TY - JOUR
T1 - Rate of hydrolysis and degradation of the cyanogenic glycoside – dhurrin – in soil.
AU - Johansen, Henrik
AU - Rasmussen, Lars Holm
AU - Olsen, Carl Erik
AU - Hansen, Hans Christian Bruun
PY - 2007/2
Y1 - 2007/2
N2 - Cyanogenic glycosides are common plant toxins. Toxic hydrogen cyanide originating from cyanogenic glycosides may affect soil processes and water quality. In this study, hydrolysis, degradation and sorption of dhurrin (4-hydroxymandelonitrile-β-d-glucoside) produced by sorghum has been studied in order to assess its fate in soil. The log K ow of dhurrin was -1.18 ± 0.08 (22 °C). Hydrolysis was a first-order reaction with respect to dhurrin and hydroxyl ion concentrations. Half lives ranged from 1.2 h (pH 8.6; 25 °C) to 530 d (pH 4; 25 °C). The activation energy of hydrolysis was 112 + 9 kJ. At pH 5.8 and room temperature, addition of humic acids (50 g l -1) increased the rate of hydrolysis tenfold, while addition of kaolinite or goethite (100-250 g l -1) both decreased the rate considerably. No significant sorption to soil components could be observed. The degradation rates of dhurrin in top and subsoils of Oxisols, Ultisols, Alfisols and Mollisols were studied at 22 °C (25 mg l -1, soil:liquid 1:1 (w:V), pH 3.8-8.1). Half-lives were 0.25-2 h for topsoils, and 5-288 h in subsoils. Hydrolysis in solution explained up to 45% of the degradation in subsoils whereas the contribution in topsoils was less than 14%, indicating the importance of enzymatic degradation processes. The highest risk of dhurrin leaching will take place when the soil is a low activity acid shallow soil with low content of clay minerals, iron oxides and humic acids.
AB - Cyanogenic glycosides are common plant toxins. Toxic hydrogen cyanide originating from cyanogenic glycosides may affect soil processes and water quality. In this study, hydrolysis, degradation and sorption of dhurrin (4-hydroxymandelonitrile-β-d-glucoside) produced by sorghum has been studied in order to assess its fate in soil. The log K ow of dhurrin was -1.18 ± 0.08 (22 °C). Hydrolysis was a first-order reaction with respect to dhurrin and hydroxyl ion concentrations. Half lives ranged from 1.2 h (pH 8.6; 25 °C) to 530 d (pH 4; 25 °C). The activation energy of hydrolysis was 112 + 9 kJ. At pH 5.8 and room temperature, addition of humic acids (50 g l -1) increased the rate of hydrolysis tenfold, while addition of kaolinite or goethite (100-250 g l -1) both decreased the rate considerably. No significant sorption to soil components could be observed. The degradation rates of dhurrin in top and subsoils of Oxisols, Ultisols, Alfisols and Mollisols were studied at 22 °C (25 mg l -1, soil:liquid 1:1 (w:V), pH 3.8-8.1). Half-lives were 0.25-2 h for topsoils, and 5-288 h in subsoils. Hydrolysis in solution explained up to 45% of the degradation in subsoils whereas the contribution in topsoils was less than 14%, indicating the importance of enzymatic degradation processes. The highest risk of dhurrin leaching will take place when the soil is a low activity acid shallow soil with low content of clay minerals, iron oxides and humic acids.
KW - laboratory techniques
KW - HPLC
KW - dhurrin
KW - pedology
KW - soil
KW - sorghum
U2 - 10.1016/j.chemosphere.2006.10.013
DO - 10.1016/j.chemosphere.2006.10.013
M3 - Journal article
SN - 0045-6535
VL - 67
SP - 259
EP - 266
JO - Chemosphere
JF - Chemosphere
IS - 2
ER -