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钙与土壤pH值相互作用在促进甲拌磷钠生物降解中的关键作用。

The crucial role of calcium interacting with soil pH in enhanced biodegradation of metam-sodium.

作者信息

Warton Ben, Matthiessen John N

机构信息

CSIRO Entomology, Private Bag 5, Wembley WA 6913, Australia.

出版信息

Pest Manag Sci. 2005 Sep;61(9):856-62. doi: 10.1002/ps.1095.

DOI:10.1002/ps.1095
PMID:16010663
Abstract

Enhanced biodegradation of soil-applied pesticides has long been correlated with soil pH above ca 6.5-7.5, but the possibility of confounding or interdependence with calcium, given that soil calcium concentration increases exponentially as pH rises above that range, has not previously been studied. Enhanced biodegradation of the broad-spectrum biocide metam-sodium was readily induced de novo in a naturally acid sandy soil (pH 4.2 measured in 0.01 M CaCl2) by multiple treatments, but only when the pH and calcium concentration were raised simultaneously using calcium carbonate (lime). Enhanced biodegradation was not induced when soil pH alone was raised with magnesium carbonate, nor when calcium alone was raised using calcium chloride. In limed sand treated monthly for 12 months, the degradation rate increased to where dissipation was complete within 24 h of application after the fifth metam-sodium treatment at pH 7.8 and after the eighth metam-sodium treatment at pH 6.8. Pesticide concentration was reduced, but not eliminated, at pH 5.8 and was unchanged at pH 4.8. When metam-sodium was applied bi- and tri-monthly, the degradation rate also increased when soil pH was raised with calcium carbonate, but to a lesser extent than with monthly applications. In an acid loam soil amended to the same pH values with calcium carbonate and treated monthly, there was no correlation between soil pH or calcium concentration and degradation. The results reveal the crucial interdependence of pH and calcium concentration in enhancement of biodegradation of soil-applied pesticides, but confirm that the phenomenon ultimately depends on interaction with soil type and frequency of application factors, all of which probably together act to affect the abundance, composition and activity of the soil microbial biomass.

摘要

长期以来,土壤中农药的生物降解增强一直与土壤pH值高于约6.5 - 7.5相关,但鉴于土壤钙浓度在pH值高于该范围时呈指数增加,此前尚未研究过与钙的混杂或相互依存可能性。在天然酸性砂质土壤(在0.01 M氯化钙中测得pH值为4.2)中,通过多次处理可轻易地从头诱导广谱杀生物剂甲基异柳磷的生物降解增强,但前提是使用碳酸钙(石灰)同时提高pH值和钙浓度。单独用碳酸镁提高土壤pH值时,或单独用氯化钙提高钙浓度时,均未诱导生物降解增强。在每月用石灰处理12个月的砂质土壤中,在pH值为7.8时进行第五次甲基异柳磷处理后,以及在pH值为6.8时进行第八次甲基异柳磷处理后,降解率提高到施用后24小时内消散完全的程度。在pH值为5.8时,农药浓度降低但未消除,在pH值为4.8时保持不变。当每两个月和每三个月施用一次甲基异柳磷时,用碳酸钙提高土壤pH值时降解率也会增加,但程度低于每月施用的情况。在用碳酸钙将酸性壤土改良到相同pH值并每月处理的情况下,土壤pH值或钙浓度与降解之间没有相关性。结果揭示了pH值和钙浓度在增强土壤中农药生物降解方面的关键相互依存关系,但证实该现象最终取决于与土壤类型和施用频率因素的相互作用,所有这些因素可能共同作用影响土壤微生物生物量的丰度、组成和活性。

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