Herbicide residues in Australian grain cropping soils at sowing and their relevance to crop growth

被引:14
|
作者
Rose, Michael T. [1 ,7 ]
Zhang, Pei [2 ]
Rose, Terry J. [3 ,7 ]
Scanlan, Craig A. [4 ]
McGrath, Gavan [5 ,6 ,7 ]
Van Zwieten, Lukas [1 ,3 ,7 ]
机构
[1] NSW Dept Primary Ind, Wollongbar, NSW 2477, Australia
[2] Agr Victoria Res AVR, Macleod, Vic 3085, Australia
[3] Southern Cross Univ, Lismore, NSW 2480, Australia
[4] Dept Primary Ind & Reg Dev, Northam, WA 6401, Australia
[5] Murdoch Univ, Coll Sci Hlth Engn & Educ, Agr Discipline, 90 South St, Murdoch, WA 6150, Australia
[6] Dept Biodivers Conservat & Attract, Biodivers & Conservat Sci, Kensington, WA 6151, Australia
[7] Cooperat Res Ctr High Performance Soils, Callaghan, NSW 2380, Australia
关键词
Carryover; Plant-back; Pesticide; Risk assessment; Sustainable agriculture; Crop rotation; 3 VICTORIAN SOILS; SURFACE WATERS; NO-TILL; AMINOMETHYLPHOSPHONIC ACID; PESTICIDE-RESIDUES; AGRICULTURAL SOILS; MICROBIAL BIOMASS; GLYPHOSATE; AMPA; TRIFLURALIN;
D O I
10.1016/j.scitotenv.2022.155105
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Herbicides are used extensively in Australian grain cropping systems. Despite occasional observations of herbicide induced phytotoxicity, there is little information on the persistence and carryover of multiple herbicide classes in cropping soils and the risk to subsequent crops. Two soil surveys were conducted, in 2015 (n = 40) and 2016 (n = 42), across different Australian grain cropping fields prior to sowing of winter crops, and soil samples analysed for herbicide residues (16 analytes in 2015 and 22 analytes in 2016). Samples in 2015 were taken at two depths (0-10 cm and 10-30 cm), whilst samples in 2016 were taken in topsoil (0-10 cm) only, but from two discrete locations in each field. Our research in both years found at least one herbicide (or herbicide metabolite) residue at all sites, with a median of 6 analytes detected in 2015 and 7 analytes detected in 2016. The most frequently detected residues were glyphosate and its primary breakdown product aminomethylphosphonic acid (AMPA), in 87 and 100%, respectively, of topsoil (0-10 cm) samples in 2015, and 67 and 93% of samples in 2016. The median concentration of glyphosate in 2015 was 0.12 mg kg(-1), while AMPA was 0.41 mg kg(-1). In 2016, median concentrations of glyphosate and AMPA were 0.22 mg kg(-1) and 0.31 mg kg(-1). Residues of 2,4-dichlorophenoxyacetic acid, trifluralin and diflufenican were also detected in > 40% of topsoil samples in both seasons, but with median concentrations of < 0.05 mg kg(-1). A literature review found limited availability of phytotoxicity thresholds for major grain crops exposed to soilborne herbicide residues. A risk assessment using available thresholds suggested that although up to 29% of fields contained trifluralin residues that could constrain cereal crop growth, and 24% of fields contained residues of phenoxy or sulfonylureas that could affect dicotyledonous crops, the majority of these fields when planted with tolerant crops would be unlikely to be affected by herbicide residues. More work is required to ascertain the spatial distribution, bioavailability and phytotoxicity of residues and residue mixtures to enable a more accurate agronomic risk assessment.
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页数:14
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