盐胁迫下真盐生植物与泌盐植物的渗透调节物质及其贡献的比较研究

分别用含有0、100、200、400 mmol L-1 NaCl的Hoagland培养液处理真盐生植物海蓬子(Salicornia europaea)、盐地碱蓬(Suaeda salsa),含有0、100、200 mmol L-1 NaCl的Hoagland培养液处理泌盐植物二色补血草(Limonium bicolor)、滨藜(Atriplex spongiosa)、獐毛(Aleuropus sinensis)和隐花草(Crypsis aculenta)幼苗.处理一定时间后测定其鲜重、干重、有机干重、有机和无机渗透调节剂、渗透调节能力、渗透势、c(Na)/c(K)、c(Suc)/c(SS)等.结果发现,在较适盐度下,实验植物的干鲜重、有机干重和含水量均随盐度增高而增大,而在高盐度下则大部分植物受到抑制.双子叶植物和单子叶植物的无机渗透调节剂Na+、Cl-含量均随盐度升高而增大,双子叶植物的增幅大于单子叶植物,c(Na)/c(K)也高于单子叶植物.双子叶盐生植物的有机渗调剂在渗调中的贡献随外界盐度的升高而降低,而单子叶盐生植物则相反,其可溶性糖含量远高于双子叶植物,蔗糖含量尤其突出,c(Suc)/c(SS)也大于双子叶植物.双子叶植物的渗透调节能力大于单子叶植物,真盐生植物的渗透调节能力大于泌盐植物.另外,6种植物的实测渗透势大于计算渗透势,证明实验植物中还有一些未测定的渗透调节物质.本文还讨论了双子叶植物与单子叶植物、真盐生植物与泌盐植物在渗透剂、渗透调节能力、c(Na)/c(K)、c(Suc)/c(SS)存在区别的可能原因.图3 表4 参24     

Growth and Cd accumulation of two halophytes and a non-halophyte grown in a non-saline and a saline soil with different Cd levels

Two halophytes, Salicornia europaea and Atriplex verucifera, and the non-halophyte Chenopodium album were grown in pots on sodic and non-sodic Iranian soils spiked with up to 100 mg Cd kg^?1. The halophytes grew best on the sodic soil in the absence of Cd spiking, while C. album performed better on non-sodic soil. Cadmium spiking reduced the growth of all plants, with Cd tolerance decreasing in the order S. europaea>A. verucifera>C. album. The observed order of Cd tolerance corresponds to the abilities of the plants to tolerate sodic soil properties. The variation of Cd concentration in shoots in response to sodicity was related to different mechanism, including dilution (C. album) Cd solubilisation by Ca²⁺ (S. europea) and Ca²⁺ competition for uptake and translocation of Cd (A. verucifera). Improved understanding of these complex interactions will help to design phytoextraction technology for Cd-polluted soils in arid regions.     

盐胁迫条件下三角滨藜叶片中盐分的积累与分配

用扫描电镜和能谱仪测定不同浓度NaCl胁迫2wk后的三角滨藜幼叶和成熟叶中Na 在细胞外和细胞内的分布情况,并利用原子吸收分光光度计测定叶片中Na 的积累量,同时还观测了盐囊泡及其与盐的积累、分泌之间的关系.结果表明,在盐胁迫下,三角滨藜叶片中的Na 积累量随根外溶液盐浓度的升高而增加,而盐囊泡的含盐量并无显著变化.同时发现,叶片中的Na 主要积累在细胞内.因此,可以认为,三角滨藜主要靠吸收并在细胞内积累Na 来降低渗透势,保证植株的水分吸收,而三角滨藜的盐囊泡在盐分分泌与抗盐中并无实质性作用.图2表3参12     

盐生植物在盐渍土壤改良中的作用

盐生植物盐爪爪〔Kalidiumfoliatum (Pall.)Moq.〕、盐地碱蓬 (SuaedasalsaL .Pall)、中亚滨藜 (AtriplexcentralasiatieaIljin)、西伯利亚白刺 (NitrariasibiricaPall) ,在中国禹城地区〔φ(N) =36°5 5′,λ(E) =116°40′〕含盐量较高 (1%～ 1.3%)的试验田中分别种植 .出苗后定苗 ,株密度n =80m-2 ,小区面积为 4m2 ,每种植物 3个重复 .种植前分别测定土壤Na+ 含量 ,N、P、K含量 ,有机质含量 ,细菌和真菌数量 .萌发后 15d测定植株干重、植株Na+ 含量 .在花芽形成期收获 ,再测定植物干重和植株Na+ 含量 ,以及土壤Na+ 含量 ,N、P、K含量 ,有机质含量 ,细菌和真菌数量 .结果发现 ,盐渍土壤种植 4种盐生植物 1个季度后 ,土壤Na+ 含量显著降低 ,每季盐爪爪从土壤中吸收Na+ 量 934 5 .6kg/hm2 ,盐地碱蓬吸收Na+ 量 6 85 1.4kg/hm2 ,西伯利亚白刺吸收 6 0 19.2kg/hm2 ,中亚滨藜吸收 6 0 98.4kg/hm2 .土壤有机质 ,N、P、K以及细菌和真菌数量也有不同程度的增加 .这再次证明 ,盐生植物是一类良好的吸盐植物 .并对盐渍土壤种植盐生植物后Na+盐降低、土壤肥力和微生物数量增加的原因进行了讨论 .表 7参 13     

Sorption of hazardous metals from single and multi-element solutions by saltbush biomass in batch and continuous mode: interference of calcium and magnesium in batch mode

Batch studies were performed to determine the interference of calcium (Ca) and magnesium (Mg) on the sorption of Cu(II), Cd(II), Cr(III), Cr(VI), Pb(II), and Zn(II) [from CuSO(4), K(2)Cr(2)O(7), Pb(NO(3))(2), Cr(NO(3))(3), ZnCl(2), and Cd(NO(3))(2)] by saltbush (Atriplex canescens) biomass. The results demonstrated that Ca and Mg at concentrations of at least 20 times higher than the concentration of most of the target metals did not interfere with the metal binding. The data show that the batch binding capacity from a multimetal solution at pH 5.0 was (micromol/g) about 260 for Cr(III) and Pb, and about 117, 54, and 49 for Cu, Zn, and Cd, respectively. The use of 0.1M HCl allowed the recovery of 85-100% of the bound Cu, Cr(III), and Pb, and more than 37% of the bound Cd and Zn. The column binding capacity for Pb was about 49 micromol/g from both the single and multimetal solutions, while it was, respectively about 35 and 23 micromol/g for Cr(III). The binding capacity for Cu and Zn from the single and multimetal column experiments was 35 micromol/g and less than 10 micromol/g, respectively. The stripping data from the single column experiment showed that 0.1M HCl allowed the recovery of all the bound Cu and Zn, 90% and 74% of the bound Pb and Cr(VI), respectively, and less than 25% of the bound Cd and Cr(III), while the stripping from the multimetal experiment showed that 0.1M HCl allowed the recovery of all the bound Cu and about 74%, 54%, 43%, and 40% of the bound Pb, Zn, Cd, and Cr(III), respectively.