Residue management for reducing evaporation in relation to soil type and evaporativity1

Abstract. Usual residue-management options are to remove the residue, use it as mulch with or without undercutting or to incorporate it into the soil. While the role of surface mulch in evaporation has been widely studied, the information on the effect on evaporation of mulch with undercutting or residue incorporated into soil, particularly in relation to soil type and evaporativity (E_o) is lacking. We studied the effect of wheat straw used in various ways on the course of evaporation loss from soil columns with three soils at Ludhiana, India and one soil at Bushland, Texas, USA, under two E_o's Energy-limited evaporation rates under mulch (E_om) followed the soil-specific relation E_om/E_o= a e^(bRes+cEo), where Res is residue rate t/ha and a, b and c are constants; E_o, is expressed in mm/d. In an effort to model the total evaporation (CE) during the energy-limited stage ‘U’ was obtained from appropriate CE versus time curves and (CE-U) was regressed over (t - ti)^0.5 to obtain the slope ‘α’ (Ritchie 1972) for the soil-limited evaporation stage. The observed ‘U’ was independent of mulch rate and E_o but was strongly affected by soil type, Values of ‘α’ decreased with increase in mulch rate and decrease in E_o and coarseness of soil. The otherwise short lived benefit of evaporation reduction with mulch per se, which peaked after a few days was maintained when residue was mixed with soil at the stage when evaporation reduction reached a maximum; this benefit continued for several weeks. Cumulative evaporation values computed from ‘U’ and ‘α’ agreed closely with the observed values under straw mulch for loamy sand and clay loam soils and for ‘undercut’ and ‘residue mixed’ treatments on all soils regardless of E_o, and for all situations under small E_o. However, for sandy loam and silt loam soils under E_o of 10 mm/d, the modified square root of the time function of Jalota et al. (1988) gave a better fit.     

Effect of recent cropping history and herbicide use on the degradation rates of isoproturon in soils

Five soil samples were taken from each of five fields with different crop management histories. Three of the fields were in an arable rotation, the fourth field was temporary grassland, and the final field was under permanent grass. Of the three arable fields, two had been cropped with winter wheat in three of the preceding 6 years, and the third had last been cropped with winter wheat once only, 6 years previously. With one exception, the winter wheat had been sprayed with the herbicide isoproturon. The rate of isoproturon degradation in laboratory incubations was strongly related to the previous management practices. In the five soils from the field that had been treated most regularly with isoproturon in recent years, <2.5% of the initial dose remained after 14 days, indicating considerable enhancement of degradation. In the soils from the field with two applications of the herbicide in the past 6 years, residues after 27 days varied from 5% to 37% of the amount applied. In soils from the other three sites, residue levels were less variable, and were inversely related to microbial biomass. In studies with selected soils from the field that had received three applications of isoproturon in the previous 6 years, kinetics of degradation were not first‐order but were indicative of microbial adaptation, and the average time to 50% loss of the herbicide (DT₅₀) was 7.5 days. In selected soils from the field that had received just one application of isoproturon, degradation followed first‐order kinetics, indicative of cometabolism. Pre‐incubation of isoproturon in soil from the five fields led to significant enhancement of degradation only in the samples from the two fields that had a recent history of isoproturon application.     

猪肾脏中氯丙嗪和异丙嗪残留检测方法的建立

建立了猪肾脏中氯丙嗪和异丙嗪残留量检测的高效液相色谱法。猪肾脏中残留的氯丙嗪和异丙嗪,用乙腈提取,再依次用酸化乙腈和正己烷净化,氮气吹干,甲醇溶解后,用Waters高效液相色谱系统,HypersilC18柱,UV检测器,用V(乙腈)∶V(水)∶V(0.5mol·L-1乙酸铵)(50∶49∶1)为流动相,流速1.2mL/min,波长254nm测定,内标法定量。结果表明,氯丙嗪和异丙嗪在猪肾脏中的最低检测限均为10μg/kg,组织中添加量为10μg/kg时,氯丙嗪和异丙嗪的回收率分别为83%和84%,批间变异系数均小于20%。该方法样品处理简单,可同时检测氯丙嗪和异丙嗪在猪肾脏中的残留量。     

蜂蜜中氯霉素残留量检测方法研究概况

综述了近几年来国内外蜂蜜中氯霉素残留检测方法.着重介绍了高效液相色谱法、毛细管电泳法、酶联免疫法、色/质联用分析法以及生物传感器法,并分别综述了各种方法的优势与不足,最后展望了蜂蜜中氯霉素残留检测的发展趋势.     

Logistic模型评价寒地果桑最佳采收期

[目的]评价牡丹江地区果桑最佳采收期.[方法]对牡丹江地区果桑果实发育情况进行观测,应用Logistic方程拟合果桑果实生长曲线.[结果]Logistic方程拟合优度(R2)为0.96295,拟合效果好,模型选择正确,预测结果较真.[结论]最佳采收期应不迟于果桑落花后第5.34周,牡丹江地区应在5月下旬进行采摘.     

莫比朗在柑桔和土壤中的残留动态研究

采用田间试验方法,研究了莫比朗在柑桔和土壤中的消解动态和最终残留。样品用乙腈提取,过Envi-Florial固相小柱净化,液相色谱紫外检测器检测,外标法定量。残留动态试验结果表明,施药浓度为推荐剂量的两倍时(有效成分120g·hm-2),莫比朗在柑桔中的半衰期分别为7.00～8.90d,土壤中为4.00～6.38d。在有效成分为60g·hm-2的剂量下,施药3次,施药后第21d柑桔中莫比朗残留量低于0.10mg·kg-1。     

诺氟沙星在水产动物体内的药物动力学及残留研究

概述诺氟沙星在水产动物体内的药物动力学及残留研究现状,阐明诺氟沙星的药代学参数、残留规律、其影响因素以及我国氟喹诺酮类药物的应用前景。     

二硫代氨基甲酸盐类(DTCs)杀菌剂残留分析方法综述

综述了二硫代氨基甲酸盐类(DTCs)杀菌剂及其代谢物的残留分析研究现状,并对当前主要的残留分析方法如分光光度法、气相色谱法、液相色谱法及液相色谱-质谱联用技术和毛细管电泳法进行了较为详细的比较、分析,对DTCs类杀菌剂残留分析方法的未来发展进行了展望。衍生化液相色谱法虽然操作步骤较繁琐、耗时长,但结果稳定可靠,并能区分不同结构类型,是目前重点且被广泛采用的方法,而同时测定DTCs类杀菌剂母体及其代谢物的串联质谱方法将是今后进一步研究的热点课题。     

戊唑醇分子印迹传感器制备及其农药残留检测的电学传感机理分析

以甲基丙烯酸为功能单体,戊唑醇(tebuconazole,TEB)为模板分子,乙二醇二甲基丙烯酸酯为交联剂,应用电化学聚合法制备了分子印迹电化学传感器(TEB-MIP/F-CNTs/GCE)。利用循环伏安法(cyclic voltammetry,CV)和交流阻抗法(electrochemical impedance spectroscopy,EIS)对新型传感器进行了表征,并用差分脉冲伏安法(differential pulse voltammetry,DPV)考察了新型传感器对戊唑醇的检测性能。结果表明:戊唑醇分子印迹电化学传感器具有一定特异性;传感器表观表面积比裸电极显著提高;新型传感器具有良好的印迹效果,相较于其他结构类似的三唑类化合物(如苯醚甲环唑),TEB-MIP/F-CNTs/GCE对戊唑醇表现出高效的识别能力,具有专一性和强选择性,且在C_(TEB)≤2.0×10~(-6)mol/L范围内传感器峰电流与C_(TEB)存在定量关系;数据模拟分析得到传感器的电学阻抗谱等效电路模型为R_1(CPE_1(R_2(CPE_2(R_3)))),计算各电极/传感器的等效电路中各元件参数,证明该模型能有效地模拟传感器检测戊唑醇的传感机理。该研究结果可为三唑类农药残留仿生免疫检测方法的建立提供技术支撑。     

司帕沙星在雏鸡体内药代动力学及残留的研究

选用30日龄健康海兰鸡65只,按5mg／kg体重口服给予司帕沙星,定期采样,以高效液相色谱法测定血浆、肝、肾、心、肺和肌肉中司帕沙星的含量,研究司帕沙星在鸡体内的药动学与残留。结果表明:司帕沙星在血液中经时过程符合一级吸收二室开放模型,其主要动力学参数如下:t1／2α0.9585h,t1／2β11.7447h,tmax0,6514 h,Cmax0.5271 μg／ml,AUC1.7908mg／L／h。肾脏、心脏的药时数据符合一级吸收二项指数方程,其主要动力学参数分别为:t1/2Ka0.3733 h、0.1530h,t1／2k1.3007 h、2.1013h,tmax1.01420h、0.6239 h,Cmax2.1104μg／ml、1.6721 μg／ml,AUC6.51764 mg／L／h、6.2286mg／L／h。司帕沙星在肝脏、肺脏、肌肉中的经时过程符合一级吸收三项指数方程,主要动力学参数分别为t1/2α0.3672 h、0.6156 h、1.5835 h,t1/2β3.9998 h、15.0271 h、12.0103h,tmax0.7458 h、0.7322 h、1.3726 h,Cmax4.4709μg／ml、2.5267μg／ml、0.9760μg／ml,AUC20.893 mg／L／h,27.242 mg／L／h、9.7943mg/L/h。建议司帕沙星在鸡体内的休药期为7d。