Applied Ecology and Environmental Sciences
ISSN (Print): 2328-3912 ISSN (Online): 2328-3920 Website: https://www.sciepub.com/journal/aees Editor-in-chief: Alejandro González Medina
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Applied Ecology and Environmental Sciences. 2014, 2(3), 74-81
DOI: 10.12691/aees-2-3-1
Open AccessArticle

Microbial Community Structure in Soils Amended With Glyphosate-tolerant Soybean Residue

Mark Nye1, Nigel Hoilett2, Cliff Ramsier3, Peter Renz1 and Richard P. Dick1,

1School of Environment and Natural Resources, The Ohio State University, 2021 Coffey Rd, Columbus OH, 43210, USA

2Department of Agricultural Sciences, Northwest Missouri State University, 800 University Dr, Valk 101, Maryville MO 64468, USA

3Ag Spectrum, 428 East 11th Street, DeWitt IA, 52742, USA

Pub. Date: June 12, 2014

Cite this paper:
Mark Nye, Nigel Hoilett, Cliff Ramsier, Peter Renz and Richard P. Dick. Microbial Community Structure in Soils Amended With Glyphosate-tolerant Soybean Residue. Applied Ecology and Environmental Sciences. 2014; 2(3):74-81. doi: 10.12691/aees-2-3-1

Abstract

Glyphosate is a broad-spectrum herbicide used extensively worldwide to control broadleaf weeds in agriculture. Research suggests that repeated application causes a change in soil microbial properties which could be affecting soil quality and productivity. Although glyphosate is generally regarded as having relatively low environmental impact, after 10 or more years of widespread use, field observations by farmers and emerging research suggest that long-term glyphosate tolerant (GT) cropping is having cumulative and non-target effects on soils and crop productivity. There is very little information on the effects of GT residue when added to soils. Therefore, the objective was to determine shifts in the soil microbial community during GT residue decomposition in soils with and without a history of glyphosate exposure. Soybean residues from a simulated long-term GT cropping system were used in laboratory incubation. The experiment was a 2x3x4 factorial design with 2 soils (with or without glyphosate), three residue types (leaf, stem,or root), and 4 soybean residue treatments (GT residue exposed to glyphosate with potassium salt carrier, GT residue exposed to glyphosate with isopropylamine salt carrier, untreated GT genotype, and untreated non-GT genotype). These soils were profiled using phospholipid fatty acid analysis to determine shifts in soil microbial community structure due to the addition of GT residue to soil. The results showed that microbial shifts during decomposition of GT soybean residue varied between soils with or without long-term exposure to glyphosate. There was also a trend that GT material that had been exposed to glyphosate cause a differential shift in the communities over GT residue that had not been exposed to glyphosate. Commercially available glyphosate formulations have two major types of salt carriers; potassium salt and isopropylamine salt which could be a factor besides glyphosate in affecting the chemistry of GT residues and subsequently microbial response during decomposition. However, the results showed that carrier did not significantly affect PLFA profiling in soils regardless of the soil’s history of glyphosate exposure. Ratios of saturated to monounsaturated PLFAs are used as indicators of microbial stress. Our results showed that soil history of glyphosate exposure significantly affected microbial stress. There were also significant differences in stress between glyphosate residue treatments in soil with a history of glyphosate exposure.

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References:

[1]  Grube, A. USEPA Pesticide Industry Sales and Usage Report. 2011.
 
[2]  Young, B.G., Changes in herbicide use patterns and production practices resulting from glyphosate-resistant crops. Weed Technol. 20: 301-307. 2006.
 
[3]  Fawcett, R.S., B.R. Christensen, and D.P. Tierney. The impact of conservation tillage on pesticide runoff into surface water: A review and analysis J. Soil Water Conserv. 49: 126-135. 1994.
 
[4]  Andréa, M.M. de. Influence of repeated applications of glyphosate on its persistence and soil bioactivity. Pesq. Agropec. Bras. 38: 1329-1335. 2003.
 
[5]  Lancaster, S.H., E.B. Hollister, S.A. Senseman and T.J. Gentry. Effects of repeated glyphosate applications on soil microbial community composition and the mineralization of glyphosate. Pest Manag. Sci. 66: 59-64. 2010.
 
[6]  Quinn J.P., J.M.M. Peden, and R.E. Dick. Glyphosate tolerance and utilization by the microflora of soils treated with the herbicide. Appl. Microbiol. Biotechnol. 29: 511-516. 1988.
 
[7]  Fernandez, M.R., F. Selles, D. Gehl, R. Depauw and R. Zentner. Crop production factors associated with Fusarium head blight in spring wheat in eastern Saskatchewan. Crop Sci. 45: 1908-1916. 2005.
 
[8]  Huber, D. Strategies to ameliorate glyphosate immobilization of manganese and its impact on disease. Phytopathology. 97: S168-S168. 2007.
 
[9]  Locke, M., R. Zablotowicz and K. Reddy. Integrating soil conservation practices and glyphosate-resistant crops: Impacts on soil. Pest Manag. Sci. 64: 457-469. 2008.
 
[10]  Fernandez, M.R., R.P. Zentner, P. Basnyat, D. Gehl, F. Selles and D. Huber. Glyphosate associations with cereal diseases caused by Fusarium spp. in the canadian prairies. Eur. J. Agron. 31: 133-143. 2009.
 
[11]  Johal, G. and D. Huber. Glyphosate effects on diseases of plants. Eur. J. Agron. 31: 144-152. 2009.
 
[12]  Kremer, R. and N. Means. Glyphosate and glyphosate-resistant crop interactions with rhizosphere microorganisms. Eur. J. Agron. 31: 153-161. 2009.
 
[13]  Yamada, T., R. Kremer, P. Castro and B. Wood. Glyphosate interactions with physiology, nutrition, and diseases of plants: Threat to agricultural sustainability? preface. Eur. J. Agron. 31: 111-113. 2009.
 
[14]  Eker, S., L. Ozturk, A. Yazici, B. Erenoglu, V. Romheld and I. Cakmak. Foliar-applied glyphosate substantially reduced uptake and transport of iron and manganese in sunflower plants. J. Agric. Food Chem. 54: 10019-10025. 2006.
 
[15]  Neumann, G., S. Kohls, E. Landsberg, K. Souza, T. Yamada and V. Roemheld. Relevance of glyphosate transfer to non-target plants via the rhizosphere. Journal of Plant Dis. Protect. 20: 963-969. 2006.
 
[16]  Coupland, D. and J. Caseley. Presence of 14C activity in root exudates and guttation fluid from agropyron-repens treated with 14C-labeled glyphosate. New Phytol. 83: 17-22. 1979.
 
[17]  Kremer, R., N. Means and S. Kim. Glyphosate affects soybean root exudation and rhizosphere micro-organisms Int. J. Environ. Anal. Chem. 85: 1165-1174. 2005.
 
[18]  Rueppel, M., B. Brightwell, J. Schaefer and J. Marvel. Metabolism and degradation of glyphosate in soil and water. J. Agric. Food Chem. 25: 517-528. 1977.
 
[19]  Shushkova, T.V., G.K. Vasilieva, I.T. Ermakova, and A.A. Leontievsky. Sorption and microbial degradation of glyphosate in soil suspensions. Appl. Biochem. Microbiol. 45: 599-603. 2009.
 
[20]  Charnay, M. P., C. Mougin, A. Farrugia, and E. Barriuso. Incorporation of pesticides by soil micro-organisms as a way of bound residues formation. Environ. Chem. Lett. 2: 27-30. 2004.
 
[21]  Powell, J.R., D.J. Levy-Booth, R.H. Gulden, W.L. Asbil, R.G. Campbell, K.E. Dunfield, A.S. Hamill, M. Hart, S. Lerat, R.E. Nurse, K. Pauls, P. Sikkema, C.J. Swanton, J.T. Trevors and J.N. Klironomos. Effects of genetically modified, herbicide-tolerant crops and their management on soil food web properties and crop litter decomposition. J. Appl. Ecol. 46: 388-396. 2009.
 
[22]  Bergersen, F.J., G.L. Turner, R.R. Gault, M.B. Peoples, L.J. Morthorpe, J. Brockwell, Contributions of Nitrogen in Soybean Crop Residue to Subsequent Crops and to Soil. Aust. J. Agric. Res. 43: 155-169. 1992
 
[23]  Frostegård, A. and E. Bååth. The use of phospholipid fatty acid analysis to estimate bacterial and fungal biomass in soil. Biol. Fert. Soils. 22: 59-65. 1996.
 
[24]  Bligh, E.G., and W.J. Dyer. A Rapid Method of Total Lipid Extraction and Purification. Can. J. Biochem. Physiol. 37: 911–917. 1959,
 
[25]  Larkin, R.P. Characterization of soil microbial communities under different potato cropping systems by microbial population dynamics, substrate utilization, and fatty acid profiles. Soil Biol. Biochem. 35: 1451-1466. 2003
 
[26]  Moore-Kucera, J and R.P. Dick. PLFA profiling of microbial community structure and seasonal shifts in soils of a Douglas-fir chronosequence. Microb. Ecol. 55: 500-511. 2008.
 
[27]  Lupwayi, N.Z., and R.E. Blackshaw. Soil microbiology in glyphosate-resistant corn cropping systems. Agron. J. 104: 1041-1048. 2012.
 
[28]  Hart, M.R. and P.C. Brookes. Soil microbial biomass and mineralization of soil organic matter after 19 years of cumulative field applications of pesticides. Soil Biol. Biochem. 28: 1641-1649. 1996.
 
[29]  Wardle, D.A., and D. Parkinson. Influence of the herbicide glyphosate on soil microbial community structure. Plant and Soil. 122: 29-37. 1990.
 
[30]  Wardle, D.A., and D. Parkinson. The influence of the herbicide glyphosate on interspecific interactions between four soil fungal species. Mycol. Res. 96: 180-186. 1992.
 
[31]  Ratcliff, A.W., M.D. Busse, C.J. Shestak. Changes in microbial community structure following herbicide (glyphosate) additions to forest soils. Appl. Soil Ecol. 34: 114-124. 2006.
 
[32]  Weaver, M.A., L.J. Krutz, R.M. Zablotowicz, and K.N. Reddy. Effects of glyphosate on soil microbial communities and its mineralization in Mississippi soil. Pest. Manag. Sci. 63: 388-393. 2007.
 
[33]  Duke, S.O., J. Lydon, W.C. Koskinen, T.B. Moorman, R.L. Chaney, and R. Hammerschmidt. Glyphosate effects on plant mineral nutrition, crop rhizosphere microbiota, and plant disease in glyphosate-resistant crops. J. Ag. Food Chem. 60: 10375-97. 2012.