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poster - International Conference of Agricultural Engineering

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The soil used for the determination <strong>of</strong> desorption, extractable and bound residues was<br />

acquired by a test <strong>of</strong> alachlor leaching, in accordance with the treatments. Figure 1 shows<br />

the steps carried out in the leaching test.<br />

Steps<br />

5th<br />

4th<br />

3rd<br />

Stages<br />

Passage <strong>of</strong> 12 V p ultra pure water<br />

Contact period<br />

Application <strong>of</strong> alachlor on top <strong>of</strong> columns: 5 times the concentration <strong>of</strong> 3360 g <strong>of</strong> active<br />

ingredient per hectare (NORTOX, 2011).<br />

2nd Control 1 V p <strong>of</strong> MOT-B 1 V p <strong>of</strong> MOD-B 1 V p <strong>of</strong> MOT-E 1 V p <strong>of</strong> MOD-B<br />

<br />

1st<br />

<br />

Saturation with CaCl 2 (0.01 M)<br />

FIGURE 1: Scheme <strong>of</strong> the stages performed during the leaching test.<br />

After the leaching test, column soil was air dried, pounded to break up clods and sifted<br />

in 2 mm mesh, and this material was stored in glass vials for subsequent extraction and<br />

quantification <strong>of</strong> desorption, extractable and bound residues.<br />

Adapting the methodology described by Lavorenti et al. (1998), in triplicate, 10 grams<br />

<strong>of</strong> each column soil were weighed, and placed in 50mL polyethylene centrifuge tubes.<br />

Moisture content was determined for the soil <strong>of</strong> each treatment to make the correction in the<br />

soil mass to be used in the extraction. To these tubes, 20 mL CaCl 2 solution (0.01 M) was<br />

added, and stirring was carried out on horizontal shaker at 200 rpm for 24 hours. After this<br />

period, samples were centrifuged for 56 minutes at 6000 rpm (4757 g). Alachlor<br />

concentration present in the supernatant <strong>of</strong> centrifuged samples was analyzed and<br />

characterized as desorption residue. The same extraction procedures were carried out in<br />

triplicate for a control sample contaminated with 50 mg L -1 <strong>of</strong> alachlor, to determine the<br />

percentage <strong>of</strong> recuperation <strong>of</strong> method.<br />

After this desorption, soil samples received organic solvents, chosen according to<br />

polarity grade, with solvent / sample ratio <strong>of</strong> 2:1 (volume / weight). Four extractions were<br />

performed: the first with a mixture <strong>of</strong> acetonitrile / water (1:1), the second and the third with<br />

acetonitrile, and the fourth with ethyl acetate. At each addition <strong>of</strong> organic solvent to the<br />

sample, horizontally mechanical stirring for 1 hour at 200 rpm was performed. Subsequently,<br />

the sample was centrifuged for 56 minutes at 6000 rpm (4757 g) at 20 ° C. After each<br />

centrifugation, the supernatant was reserved in glass vials properly identified according to<br />

treatment and solvent used for extraction. In this material, which represents the fraction <strong>of</strong><br />

extracted residues, concentration <strong>of</strong> alachlor was determined and results were expressed in<br />

mg in the soil column, based on the relationship between the concentration in the<br />

supernatant and the volume <strong>of</strong> extracted solution, and the relationship between soil mass<br />

used in the extraction and soil mass used in the column. According Lavorenti et al. (1997),<br />

the molecules remaining in the soil after these procedures are considered to be bound<br />

residues.<br />

3. Results and discussion<br />

It was observed in the balance <strong>of</strong> alachlor in the soil column (Table 2) that the leaching<br />

was stronger MOD than in MOT, representing 88.50% and 90.98% <strong>of</strong> the total applied in

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