艾叶叶绿素锌钠盐的制备及其稳定性研究

以艾叶(Artemisia argyi)为原料,通过超声波辅助提取得到叶绿素,经皂化、酸化、锌代等过程,制得叶绿素锌钠盐,并对其稳定性进行了初探。结果表明,该产品的水溶性较好,具有较好的耐热性,对氧化剂、还原剂不敏感,在p H为5~11的环境中均较稳定,但在光照条件下稳定性差。几种常见的食品添加剂和一些金属离子对叶绿素锌钠盐的影响小,但Fe~(3+)、Cu~(2+)、Al~(3+)、柠檬酸和维生素C对叶绿素锌钠盐的稳定性有较大影响。     

硫酸亚铁诱导根表铁膜形成对水稻吸收和转运铜锌的影响

通过水培条件下添加硫酸亚铁诱导水稻根表铁膜的形成,利用连二亚硫酸钠-柠檬酸钠-碳酸氢钠(DCB)溶液对根表铁膜进行提取后测定,采用扫描电镜-能谱仪(SEM-EDS)和X射线衍射仪(XRD)等手段对硫酸亚铁诱导产生的根表铁膜进行表征,并分析根表铁膜对水稻吸收铜锌的影响。结果表明,添加硫酸亚铁可以诱导根表铁膜在水稻根系表面产生,未处理的水稻根表Fe含量为731 mg·kg~(-1),80 mg·kg~(-1) Fe~(2+)处理下水稻根表Fe含量为53 562 mg·kg~(-1);SEM-EDS和XRD分析发现大量颗粒状含铁化合物附着于水稻根表。与未经硫酸亚铁处理相比,有根表铁膜水稻的铁膜中,其Cu含量最高增加73.16%,Zn含量最高增加112.10%;水稻根系Cu含量最高降低31.15%,Zn含量最高降低13.02%;水稻茎叶Cu含量最高降低19.50%,Zn含量最高降低25.56%。土壤添加硫酸亚铁可以显著降低水稻对Cu和Zn的吸收与积累。     

广西某铅锌矿影响区农田土壤重金属污染特征及修复策略

为了解铅锌矿影响区农田土壤重金属分布特征及探究污染农田的修复措施,以广西某铅锌矿影响区为研究对象,分别采集影响区自然土壤和农田耕作层土壤样品41个和277个,同时分别采集62个蔬菜和35个粮食样品,分析重金属含量。结果表明,铅锌矿影响区耕作层土壤As、Cd、Pb、Cu、Zn和Cr含量范围分别为4.50~104.8、0.031~36.26、24.80~2989、16.90~251.6、79.90~11 500和24.0~222.0 mg·kg~(-1);与土壤基线值相比,6种重金属的超标率分别为1.4%、91.7%、60%、60%、60%和0。与《食品中污染物限量》(GB 2762—2017)中限值相比,大米样本As、Pb、Cd含量超标率分别为93%、86%、64%,玉米样本Pb、Cd含量超标率为100%、100%,叶菜类蔬菜As、Pb、Cd含量超标率分别为50%、100%、60%,根茎类蔬菜As、Pb、Cd含量超标率为23%、100%和100%,瓜果类蔬菜As、Pb、Cd含量超标率为14%、96%和100%。通过分析土壤和农产品重金属超标情况,确定As、Pb、Cd为优先控制的重金属,依据研究区土壤重金属污染空间分布特性,划为3个分区:轻度污染区(Cd污染区),建议采取活化剂+植物萃取去除污染物;中度污染区则采用钝化剂与低积累农作物结合的方式;重度污染区则不宜种植进入食物链的农作物,建议采取施加活化剂与种植超富集植物结合的方式降低土壤重金属含量。     

异源表达玉米ZmC3H54基因增强水稻的耐旱性

CCCH锌指蛋白是一类重要的转录调控因子。从玉米中分离得到一个受干旱和ABA诱导表达的CCCH型锌指蛋白基因ZmC3H54,通过构建过量表达载体并转化水稻来进一步研究其功能。 与对照组相比,转基因植株在干旱胁迫处理下具有更高的相对含水量与存活率以及较低的相对电导率,表明过量表达ZmC3H54基因可以提高转基因水稻的耐旱性。此外,转基因水稻幼苗对外源ABA敏感性更高。以上结果表明玉米ZmC3H54基因可能是通过ABA信号通路调控植物对干旱的耐受性。     

长株潭地区5种母质发育水稻土锌和铜及镍元素剖面分布特征

以长株潭地区5种母质发育的水稻土,即河沙泥、红黄泥、黄泥田、麻沙泥和紫泥田为研究对象,按土壤系统分类原则挖掘典型剖面24个及剖面土样137个,分析测定了土壤全量和有效态铜、锌、镍含量以及土壤pH值、颗粒分级组成、有机质、游离氧化铁含量,研究水稻土铜、锌、镍元素的剖面分布特征以及与土壤理化性质之间的关系。结果表明:剖面各层土壤全铜、全锌含量平均值随剖面加深逐渐降低,耕作层、犁底层、底土层全铜含量分别为26.82、21.54、18.54 mg/kg,全锌含量分别为75.84、66.00、63.19 mg/kg,全镍含量分别为18.40、17.50、18.23 mg/kg;土壤铜、锌、镍有效态含量平均值随剖面加深均逐渐降低,耕作层、犁底层、底土层有效铜含量分别为4.04、2.99、1.29 mg/kg,有效锌含量分别为4.77、2.76、1.14 mg/kg,有效镍含量分别为0.54、0.44、0.23mg/kg;黄泥田的全量和有效态铜、锌、镍含量均较高,麻沙泥的较低;土壤有机质含量是决定土壤有效态铜、锌、镍含量的主要因子,土壤游离氧化铁含量是决定土壤全铜、全镍含量的主要因子,全锌含量与土壤pH值、颗粒分级组成、有机质、游离氧化铁含量均无显著相关性。总体上,长株潭地区水稻土0～25 cm土体以及部分剖面土壤全层有效态铜和锌含量高于临界值(铜1.5 mg/kg、锌0.5 mg/kg),呈盈余状态,可满足浅根或中根作物对铜、锌的需求。     

锌的消化吸收机制研究进展

介绍了不同锌源的消化吸收特点、锌的吸收机制、分布和调节等方面的研究进展，为进一步研究锌的吸收及其在动物生产中的合理利用提供参考依据。     

Effect of high rates of zinc on several crops grown on an irrigated plainfield sand

Abstract

A field experiment was conducted to determine whether Zn applied for pathogen control could accumulate to a level which would be toxic to snapbeans, cucumbers, or corn. Zinc sulfate (ZnSO₄) was applied at rates varying from 0 to 363 kg Zn/ha on a Flainfield loamy sand to approximate 3, 9, 27 and 81 years of fungicidal treatment.

Even at the high rate of Zn, yields of snapbeans, cucumbers, or corn generally were not reduced. As rates of applied Zn increased, there was a corresponding increase in the level of Zn in the leaf tissue of all crops grown. At the high Zn rate, snapbean and cucumber leaf tissue accumulated over 350 ppm Zn. Available soil Zn was extracted with 0.1N HCl, EDTA, or DTPA. Highly significant correlations were observed between the Zn removed by each extractant and plant tissue Zn, thus, indicating that the various extractants were equally effective in predicting Zn uptake.

Very little downward movement of Zn was observed. Two and one‐half years after application, the Zn had leached to a depth of only 30 cm in the soil profile at the higher Zn rates.

These data indicate that application of Zn‐containing fungicides and bactericides should not cause a Zn toxicity problem on the Plainfield sand in the foreseeable future.     

Effect of zinc levels on phosphorous and zinc content in sand‐cultured soybeans

Soybeans (Glvcine max L.) cv. “Clark”; were grown in the greenhouse in sand‐filled plastic pots sub‐irrigated with Hoagland No. 1 solution to determine the possible inhibitory effects of Zn on the uptake of P. Zinc rates used were 0.05 (control), 0.25, 0.5 and 2.5 ppm. Yields equalled the control at Zn levels of 0.25 and 0.5 ppm, but plants grown in solutions containing 2.5 ppm Zn were stunted severely. Foliar Zn and P levels differed very little among Zn treatments. Zinc levels were highest and P levels were lowest, however, in the roots and stems of soybeans grown in solutions of 2.5 ppm Zn. Zinc and P uptake was significantly inhibited in the leaves, stems and roots of plants grown at the highest Zn rate. The recycling of wastes containing high Zn content could adversely affect plant growth by a suspected antagonism with P.     

Germination-enhancing and zinc-sparing roles for selenium in broccoli

Large areas of China have soils low in both available selenium (Se) and zinc (Zn). In order to investigate whether Se supplied as either selenate or selenite can increase germination and growth compared with low-Se controls we used broccoli, an important vegetable with anticancer effects, especially when biofortified with Se. Broccoli was grown under both Zn adequacy and Zn deficiency to determine whether interactions between these minerals affect plant growth. Selenite and selenate at a wide range of doses increased the speed and extent of germination. Both inorganic Se forms increased early root and shoot growth at low concentrations, with selenite having a stronger effect than selenate. A sand culture trial showed a similar growth increase due to low-dose Se under Zn deficiency but not under Zn adequacy. Conversely, at high Se levels, the results provided evidence from biomass, water use, photosynthesis and gas exchange that broccoli growth was inhibited at high Se levels, with selenite being more toxic than selenate. In this broccoli trial, the two Se forms were equally effective in increasing leaf Se concentration, whereas in most plants selenite is largely converted to organic Se forms and stored in the roots. This study suggests that Se, supplied either as selenate or selenite, may improve germination and growth in broccoli, especially on Zn-deficient soils. Field trials conducted on soils which are very low in both plant-available Se and Zn are needed.