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[通过研究葡萄糖-14C(U)的矿化作用以及放射性在土壤各组分中的分布,探讨除草剂敌稗施用于土壤的效果(实验室和田间试验)]

[Effect of application of a herbicide propyzamide into the soil by study of mineralization of glucose 14C(U) and distribution of radioactivity in various fractions of the soil (laboratory and open field tests)].

作者信息

Thibaud M C, Bastide J, Coste C M, Gadel F, Cahet G

出版信息

J Environ Sci Health B. 1983;18(2):229-52. doi: 10.1080/03601238309372366.

Abstract

The effects of the herbicide PROPYZAMIDE are studied in laboratory and field conditions. The modifications involved are characterized by measurement of 14C-glucose mineralization and radioactivity incorporation into the soil fractions. In laboratory conditions, temperature and moisture are kept stable and the experiment is performed during less than 24 hours. In these conditions, Kerb 50 (commercial formulation of propyzamide) and the emulsifier (material used in propyzamide formulation) exert little effect on 14CO2 evolution. In field conditions, propyzamide andKerb 50 are applied once at two different doses: at field rate (1,5 kg/ha) and twentyfold this rate. Essays are duplicated. The herbicide (propyzamide in Celanol and Kerb 50) and the emulsifiers alone (Celanol and the material used in propyzamide formulation) are applied on the soil surface (application date: 3.02.81). Two weeks later and then every month during four months, samples are taken to the depth of about 5 cm (Propyzamide migrates very slowly in the first centimeters of the soil). The characterization experiment is performed on 10 g soil samples by 14C-glucose incubation at 28 degrees C during two hours. 14CO2 evolved is measured after incubation and acidification with HCl. Then radioactivity distribution in the soil is counted after chemical fractionation of soil. This distribution is about 10-16.5% as 14CO2, 22-37% in the acid-soluble fraction, 10-25% in the alkali-soluble fraction and 15-45% in the human fraction (measured as 14CO2 evolved after combustion). This distribution is little modified by the herbicides or the emulsifiers but its evolution is significantly related to environmental conditions (temperature). Nevertheless a few modifications are observed. They can be due to the herbicide propyzamide itself but the emulsifiers and the degradation products of propyzamide can also influence the measurement (After forty days in the soil, 70-95% of the starting active ingredient have disappeared). They can also be a result of the initial effects of the products (modification of the microflora and of the environment).

摘要

在实验室和田间条件下研究了除草剂敌稗的效果。所涉及的变化通过测量14C - 葡萄糖矿化以及放射性掺入土壤组分来表征。在实验室条件下,温度和湿度保持稳定,实验在不到24小时内完成。在这些条件下,克草胺50(敌稗的商业制剂)和乳化剂(用于敌稗制剂的材料)对14CO2释放的影响很小。在田间条件下,敌稗和克草胺50以两种不同剂量各施用一次:田间用量(1.5千克/公顷)和该用量的二十倍。实验重复进行。除草剂(敌稗在西拉诺尔中的制剂和克草胺50)以及单独的乳化剂(西拉诺尔和用于敌稗制剂的材料)施用于土壤表面(施用日期:1981年2月3日)。两周后,然后在四个月内每月一次,采集深度约为5厘米的样本(敌稗在土壤最初的几厘米中迁移非常缓慢)。通过在28摄氏度下将10克土壤样本与14C - 葡萄糖孵育两小时来进行表征实验。孵育并用盐酸酸化后测量释放的14CO2。然后在对土壤进行化学分级后计算土壤中的放射性分布。这种分布以14CO2计约为10 - 16.5%,在酸溶性组分中为22 - 37%,在碱溶性组分中为10 - 25%,在腐殖质组分中为15 - 45%(燃烧后测量释放的14CO2)。这种分布受除草剂或乳化剂的影响很小,但其变化与环境条件(温度)显著相关。然而,观察到了一些变化。它们可能是由于除草剂敌稗本身,但乳化剂和敌稗的降解产物也会影响测量结果(在土壤中放置四十天后,初始活性成分的70 - 95%已消失)。它们也可能是产品初始效应(微生物群落和环境的改变)的结果。

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