poster - International Conference of Agricultural Engineering
poster - International Conference of Agricultural Engineering poster - International Conference of Agricultural Engineering
DESORPTIONS, EXTRACTABLES AND BOUND RESIDUES OF ALACHLOR IN SOIL WITH THE ADDITION OF ORGANIC MATTER FROM SWINE WASTEWATER Tatiane C. Dal Bosco 1* , Silvio C. Sampaio 2 , Silvia R.M. Coelho 2 , Natássia J. Cosmann 2 , Marcos H. Kunita 3 , Morgana S.Gonçalves 4 1 Universidade Tecnológica Federal do Paraná (Technological University of Paraná), Câmpus Londrina, Avenida dos Pioneiros, 3131, Londrina-PR, 86036-370, Brazil. 2 Universidade Estadual do Oeste do Paraná (State University of West Paraná), Câmpus Cascavel, Rua Universitária, 2069, Cascavel –PR, 86819-110, Brazil. 3 Universidade Estadual de Maringá (State University of Maringá), Avenida Colombo, 5970, Maringá –PR, 87020-900, Brazil. 4 Universidade Tecnológica Federal do Paraná (Technological University of Paraná), Câmpus Francisco Beltrão, Linha Santa Bárbara, sem número, Francisco Beltrão-PR, 85601-970, Brazil. Corresponding author. E-mail: tatianebosco@utfpr.edu.br Abstract Swine wastewater application into soil to reuse water on cropping provides the addition of total and dissolved organic matter to soil, which interferes in the dynamics of pesticides in soil. This study aims at evaluating the effects of total and dissolved organic matter application from two systems of swine wastewater, biodigestor and lagoon treatments, in alachlor formation of bound residues into soil. Extraction and quantification of desorption, extractable and bound residues were carried out after the evaluation of miscible displacement of alachlor performed by disturbed soil columns. The dissolved organic matter did not show desorption residues, only extractable ones. From a soil contamination perspective, biodigester swine wastewater in dissolved form would be the treatment that would less contribute to this process. Whereas from a toxicological perspective, biodigester swine wastewater in dissolved form would result in less damage to soil biota, since it showed greater bound residue formation and dissipation of alachlor. Keywords: biodigestor wastewater, lagoon treatment wastewater, pesticides. 1. Introduction In soil, pesticides may be sorbed to soil particles, degraded into other chemical forms by physical and / or microbiological chemical processes, leached downward to groundwater or transferred from surface water to groundwater, causing impacts on public health (Cheng et al., 2010; Bouchonnet et al., 2011). These processes occur simultaneously and are subject to complex interactions. Considering that the majority of pesticides is found in middle-depth soil, pesticide residues are the main source of contamination of groundwater and of agricultural crops (Majumdar & Singh, 2007). According to Andréa (1992), during the dissipation process, pesticides can react with soil organic matter and in several manners, many of such reactions lead to the formation of residues. These residues may be from the pesticide itself and / or from metabolites which may be removable or, alternatively, residues that are not extractable, also called bound residues. Muller et al. (2007) reported that irrigation with effluents can promote remobilization of bound residues in the degradation of organic matter mediated by microorganisms. Moreover, the introduction of organic and inorganic chemical compounds from irrigation with effluents can increase the amount of dissolved organic matter, favoring the formation of bound residues. According Lerch et al. (2009), the first consequence of the formation of nonextractable bound residues is associated to decreased availability of pesticide residues with the consequent increase in persistence in soil. The possibility of reversal among the forms of
extractable and non-extractable bound residues plays an important role in the destination of pesticides in the soil in the long term. Accordingly, this study aims at quantifying desorption, extractable and bound residues of alachlor in swine wastewater (SWW) treated soil, in dissolved and total forms, from two effluent treatment systems and subjected to tests of miscible displacement. Moreover, this work also aimed at determining the percentage of extractable residues of alachlor according to solvents used for extraction. 2. Materials and Methods Tested treatments included: Control: no addition of SWW, MOD-B: dissolved organic matter from SWW treated in biodigester, MOT-B: total organic matter from SWW treated in biodigester; MOD-E: dissolved organic matter from SWW treated in lagoon treatments, and, MOT-E: total organic matter from SWW treated in lagoon treatments. The SWWs were collected from two farms that have piglet production system. One of the properties has integrated biosystem for the treatment of pig manure, and the collection was conducted at the point where the effluent leaves the biodigester, because most of the properties that work with pig manure in biodigesters do not perform the other treatment steps provided in the integrated biosystem. The SWW from lagoon treatments was collected in another farm that treats swine waste in a sequence of three lagoon treatments. The collection was conducted at the output of the third lagoon effluent. The MOT consisted of SWW just as it was collected, and the MOD was extracted from SWW according to an adaptation of the methodology described by Zhaohai et al. (2008). In the extraction of MOD, centrifugation and filtration methods were used. Initially, centrifugation at 3200 rpm (2474 g) was performed for 15 minutes, and then the supernatant was filtered through a membrane of cellulose acetate of 0.45 mm in porosity. After filtration, the material was frozen. The main physical and chemical characteristics of SWW treated in biodigester and lagoon treatments in dissolved and total form, can be found in Table 1. TABLE 1: Swine wastewater characterization Parameters Unit MOT-B MOD-B MOT-E MOD-E pH (CaCl2) - 7.15 8.27 7.20 8.07 Electric conductivity µS cm -1 6,810.00 5,820.00 6990.00 6270.00 Oxigen chemical demand 4,830.00 1,539.00 2154.00 1405.00 Total nitrogen mg L -1 1,190.00 905.30 967.90 863.30 Total solids 3,860.00 2510.00 3193.00 2104.00 Total organic carbon (TOC) 967.00 355.60 547.30 255.40 Fixed solids 2,106.00 1674.00 2129.00 1457.00 Volatile solids 1,755.00 837.00 1064.00 647.00 Protocol of APHA, AWWA and WEF (1998). Total organic carbon (TOC) was determined by TOC analyzer. The soil (Oxisol, according to EMBRAPA, 2006) was collected in forest area, in order to ensure no soil contamination by alachlor and other pesticides. Collection depth was 30-60 cm to eliminate the effect of organic matter resulting from litter. This soil consists of 10.87% sand, 12.32% silt and 76.81% clay. The pH is 4.25, the organic matter content is 17 g dm -3 , CEC is 151 mmol c dm -3 and the concentration of total nitrogen is 467 mg dm -3 . It was used the alachlor (2-chloro-2,6-diethyl-N-(methoxymethyl acetamide)), an herbicide from the chloroacetamide group, analytical grade (Pestanal ® ), with water solubility of 172 mg L -1 . Quantification was performed using the high-performance liquid chromatography (HPLC) technique in Shimadzu ® , Prominence chromatograph. The samples were filtered through a membrane of 0.45 mm pore size, and injected into the chromatograph at the following conditions: C-18 column (150 x 4.6 mm), mobile phase acetonitrile: water (60:40, v / v) Detector UV - 220 nm, continuous flow of 1 mL min -1 , oven temperature of 35 °C, and injection volume of 20 µL (Silva & Vieira 2009; Sopeña et al., 2009).
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DESORPTIONS, EXTRACTABLES AND BOUND RESIDUES OF<br />
ALACHLOR IN SOIL WITH THE ADDITION OF ORGANIC MATTER<br />
FROM SWINE WASTEWATER<br />
Tatiane C. Dal Bosco 1* , Silvio C. Sampaio 2 , Silvia R.M. Coelho 2 , Natássia J.<br />
Cosmann 2 , Marcos H. Kunita 3 , Morgana S.Gonçalves 4<br />
1 Universidade Tecnológica Federal do Paraná (Technological University <strong>of</strong> Paraná),<br />
Câmpus Londrina, Avenida dos Pioneiros, 3131, Londrina-PR, 86036-370, Brazil.<br />
2 Universidade Estadual do Oeste do Paraná (State University <strong>of</strong> West Paraná), Câmpus<br />
Cascavel, Rua Universitária, 2069, Cascavel –PR, 86819-110, Brazil.<br />
3 Universidade Estadual de Maringá (State University <strong>of</strong> Maringá), Avenida Colombo, 5970,<br />
Maringá –PR, 87020-900, Brazil.<br />
4 Universidade Tecnológica Federal do Paraná (Technological University <strong>of</strong> Paraná),<br />
Câmpus Francisco Beltrão, Linha Santa Bárbara, sem número, Francisco Beltrão-PR,<br />
85601-970, Brazil.<br />
Corresponding author. E-mail: tatianebosco@utfpr.edu.br<br />
Abstract<br />
Swine wastewater application into soil to reuse water on cropping provides the addition <strong>of</strong><br />
total and dissolved organic matter to soil, which interferes in the dynamics <strong>of</strong> pesticides in<br />
soil. This study aims at evaluating the effects <strong>of</strong> total and dissolved organic matter<br />
application from two systems <strong>of</strong> swine wastewater, biodigestor and lagoon treatments, in<br />
alachlor formation <strong>of</strong> bound residues into soil. Extraction and quantification <strong>of</strong> desorption,<br />
extractable and bound residues were carried out after the evaluation <strong>of</strong> miscible<br />
displacement <strong>of</strong> alachlor performed by disturbed soil columns. The dissolved organic matter<br />
did not show desorption residues, only extractable ones. From a soil contamination<br />
perspective, biodigester swine wastewater in dissolved form would be the treatment that<br />
would less contribute to this process. Whereas from a toxicological perspective, biodigester<br />
swine wastewater in dissolved form would result in less damage to soil biota, since it showed<br />
greater bound residue formation and dissipation <strong>of</strong> alachlor.<br />
Keywords: biodigestor wastewater, lagoon treatment wastewater, pesticides.<br />
1. Introduction<br />
In soil, pesticides may be sorbed to soil particles, degraded into other chemical forms<br />
by physical and / or microbiological chemical processes, leached downward to groundwater<br />
or transferred from surface water to groundwater, causing impacts on public health (Cheng et<br />
al., 2010; Bouchonnet et al., 2011). These processes occur simultaneously and are subject<br />
to complex interactions. Considering that the majority <strong>of</strong> pesticides is found in middle-depth<br />
soil, pesticide residues are the main source <strong>of</strong> contamination <strong>of</strong> groundwater and <strong>of</strong><br />
agricultural crops (Majumdar & Singh, 2007).<br />
According to Andréa (1992), during the dissipation process, pesticides can react with<br />
soil organic matter and in several manners, many <strong>of</strong> such reactions lead to the formation <strong>of</strong><br />
residues. These residues may be from the pesticide itself and / or from metabolites which<br />
may be removable or, alternatively, residues that are not extractable, also called bound<br />
residues. Muller et al. (2007) reported that irrigation with effluents can promote remobilization<br />
<strong>of</strong> bound residues in the degradation <strong>of</strong> organic matter mediated by microorganisms.<br />
Moreover, the introduction <strong>of</strong> organic and inorganic chemical compounds from irrigation with<br />
effluents can increase the amount <strong>of</strong> dissolved organic matter, favoring the formation <strong>of</strong><br />
bound residues. According Lerch et al. (2009), the first consequence <strong>of</strong> the formation <strong>of</strong> nonextractable<br />
bound residues is associated to decreased availability <strong>of</strong> pesticide residues with<br />
the consequent increase in persistence in soil. The possibility <strong>of</strong> reversal among the forms <strong>of</strong>