamocarb |
2
|
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0.011
|
Vinclozolin |
2
|
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0.053
|
Naphthalene acetamide |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
2,4-D, sum |
1
|
0
|
0
|
1
|
0
|
0
|
0
|
0
|
0.12
|
Acephate |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Acrinathrin |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Anthraquinone |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Atrazine-desethyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Azinphos-methyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Benthiavalicarb-isopropyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Carbendazim metabolite, 2-Aminobenz-imidazole |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.007
|
Carbofuran, sum |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Chlorothalonil-4-hydroxy |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Cymoxanil |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Cyromazine |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.005
|
Dichlorprop |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Diflufenican |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Dinotefuran |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
ETU |
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0
|
0.013
|
Fenarimol |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Fenazaquin |
1
|
0
|
0
|
1
|
0
|
0
|
0
|
0
|
0.069
|
Fenitrothion |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Fenpropathrin |
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0
|
0.012
|
Fenpropidin |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Fipronil, sum |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Fluazifop |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Flubendiamide |
1
|
0
|
0
|
1
|
0
|
0
|
0
|
0
|
0.095
|
Flufenacet |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Fluroxypyr |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Flusilazole |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Isopyrazam |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Isoxaben |
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0
|
0.012
|
Ivermectin |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Linuron |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Lufenuron |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
MCPA |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Metalaxyl metabolite CGA 107955 |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Oxydemeton-S-methyl, sum |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Oxyfluorfen |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.007
|
Parathion |
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0
|
0.012
|
Pentachloroanisole |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.006
|
Pirimiphos-methyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Probenazole |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Profenofos |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Propamocarb-N-oxide |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.007
|
Prosulfocarb |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
CGA 313124 (6-hydroxymethyl-pymetrozine) |
1
|
0
|
1
|
0
|
0
|
0
|
0
|
0
|
0.01
|
Terbutylazine-desethyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Tolfenpyrad |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Tolylfluanid, sum |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.001
|
Trichlorfon |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.002
|
Triflusulfuron-methyl |
1
|
1
|
0
|
0
|
0
|
0
|
0
|
0
|
0.003
|
Parameter | In der Rückstandsdefinition enthalten und analytisch erfasst |
---|---|
Abamectin |
Avermectin B1a |
Aldicarb, sum |
Aldicarb |
Amitraz, sum |
Amitraz |
Benzalkonium chloride, sum (BAC) |
Benzyldimethyloctylammonium chloride (BAC-C8) |
Carbofuran, sum |
Carbofuran |
DDT, sum |
DDE, pp- |
Dialkyldimethylammonium chloride, sum (DDAC) |
Dioctyldimethylammonium chloride (DDAC-C8) |
Dieldrin, sum |
Dieldrin |
Dimethoate, sum |
Dimethoate |
Disulfoton, sum |
Disulfoton |
Endosulfan, sum |
Endosulfan, alpha- |
Fenamiphos, sum |
Fenamiphos |
Fenthion, sum |
Fenthion |
Fipronil, sum |
Fipronil |
Flonicamid, sum |
Flonicamid |
Fosetyl, sum |
Fosetyl |
Glufosinate, sum |
Glufosinate |
Heptachlor, sum |
Heptachlor |
Malathion, Summe |
Malathion |
Methiocarb, Summe |
Methiocarb |
Methomyl, Summe |
Methomyl |
Milbemectin |
Milbemectin A3 |
Oxydemeton-S-methyl, Summe |
Oxydemeton-methyl |
Parathion-methyl ,Summe |
Parathion-methyl |
Phorat, Summe |
Phorate |
Phosmet, Summe |
Phosmet |
Pirimicarb, Summe |
Pirimicarb |
Prochloraz, Gesamt |
Prochloraz |
Pyrethrum, Summe |
Pyrethrin I |
Pyridat, Summe |
Pyridate |
Quintozen, Summe |
Quintozene |
Sethoxydim, Gesamt |
Sethoxydim |
Spirotetramat, Summe |
Spirotetramate, |
Terbufos, Summe |
Terbufos |
Thiamethoxam, sum |
Thiamethoxam |
Tolylfluanid, Summe |
Tolylfluanid |
Triadimefon u. Triadimenol |
Triadimefon |
Triflumizol |
Triflumizol |
Translator: Catherine Leiblein