Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia

Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA...
Ausführliche Beschreibung

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Autor*in:	Swilling, Keagan J. [verfasserIn] Shrestha, Utsala Ownley, Bonnie H. Gwinn, Kimberly D. Butler, David M.

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2021

Schlagwörter:	Soil disinfestation Organic acids Biological soil disinfestation

Anmerkung:	© Koninklijke Nederlandse Planteziektenkundige Vereniging 2021

Übergeordnetes Werk:	Enthalten in: European journal of plant pathology - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895, 162(2021), 1 vom: 24. Sept., Seite 149-161
Übergeordnetes Werk:	volume:162 ; year:2021 ; number:1 ; day:24 ; month:09 ; pages:149-161

Links:	Volltext

DOI / URN:	10.1007/s10658-021-02392-8

Katalog-ID:	SPR045869324

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100	1		\|a Swilling, Keagan J. \|e verfasserin \|4 aut
245	1	0	\|a Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
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520			\|a Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture.
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700	1		\|a Shrestha, Utsala \|4 aut
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700	1		\|a Gwinn, Kimberly D. \|4 aut
700	1		\|a Butler, David M. \|0 (orcid)0000-0002-5897-1382 \|4 aut
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912			\|a GBV_ILN_31
912			\|a GBV_ILN_32
912			\|a GBV_ILN_39
912			\|a GBV_ILN_40
912			\|a GBV_ILN_60
912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_65
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
912			\|a GBV_ILN_74
912			\|a GBV_ILN_90
912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2110
912			\|a GBV_ILN_2111
912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2118
912			\|a GBV_ILN_2122
912			\|a GBV_ILN_2129
912			\|a GBV_ILN_2143
912			\|a GBV_ILN_2144
912			\|a GBV_ILN_2147
912			\|a GBV_ILN_2148
912			\|a GBV_ILN_2152
912			\|a GBV_ILN_2153
912			\|a GBV_ILN_2188
912			\|a GBV_ILN_2190
912			\|a GBV_ILN_2232
912			\|a GBV_ILN_2336
912			\|a GBV_ILN_2446
912			\|a GBV_ILN_2470
912			\|a GBV_ILN_2472
912			\|a GBV_ILN_2507
912			\|a GBV_ILN_2522
912			\|a GBV_ILN_2548
912			\|a GBV_ILN_4035
912			\|a GBV_ILN_4037
912			\|a GBV_ILN_4046
912			\|a GBV_ILN_4112
912			\|a GBV_ILN_4125
912			\|a GBV_ILN_4126
912			\|a GBV_ILN_4242
912			\|a GBV_ILN_4246
912			\|a GBV_ILN_4249
912			\|a GBV_ILN_4251
912			\|a GBV_ILN_4305
912			\|a GBV_ILN_4306
912			\|a GBV_ILN_4307
912			\|a GBV_ILN_4313
912			\|a GBV_ILN_4322
912			\|a GBV_ILN_4323
912			\|a GBV_ILN_4324
912			\|a GBV_ILN_4325
912			\|a GBV_ILN_4326
912			\|a GBV_ILN_4328
912			\|a GBV_ILN_4333
912			\|a GBV_ILN_4334
912			\|a GBV_ILN_4335
912			\|a GBV_ILN_4336
912			\|a GBV_ILN_4338
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allfields	10.1007/s10658-021-02392-8 doi (DE-627)SPR045869324 (SPR)s10658-021-02392-8-e DE-627 ger DE-627 rakwb eng Swilling, Keagan J. verfasserin aut Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021 Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213 Shrestha, Utsala aut Ownley, Bonnie H. aut Gwinn, Kimberly D. aut Butler, David M. (orcid)0000-0002-5897-1382 aut Enthalten in European journal of plant pathology Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895 162(2021), 1 vom: 24. Sept., Seite 149-161 (DE-627)27042976X (DE-600)1477679-0 1573-8469 nnns volume:162 year:2021 number:1 day:24 month:09 pages:149-161 https://dx.doi.org/10.1007/s10658-021-02392-8 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 162 2021 1 24 09 149-161
spelling	10.1007/s10658-021-02392-8 doi (DE-627)SPR045869324 (SPR)s10658-021-02392-8-e DE-627 ger DE-627 rakwb eng Swilling, Keagan J. verfasserin aut Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021 Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213 Shrestha, Utsala aut Ownley, Bonnie H. aut Gwinn, Kimberly D. aut Butler, David M. (orcid)0000-0002-5897-1382 aut Enthalten in European journal of plant pathology Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895 162(2021), 1 vom: 24. Sept., Seite 149-161 (DE-627)27042976X (DE-600)1477679-0 1573-8469 nnns volume:162 year:2021 number:1 day:24 month:09 pages:149-161 https://dx.doi.org/10.1007/s10658-021-02392-8 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 162 2021 1 24 09 149-161
allfields_unstemmed	10.1007/s10658-021-02392-8 doi (DE-627)SPR045869324 (SPR)s10658-021-02392-8-e DE-627 ger DE-627 rakwb eng Swilling, Keagan J. verfasserin aut Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021 Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213 Shrestha, Utsala aut Ownley, Bonnie H. aut Gwinn, Kimberly D. aut Butler, David M. (orcid)0000-0002-5897-1382 aut Enthalten in European journal of plant pathology Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895 162(2021), 1 vom: 24. Sept., Seite 149-161 (DE-627)27042976X (DE-600)1477679-0 1573-8469 nnns volume:162 year:2021 number:1 day:24 month:09 pages:149-161 https://dx.doi.org/10.1007/s10658-021-02392-8 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 162 2021 1 24 09 149-161
allfieldsGer	10.1007/s10658-021-02392-8 doi (DE-627)SPR045869324 (SPR)s10658-021-02392-8-e DE-627 ger DE-627 rakwb eng Swilling, Keagan J. verfasserin aut Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021 Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213 Shrestha, Utsala aut Ownley, Bonnie H. aut Gwinn, Kimberly D. aut Butler, David M. (orcid)0000-0002-5897-1382 aut Enthalten in European journal of plant pathology Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895 162(2021), 1 vom: 24. Sept., Seite 149-161 (DE-627)27042976X (DE-600)1477679-0 1573-8469 nnns volume:162 year:2021 number:1 day:24 month:09 pages:149-161 https://dx.doi.org/10.1007/s10658-021-02392-8 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 162 2021 1 24 09 149-161
allfieldsSound	10.1007/s10658-021-02392-8 doi (DE-627)SPR045869324 (SPR)s10658-021-02392-8-e DE-627 ger DE-627 rakwb eng Swilling, Keagan J. verfasserin aut Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021 Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213 Shrestha, Utsala aut Ownley, Bonnie H. aut Gwinn, Kimberly D. aut Butler, David M. (orcid)0000-0002-5897-1382 aut Enthalten in European journal of plant pathology Dordrecht [u.a.] : Springer Science + Business Media B.V, 1895 162(2021), 1 vom: 24. Sept., Seite 149-161 (DE-627)27042976X (DE-600)1477679-0 1573-8469 nnns volume:162 year:2021 number:1 day:24 month:09 pages:149-161 https://dx.doi.org/10.1007/s10658-021-02392-8 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 162 2021 1 24 09 149-161
language	English
source	Enthalten in European journal of plant pathology 162(2021), 1 vom: 24. Sept., Seite 149-161 volume:162 year:2021 number:1 day:24 month:09 pages:149-161
sourceStr	Enthalten in European journal of plant pathology 162(2021), 1 vom: 24. Sept., Seite 149-161 volume:162 year:2021 number:1 day:24 month:09 pages:149-161
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Soil disinfestation Organic acids Biological soil disinfestation
isfreeaccess_bool	false
container_title	European journal of plant pathology
authorswithroles_txt_mv	Swilling, Keagan J. @@aut@@ Shrestha, Utsala @@aut@@ Ownley, Bonnie H. @@aut@@ Gwinn, Kimberly D. @@aut@@ Butler, David M. @@aut@@
publishDateDaySort_date	2021-09-24T00:00:00Z
hierarchy_top_id	27042976X
id	SPR045869324
language_de	englisch
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author	Swilling, Keagan J.
spellingShingle	Swilling, Keagan J. misc Soil disinfestation misc Organic acids misc Biological soil disinfestation Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
authorStr	Swilling, Keagan J.
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topic_title	Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia Soil disinfestation (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Biological soil disinfestation (dpeaa)DE-He213
topic	misc Soil disinfestation misc Organic acids misc Biological soil disinfestation
topic_unstemmed	misc Soil disinfestation misc Organic acids misc Biological soil disinfestation
topic_browse	misc Soil disinfestation misc Organic acids misc Biological soil disinfestation
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title	Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
ctrlnum	(DE-627)SPR045869324 (SPR)s10658-021-02392-8-e
title_full	Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
author_sort	Swilling, Keagan J.
journal	European journal of plant pathology
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author_browse	Swilling, Keagan J. Shrestha, Utsala Ownley, Bonnie H. Gwinn, Kimberly D. Butler, David M.
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author-letter	Swilling, Keagan J.
doi_str_mv	10.1007/s10658-021-02392-8
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title_sort	volatile fatty acid concentration, soil ph and soil texture during anaerobic soil conditions affect viability of athelia (sclerotium) rolfsii sclerotia
title_auth	Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
abstract	Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021
abstractGer	Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021
abstract_unstemmed	Abstract Volatile fatty acids (VFAs) play a role in suppression of plant pathogens during anaerobic soil disinfestation (ASD), but it is unclear how VFAs in anaerobic soil affect Athelia rolfsii (formerly Sclerotium rolfsii). Anaerobic growth chamber trials were conducted to evaluate effects of VFA and VFA concentration, and interactions with soil pH and soil texture, on A. rolfsii sclerotia viability (as indicated by sclerotia germination) and colonization by potential mycoparasites. In the first objective, sclerotia were exposed to acetic or n-butyric acids at 4, 8, or 16 mmol/kg soil in sandy soil; soil pH was buffered to 5, 6, or 7. Sclerotial germination was generally reduced by both VFAs, notably at pH 5 (29% germination at 4 mmol/kg soil, 1% at 8 mmol/kg soil, and 0% at 16 mmol/kg soil). The highest colonization rates were observed in acetic acid at 16 mmol/kg soil and soil pH of 5 and 6 (65 and 55% colonization). Sclerotial germination in water or HCl controls was consistently above 90%, with minimal colonization. In the second objective, sclerotia in sandy or sandy loam soil were exposed to 4 or 16 mmol VFA/kg soil at soil pH 5 or 6. Sclerotial germination was generally less in sandy soil compared to sandy loam soil (e.g., 4 mmol VFA/kg soil at pH 5, 62% germination in sandy loam versus 0% in sandy soil), but not at pH 5 and 16 mmol/kg soil (< 1% germination in both soil textures). Soil colloid (clay and organic matter) concentration likely plays a role in reduction of VFA activity. VFAs are probable important factors in A. rolfsii suppression due to ASD treatment in many soil environments, and activity is dependent on VFA concentration, soil solution pH, and soil texture. © Koninklijke Nederlandse Planteziektenkundige Vereniging 2021
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container_issue	1
title_short	Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia
url	https://dx.doi.org/10.1007/s10658-021-02392-8
remote_bool	true
author2	Shrestha, Utsala Ownley, Bonnie H. Gwinn, Kimberly D. Butler, David M.
author2Str	Shrestha, Utsala Ownley, Bonnie H. Gwinn, Kimberly D. Butler, David M.
ppnlink	27042976X
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doi_str	10.1007/s10658-021-02392-8
up_date	2024-07-03T18:49:48.069Z
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Volatile fatty acid concentration, soil pH and soil texture during anaerobic soil conditions affect viability of Athelia (Sclerotium) rolfsii sclerotia

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