不同pH 值土壤及其浸提液对羊草种子萌发和幼苗生长的影响

研究了不同pH值土壤以及重度盐碱土和非盐碱土浸提液对羊草(Leymus chinensis)种子萌发及幼苗生长的影响。不同pH值土壤由配土和调酸两种方式取得, 前者由重度盐碱土(pH = 10.24)与非盐碱土(pH = 7.49)按不同比例配制, 后者是由重度苏打盐碱土经硫酸调酸处理得到。配土发芽的实验结果表明, 当pH值在7.49-9.14时, 种子的发芽率均在50%以上, 且幼苗能够正常生长; pH = 9.53时, 羊草种子的发芽率低于50%, 仅部分幼苗个体能够成活; 当pH > 9.86时, 幼苗在萌发后50天左右全部枯死。说明羊草种子个体萌发期最大耐受pH值在9.14-9.53之间。重度苏打盐碱土调酸发芽实验结果表明, 当调酸后 的土壤pH值降至7.0-10.0时, 均能显著促进羊草种子的萌发, 且幼苗生长正常。确定了羊草种子萌发的最适pH值为8.0-8.5。土/水比为1: 1的非盐碱土浸提液能够显著提高羊草种子发芽率, 而重度苏打盐碱土浸提液对羊草种子萌发没有产生显著抑制。     

NaCl分根胁迫对羊草幼苗生长及其生理生化特性的影响

在自动控制的遮雨棚中,研究了200 mmol·L-1NaCl胁迫对不同分根处理羊草幼苗生物量、活性氧代谢以及渗透调节物质含量的影响.结果表明:单一胁迫根茎(RHS)、单一胁迫根系(ROS)以及同时胁迫根茎和根系(RHSS)3种处理方式下羊草幼苗各器官干重均低于对照,且大体呈现RHSS>ROS>RHS趋势.在RHS和ROS处理下,羊草叶片和根茎SOD、POD、CAT活性及MDA含量均无显著差异;RHSS处理时根系中SOD、CAT活性相比ROS处理显著降低.3种处理下根茎和根系MDA、可溶性糖、脯氨酸含量均显著高于对照,可溶性糖、脯氨酸含量在RHS和ROS处理间存在显著差异.可见,根茎在羊草响应盐胁迫的生理过程中与根系具有类似的功能;盐胁迫下羊草不同器官同一抗氧化酶对活性氧淬灭具有不同的作用,与POD相比不同器官SOD和CAT作用可能更大;根茎可能参与光合同化物——可溶性糖在羊草地上部和地下部的调节运输,且协同根系增强了羊草对盐胁迫的耐性作用.     

根茎在羊草响应短期NaCl胁迫过程中的作用

根茎是根状茎型克隆植物的特有结构,在养分储存、运输和分蘖茎的形成等方面起关键性作用。然而有关根茎生理学方面的研究却十分匮乏。为了探讨根茎在植物感应环境胁迫中的作用, 本文以羊草(Leymus chinensis)为实验材料,研究和比较了短期NaCl胁迫根、根茎、根和根茎3种处理方式下羊草对盐胁迫的响应。试验结果表明:200 mmol·L^-1 NaCl处理羊草根、根茎、根和根茎24 h,显著(p<0.05)降低羊草叶片净光合速率和蒸腾速率,增加叶片渗透浓度与脯氨酸含量;其中同时处理根和根茎叶片,蒸腾速率和净光合速率的降低程度显著高于分别处理根和根茎。在分别处理根与根茎的情况下,叶片含水量、脯氨酸含量、净光合速率、蒸腾速率均无显著性差异。不论单独胁迫根、根茎还是同时胁迫根和根茎,羊草根、根茎和叶片内Na⁺含量都显著高于对照,而羊草根、根茎和叶片内K⁺含量都显著低于对照。这些结果显示:1)根茎在羊草响应盐胁迫的生理过程中与根系具有类似的功能;2)羊草根茎在盐胁迫条件下能够有效地吸收Na⁺;3)鉴于根茎的生物量和表面积都明显地低于根系,在盐胁迫下羊草根茎吸收Na⁺的效率高于根系。     

不同pH值土壤及其浸提液对羊草种子萌发和幼苗生长的影响

研究了不同pH值土壤以及重度盐碱土和非盐碱土浸提液对羊草(Leymus chinensis)种子萌发及幼苗生长的影响。不同pH值土壤由配土和调酸两种方式取得,前者由重度盐碱土(pH=10．24)与非盐碱土(pH=7．49)按不同比例配制,后者是由重度苏打盐碱土经硫酸调酸处理得到。配土发芽的实验结果表明,当pH值在7．49-9．14时,种子的发芽率均在50％以上,且幼苗能够正常生长;pH=9．53时,羊草种子的发芽率低于50％,仅部分幼苗个体能够成活;当pH>9．86时,幼苗在萌发后50天左右全部枯死。说明羊草种子个体萌发期最大耐受pH值在9．14-9．53之间。重度苏打盐碱土调酸发芽实验结果表明,当调酸后的土壤pH值降至7．0-10．0时,均能显著促进羊草种子的萌发,且幼苗生长正常。确定了羊草种子萌发的最适pH值为8．0-8．5。土／水比为1:1的非盐碱土浸提液能够显著提高羊草种子发芽率,而重度苏打盐碱土浸提液对羊草种子萌发没有产生显著抑制。     

羊草无性系构件在不同环境下的可逆性变化

对温室内栽培羊草,人为控制温度及光照强度的条件,观测无性系构件的生长与分化的结果表明,羊草的无性系构件生长存在明显的可塑性变化,长时间的低温显著抑制羊草根茎和无性小株的分化,而对分蘖无明显抑制作用,遮荫显著抑制根茎和无性小株的分化,但对分蘖的影响并不显著,羊草的这种生态的适应特征有利于对环境变化的适应     

生活污水尾水灌溉对麦秸还田水稻幼苗及土壤环境的影响

通过盆栽试验研究了麦秸还田下生活污水尾水灌溉对水稻幼苗和土壤环境的影响.测定了不同处理水稻幼苗根系形态、根系活力、分蘖、株高、干物质累积量、土壤亚铁、有机酸、酶活性.结果表明: 与自来水灌溉相比,不施化肥氮时,生活污水尾水灌溉显著提高了水稻移栽后41 d的分蘖数和根系活力;正常施氮肥时,生活污水尾水灌溉显著促进了水稻根系和植株生长,根长、根表面积、根体积、根系活力、水稻分蘖数和干物质累积量均显著高于自来水灌溉处理.生活污水尾水灌溉处理显著降低了土壤Fe²⁺和有机酸含量,土壤脲酶、过氧化氢酶活性等显著提高.生活污水尾水灌溉和施氮耦合能有效缓解秸秆还田初期对水稻幼苗生长的不利影响,改善水稻生长状况,提升土壤肥力和质量.     

羊草无性系构件在不同环境下的可塑性变化

对温室内栽培羊草,人为控制温度及光照强度的条件,观测无性系构件的生长与分化的结果表明,羊草的无性系构件生长存在明显的可塑性变化,长时间的低温显著抑制羊草根茎和无性小株的分化（Ｐ＜０．０５）,而对分蘖无明显抑制作用．遮荫显著抑制根茎和无性小株的分化（Ｐ＜０．０５）,但对分蘖的影响并不显著．羊草的这种生态适应特征有利于对环境变化的适应．     

不同贮藏条件和发芽方法对羊草种子萌发的影响

贮藏条件(温度、水分和贮藏介质)和发芽方法(发芽床种类×播种方法)是影响羊草种子萌发的重要因素.研究了4种贮藏条件(4 ℃低温干贮、自然室温干贮和非盐碱土低温湿贮、盐碱土低温湿贮)、3种发芽床(滤纸、非盐碱土与盐碱土)和2种播种方法(表面与内部播种)对羊草种子发芽率的影响.结果表明,与室温干贮相比,低温干贮可以提高羊草种子的发芽速率和整齐度,但对最终发芽率没有显著影响.盐碱土低温湿贮显著降低羊草种子发芽率(28.8%);非盐碱土低温湿贮可显著提高羊草种子的发芽率(73.7%).6种组合发芽方法的发芽率大小和顺序依次为：非盐碱土表发芽法(89.3%)>纸间发芽法(68.0%)>纸上发芽法(64.0%)>非盐碱土内发芽法(61.3%)>盐碱土表发芽法(25.6%)>盐碱土内发芽法(6.0%).     

基因型多样性对羊草种群年龄结构的影响

基因型多样性作为遗传多样性的重要组成部分,不仅在群落水平,而且在种群水平均可以发挥重要生态作用。以羊草（Leymus chinensis）为研究对象,设置5种基因型多样性梯度试验控制小区,进行基因型多样性对羊草种群年龄结构的影响研究。结果表明：随基因型多样性梯度的逐步增加,2a分蘖株生物量和数量均显著增加（P<0.05）;1-4龄级羊草根茎生物量、长度和干物质积累量多数呈极显著性增加的变化趋势（P<0.01）。在1、2、4、8和12种基因型多样性梯度时,分蘖株生物量及数量年龄结构均以1a或2a分蘖株所占比例为最高,年龄结构表现为增长型或稳定型;而羊草种群根茎生物量和长度也以2a根茎所占比例为最高,年龄结构表现为稳定型。随基因型多样性水平的增加,羊草种群分蘖株数量和生物量的年龄结构从增长型向稳定型过渡,但根茎长度和生物量的年龄结构均为稳定型。12基因型多样性水平的4龄级分蘖株和根茎的特征高于其他基因型多样性水平。因此,在不同基因型多样性水平羊草种群分蘖株和根茎具有增长型或稳定型的年龄结构,适当的基因型多样性数量显著促进了各龄级羊草分蘖株和根茎的生物量和数量特征的升高,但高度的基因型多样性水平会增加羊草种群中高龄级的分蘖株和根茎所占的比例,种群发展表现出衰退信号。     

松嫩平原羊草草地土壤-植物间铁的动态研究

羊草草地土壤-植物间营养元素Fe的动态研究结果表明,土壤中全铁和有效铁含量均较低,羊草中Fe含量比较丰富．在生长季各时期,全铁和有效铁含量在土壤剖面分布上从上向下呈下降趋势,有效铁与有机质含量呈显著正相关,而与pH值呈显著负相关．全铁各月平均含量变化在生长季呈“V”型曲线,7月含量最低;有效铁平均含量从5～8月与全铁相似,8月后则逐渐减少．羊草各器官及枯落物Fe含量有很大变化,总的趋势是根>根茎>叶>枯落物>茎;羊草叶、茎的Fe含量在生长季中为波动型下降曲线,根茎、根及枯落物的Fe含量在生长季中为“V”型曲线．A层土壤富集有效铁的能力稍强．土壤中Fe活性平均为0．640％。从5月至8月逐渐升高,8月后逐渐下降,10月份最低．地下部的Fe向地上部的转移强度为5～7月下降,8月升高,随后又下降．地上部Fe向枯落物的转移强度平均为105．0％,与地下部Fe向地上部转移强度呈显著负相关。     

Neotyphodium Coenophialum-Infected Tall Fescue and Its Potential Application in the Phytoremediation of Saline Soils

The growth response of endophyte-infected (EI) and endophyte-free (EF) tall fescue to salt stress was investigated under two growing systems (hydroponic and soil in pots). The hydroponic experiment showed that endophyte infection significantly increased tiller and leaf number, which led to an increase in the total biomass of the host grass. Endophyte infection enhanced Na accumulation in the host grass and improved Na transport from the roots to the shoots. With a 15 g l^?1 NaCl treatment, the phytoextraction efficiency of EI tall fescue was 2.34-fold higher than EF plants. When the plants were grown in saline soils, endophyte infection also significantly increased tiller number, shoot height and the total biomass of the host grass. Although EI tall fescue cannot accumulate Na to a level high enough for it to be termed a halophyte, the increased biomass production and stress tolerance suggested that endophyte / plant associations had the potential to be a model for endophyte-assisted phytoextraction in saline soils.     

Preinoculation of lettuce and onion with VA mycorrhizal fungi reduces deleterious effects of soil salinity

The hypothesis that inoculation of transplants with vesicular-arbuscular mycorrhizal (VAM) fungi before planting into saline soils alleviates salt effects on growth and yield was tested on lettuce (Lactuca sativa L.) and onion (Allium cepa L.). A second hypothesis was that fungi isolated from saline soil are more effective in counteracting salt effects than those from nonsaline soil. VAM fungi from high- and low-salt soils were trap-cultured, their propagules quantified and adjusted to a like number, and added to a pasteurized soil mix in which seedlings were grown for 3–4 weeks. Once the seedlings were colonized by VAM fungi, they were transplanted into salinized (NaCl) soil. Preinoculated lettuce transplants grown for 11 weeks in the saline soils had greater shoot mass compared with nonVAM plants at all salt levels [2 (control), 4, 8 and 12 dS m^–1] tested. Leaves of VAM lettuce at the highest salt level were significantly greener (more chlorophyll) than those of the nonVAM lettuce. NonVAM onions were stunted due to P deficiency in the soil, but inoculation with VAM fungi alleviated P deficiency and salinity effects; VAM onions were significantly larger at all salt levels than nonVAM onions. In a separate experiment, addition of P to salinized soil reduced the salt stress effect on nonVAM onions but to a lesser extent than by VAM inoculation. VAM fungi from the saline soil were not more effective in reducing growth inhibition by salt than those from the nonsaline site. Colonization of roots and length of soil hyphae produced by the VAM fungi decreased with increasing soil salt concentration. Results indicate that preinoculation of transplants with VAM fungi can help alleviate deleterious effects of saline soils on crop yield.     

黄河三角洲盐碱土壤中AM真菌的初步调查

2000年3月－2001年2月对黄河三角洲盐碱土壤中5种优势植物柽柳（Tamarix chinensis),芦苇（Phragmites communis),碱蓬（Suaeda glauca),獐毛（Aeluropus littralis var.sinensis) 和刺儿菜（Cirsium setosum)根围内丛枝菌根（arbuscular mycorrhiza,AM)真菌进行了长期定点调查,结果表明,AM真菌在这5种植物根围土壤内都有分布,但多样性较低,尤其在冬季,AM真菌种的丰度和孢子密度分别在夏季降低了18．0％和61．6％,不同深度土层中AM真菌的分布存在诸多差异。     

盐土和沙土对新疆常见一年生盐生植物生长和体内矿质组成的影响

选用古尔班通古特沙漠南缘荒漠-绿洲交错带常见的一年生盐生植物盐角草、刺毛碱蓬、叉毛蓬、猪毛菜和碱地肤为材料,比较了它们在原状盐土和沙土中的生长及体内矿质元素组成的差异。结果表明：① 原状盐土0—100 cm各土层的pH值低于沙土,但电导率和含水量明显高于沙土;② 原状盐土中生长的植物干重是沙土中生长植物干重的7—118倍,后者的根冠比是前者的2—6倍。③ 体现肉质化程度的地上部含水率为52%—81%,中低耐盐植物含水率在两种土壤中差异显著,强耐盐植物差异不显著;④ 5种一年生盐生植物地上部氮浓度为11—34 g/kg,在有效氮含量高的盐土上植物氮浓度也高;磷浓度为1—4 g/kg,在有效磷高的盐土上植物磷浓度也较高（盐角草除外）;但沙土中的植物地上部钾浓度明显高于盐土中植株的地上部钾浓度,这与两种土壤在0—60 cm土层中的钾浓度差异相反;⑤ 尽管原状盐土0—100 cm土层中的水溶性钙、镁、钠、氯、硫浓度显著高于沙土,盐土与沙土中生长的植物地上部钠、水溶性氯和硫的浓度比值远远低于土壤中的相应元素浓度的比值,甚至盐土中的植株钙、镁浓度等于或显著低于沙土中生长的植物。表明盐土不仅影响一年生盐生植物的生长,也显著影响这些植物对矿质元素的吸收和累积。一年生盐生植物能够选择性吸收不同生境中的矿质元素。本研究期望为进一步深入研究盐生植物耐盐的适应机制提供依据,也可为植物修复盐碱土的品种选择提供参考。     

The effect of regeneration burns on the growth,nutrient acquisition and mycorrhizae of Eucalyptus regnans F. Muell. (mountain ash) seedlings

This study was conducted to compare the effects on the growth of Eucalyptus regnans seedlings of unheated soil and soil heated to different extents (as indicated by soil colour–bright red or black) in burnt logging coupes, and to separate the effects of heating of the soil on direct nutrient availability and on morphotypes and effectiveness of ectomycorrhizae. Burnt soils were collected from three logging coupes burnt 2, 14 and 25 months previously and unbumt soil from adjacent regrowth forests. Compared to unburnt soil, the early seedling growth was stimulated in black burnt soil from all coupes (burnt 2, 14 and 25 months previously). Seedling growth was generally poor in red burnt soil, especially in soil collected 2 months after burning. However, the concentration of extractable P was extremely high in red burnt soil, especially in soil collected 2 months after burning. In black burnt soil, extractable P was increased in soil 2 months after burning, but not in the soils collected 14 or 25 months after burning. However, both total P content and concentration in seedlings were increased in all collections of black burnt soil. Frequency of ectomycorrhizae was high in seedlings grown in all black burnt soils, but the mycorrhizal mantles were poorly developed in seedlings in black burnt soil collected 2 months after burning. Seedlings were also ectomycorrhizal in red burnt soil, except in soil collected 2 months after burning. Fine root inocula from seedlings grown in black burnt soils collected 14 and 25 months after burning significantly stimulated both seedling growth and P uptake compared with the uninoculated control, whereas the fine root inocula from the seedlings grown in all the other soils did not. These results suggest that, in black burnt soil, both direct nutritional changes and changes in the ectomycorrhizae may contribute to seedling growth promotion after regeneration burns. The generally poor seedling growth in red burnt soils is likely to have been due to N deficiency as the seedlings in these soils were yellow-green and the tissue concentrations of N were significantly lower than in other treatments. This revised version was published online in June 2006 with corrections to the Cover Date.     

盐碱旱地转基因抗虫棉田昆虫群落多样性

棉花是耐干旱和耐盐碱的经济作物。随着土壤的盐碱化和干旱化, 在人口数量和植棉成本剧增的背景下, 我国黄河流域和长江流域棉花种植面积锐减, 棉花种植被迫向滨海盐碱地和内陆及西北干旱地区转移。本文于2013年和2014年在山东东营滨海盐碱地和河北枣强半干旱轻度盐碱地以非转基因棉(‘中棉所49’)为对照, 以转Bt基因棉(‘中棉所79’)为试验材料, 分别作施农药和不施农药处理, 于每年5月初到9月中旬, 调查取样点棉株及地面上害虫及其天敌的种类和数量, 并分析不同施药处理下转基因和非转基因棉田昆虫群落的生物多样性参数差异。结果表明, 施药和不施药转Bt基因棉田昆虫群落和害虫亚群落昆虫的个体总数均低于非转基因棉田, 其中昆虫群落和害虫亚群落个体数在二者之间差异显著; 转Bt基因棉田昆虫群落和害虫亚群落昆虫的多样性指数和均匀度指数均高于非转基因棉田, 而优势集中性指数均低于非转基因棉田, 但差异均不显著。施药条件下两种棉田的昆虫群落和害虫亚群落昆虫个体总数、多样性指数和均匀度指数均低于不施药棉田, 优势集中性指数均高于不施药棉田, 但转基因棉田和非转基因棉田之间无显著差异。表明转基因抗虫棉在盐碱旱地对棉田靶标害虫具有较好的控制作用, 棉田昆虫群落稳定性较高, 昆虫群落对外界的入侵和干扰缓冲能力强, 而化学农药的使用对昆虫群落杀伤力较大, 容易导致某种昆虫的抗性产生和昆虫群落的不稳定, 但比非盐碱旱地棉田昆虫群落生物多样性低, 棉田生态系统更简单。     

中国盐碱土壤中AM菌的生态分布

对我国盐碱土壤中丛枝菌根（Ａｒｂｕｓｃｕｌａｒ Ｍｙｃｏｒｒｈｉｚａ,ＡＭ） 菌的种属构成、生态分布状况进行了研究．结果表明,不同地区ＡＭ 菌种属构成不同,其种属组成、分布与土壤类型、碱化度和土壤有机质含量有关．盐渍化砂土、壤土和粘土中,Ｇｌｏｍｕｓ 属的真菌数量最多,Ａｃａｕｌｏｓｐｏｒａ 属次之,而Ｇｌｏｍｕｓ 属中的Ｇ．ｍｏｓｓｅａｅ 则是分布最为广泛的菌种．随土壤碱化度的增加,Ｇｌｏｍｕｓ ｍｏｓｓｅａｅ 出现频率随之相对增加．在一定范围内有机质含量越高,土壤中ＡＭ 菌种和属的种类就越多．ＡＭ 菌的种属组成因不同寄主植物而异,其中豆科植物根围中ＡＭ 菌分布的种属数量最多．     

不同生境条件下羊草种群无性系和有性生殖特征的比较研究

比较研究了东北草原不同生境条件下4个羊草种群无性系和有性生殖数量特征的差异,结果表明,由于各种群所处立地的资源（特别是土壤水分）,导致各种群在无性系（包括营养枝和根茎芽密度）和有性生殖（生殖枝密度、生殖技分化率、生殖贡献）等数量特征方面差异显著,尤其在低平原种群与沙的天种群之间最为显著,与沙丘种群相比,低平原种群营养枝平均密度高50％;根茎芽平均密度高30％以上;生殖枝密度平均值高200％以上。     

恢复措施对退化草地羊草种群有性生殖数量特征的影响

在封育和翻耙处理的退化羊草草地上,对羊草种群有性生殖的数量特征进行了比较研究．结果表明,翻耙样地羊草种群密度下降显著,生殖蘖密度变化不显著,生殖蘖穗长、节间长、生殖生长比率、穗节数、小穗数、小花数、饱满籽实数和结实率都有显著增长,籽实产量、净籽实重和千粒重分别是封育样地的2．68、3．49和1．3倍．在翻耙样地中,羊草种群发育有复小穗的生殖蘖比封育样地多16％,生殖蘖上复小穗的数量也显著增加,生殖蘖以相对少的小穗,生产了较多的小花和更多的籽实来提高种群的籽实产量．两个样地中羊草种群的生物量生殖分配在种群对生殖蘖RA1、生殖蘖对穗序RA4、穗序对籽实RA6 3个层次上无显著差异,而种群对穗序RA2、生殖蘖对籽实RA5的生殖分配差异显著,种群对籽实RA3的生殖分配差异极显著．     

Abscisic acid concentration,root pH and anatomy do not explain growth differences of chickpea (Cicer arietinum L.) and lupin (Lupinus angustifolius L.) on acid and alkaline soils

The ABA concentrations of leaves, roots, soils and transport fluids of chickpea and lupin plants growing in acid (pH=4.8) and alkaline (pH=8.0) soils and an acid soil with an alkaline subsoil and an alkaline soil with an acid subsoil were measured with the aim of explaining the poor growth of narrow-leafed lupins in alkaline soil. The ABA concentration in the leaves was higher in lupin than chickpea, but did not differ when the plants were grown in alkaline compared to acid soil. The ABA concentration of the roots and xylem sap of lupin did not differ significantly when grown in acid or alkaline soil. Chickpea roots and xylem sap had, however, lower ABA concentrations in acid soil. The ABA concentration in the soil solution was higher in the acid than in the alkaline soil. Roots of lupin and chickpea showed no suberization of the hypodermis or exodermis whether grown aeroponically or hydroponically and the pH of the cytoplasm did not change significantly when root cells of lupin and chickpea were exposed to external pHs of 4.8 or 8.0. The chickpea roots had greater suberization of the endodermal cells adjacent to radial xylem rays and maintained a slightly higher vacuolar pH than lupin in both acid and alkaline external media, but these small differences are insufficient to explain the reductions in lupin growth in alkaline soil.