镉在不同土壤和蔬菜中残留规律研究

研究了镉在不同类型土壤和蔬菜中的残留积累规律.结果表明,含镉污水灌溉是造成农田土壤镉污染主要原因之一.土壤中镉残留量随污水镉浓度增加而增高.土壤镉含量与蔬菜中镉含量呈显著正相关.供试土壤及蔬菜可食部分镉的累积顺序为:粘土>壤土;壤土蔬菜>粘土蔬菜,小白菜(叶)>萝卜(根)>莴苣(茎)>辣椒(果)>豇豆(豆).     

四种南京地产栽培野菜蛋白质营养价值的评价研究

4种传统野菜已在南京地区规模栽培利用。采用模糊识别法和氨基酸比值系数法,分别以鸡蛋蛋白质为标准蛋白 ,以WHO/FAO氨基酸参考模式为评价标准 ,对这4种野菜蛋白质营养价值进行了评价 ,并与6种常见蔬菜蛋白进行对照比较。结果表明 ,4种野菜蛋白质含量为2.3 %～5.0 % ,蛋白质中氨基酸种类齐全 ,其含量为77.73 %～89.36 % ,必需氨基酸占总氨基酸量的36.72 %～42.04 % ,第一限制性氨基酸为含硫氨基酸 (Met +Cys)。其蛋白质营养价值分别优于同科的一些常见蔬菜。     

天然植物单宁季铵盐改性絮凝剂的制备和性能评价

用植物单宁和二甲胺、甲醛及环氧氯丙烷进行季铵化反应 ,制得了JK A和JK B两种阳离子絮凝剂。测试了产品的红外光谱 ,并对两种絮凝剂处理效果进行了比较     

湛江市典型区域蔬菜硝酸盐和亚硝酸盐污染评价

在湛江市典型区域采集了14个蔬菜品种的28个样品,分析了样品中硝酸盐和亚硝酸盐的含量,对其污染状况及食用安全性进行了评价.结果表明:叶菜类硝酸盐含量普遍较高,有8个样品超标,根茎类和瓜果类硝酸盐含量均没有超标,而所有样品亚硝酸盐含量均较低.根据WHO/FAO规定的硝酸盐日允许摄入量换算得到的标准进行评价,青瓜、莲藕、葫芦瓜、花菜、包菜等品种食用较为安全,而萝卜、瓢瓜和生菜、大白菜等蔬菜经盐溃或煮熟后也可放心食用;但菜心、芥菜、通心菜、小白菜和油麦菜等蔬菜属于严重污染,食用可能会对人体健康带来风险.     

昆明市蔬菜及其土壤中铅、镉、铜和锌含量水平及污染评价

对昆明市蔬菜及其土壤中铅、镉、铜和锌含量水平进行了初步的调查并对其土壤污染进行了评价,结果表明蔬菜土壤重金属Pb、Cd、Cu、Zn均存在一定程度的污染,其中Pb、Zn为轻污染,Cd、Cu为中污染,土壤重金属综合评价为中污染.蔬菜可食部分Pb、Cd、Zn的含量均超过国家食品卫生标准和绿色蔬菜标准,依次为Pb、Cu、Cd、Zn.蔬菜中Pb含量过高与汽车尾气Pb污染有很大的关系.     

菜田土壤氮素淋失及其调控措施的研究进展

从菜田中硝态氮的动态变化、土壤氮素的矿化、硝态氮对地下水的影响等几方面概述了近年来国内外的研究进展，介绍了渗漏测定计法、土壤溶液提取器和15N同位素示踪技术等3种测定土壤氮素淋失的研究方法其应用前景；论述了影响菜田土壤氮素淋失的主要因素和降低菜田土壤氮素淋失的丰要调控措施；提出了今后菜田土壤氮素淋失应加强的研究方向。     

河北省藁城市蔬菜种植区化肥施用与地下水硝酸盐污染研究

通过农户问卷调查和地下水田间取样分析 ,主要对河北省藁城市蔬菜种植区的化肥施用与地下水硝酸盐污染现状进行了研究。结果表明 :2 0 0 1年藁城市蔬菜种植区化肥施用纯量为 1 4 0 8.6kg·hm-2 ,其中氮肥施用纯量为 84 0 .8kg·hm-2 ;藁城市各蔬菜种植模式下氮肥施用量由高到低的顺序依次为大棚 >温室 >中棚 >小棚 >地膜 >露地 ;温室、中棚和露地蔬菜区地下水硝酸盐含量最高值出现在 8月 ,而地膜蔬菜区则在 1 1月 ;各蔬菜种植模式对地下水影响的大小顺序为地膜 >中棚 >温室 >露地 ,影响因素主要有密集度、种植模式、种植年限、氮肥施用量和土壤质地等。     

5种水培蔬菜对金属元素富集水平研究

检测分析了5种水培蔬菜中4种常量金属元素、18种稀有金属元素以及10种重金属元素含量,并与对照组陆生蔬菜金属元素含量进行比较,评价水培蔬菜的食用安全性。结果表明,污染水体中水培蔬菜的金属元素富集水平是不同的。常量金属元素平均富集系数为2~150倍;稀有元素平均富集量总体上高于陆生蔬菜;重金属元素富集系数大多在10倍左右,与陆生蔬菜重金属元素含量相比,两者均在同一水平,低于国家2001年10月1日执行的蔬菜农产品安全质量标准。     

立柱无土栽培研究初报

立柱无土栽培研究初报龚颂福，李止正（中国科学院上海植物生理研究所上海２０００３２）关键词立柱无土栽培；蔬菜；花卉ＳＴＵＤＩＥＳＯＮＴＨＥＳＯＩＬＬＥＳＳＣＵＬＴＵＲＥＳＯＮＶＥＲＴＩＣＡＬＣＯＬＵＭＮＳ￥ＧｏｎｇＳｏｎｇｆｕａｎｄＬｉＺｈｉｓｈｅｎｇ...     

Photodegradation of polychlorinated dibenzo-p-dioxins and dibenzofurans in soil with vegetable oil

GOAL, SCOPE AND BACKGROUND: This study was carried out to investigate the effect of olive oil on the photodegradation of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in contaminated sawmill soil. Previous studies had shown that the solubility of PCDD/Fs in olive oil is high and a rapid photodegradation of PCDD/Fs takes place in olive oil when irradiated with ultraviolet (blacklight) lamps. The efficiency of this treatment method was evaluated under more practical conditions. These included the use of sunlight irradiation and a lower-grade olive oil, without a preliminary extraction of soil with olive oil. METHODS: A 1-cm layer of contaminated sawmill soil was blended with 20 weight-% of olive oil and exposed to sunlight for four weeks. In another experiment, a new dose of olive oil was added at the middle of the exposure period. The PCDD/F concentrations of the soils were monitored periodically. RESULTS AND DISCUSSION: A reduction in the concentration of 2,3,7,8-chlorinated PCDD/Fs by 59% and in WHO-TEQ in contaminated sawmill soil by 48% was attained after blending the soil with two doses (20 + 20%) of olive oil and exposing the mixture to sunlight for four weeks. Photodegradation with only one dose of olive oil was less efficient. This suggests that periodical additions of olive oil would be needed to maintain a proper degradation rate. After the oil additions, the WHO-TEQ content of the soil declined with first order reaction half-lives of 19.2 to 19.7 d. The overall half-life during the four-week treatment, however, was 30 d. CONCLUSION: A significant reduction in the PCDD/F concentration of aged sawmill soil can be achieved with a relatively simple olive oil-sunlight treatment. RECOMMENDATIONS AND OUTLOOK: Some theoretical and technological questions need to be solved before using the investigated soil decontamination method in larger-scale applications. The functions of vegetable oils in photodegradation processes should be studied in more detail. The amount of oil that is needed for a proper solubilisation and photodegradation of PCDD/Fs should be minimised. Moreover, special care should be taken to prevent mobilisation of PCDD/Fs to the surrounding environment and to avoid leaving bioavailable residuals of PCDD/Fs in soil.