荒漠植物种子逆境萌发研究进展

对水分、温度、光照、沙埋深度、盐分胁迫及以上几种综合因素在逆境条件下对荒漠植物种子萌发的影响进行了综述。降雨次数、雨量大小、分布及土壤湿度是决定荒漠植物种子萌发的重要生态因子;温度是影响荒漠植物种子萌发的关键生态因子之一,变温有利于荒漠植物种子萌发;光照并非大多数荒漠植物种子萌发的必要条件,少部分荒漠植物种子萌发需要光照,有些要在黑暗中萌发,有些则对光照无特殊要求,光照对有些荒漠植物种子萌发有一定的抑制;不同沙埋深度具有不同的土壤湿度,土壤温度和光照等条件,综合调控荒漠植物种子的萌发;盐分胁迫抑制种子的萌发。荒漠植物种子的萌发在以上几种因素的共同协调作用下表现出一定的适应性。随着研究的不断深入和生态环境建设的需求,需要加强荒漠植物生理生态研究的深度和研究的系统性。     

西鄂尔多斯珍稀濒危植物长叶红砂种子萌发特征

珍稀濒危灌木长叶红砂是我国西北干旱地区荒漠植被中的古老残遗物种,对维持荒漠植被稳定具有重要作用.本文研究了长叶红砂种子特性,及其在不同光照、温度、土壤水分和沙埋等环境因子中的萌发策略.结果表明:长叶红砂种子具有高活力、高萌发率、耐贮存的特点,在光照和黑暗条件下均能很好地萌发.种子萌发的适宜温度为恒温20 ℃～25 ℃或变温15 ℃/25 ℃,萌发率高达93%.土壤含水量为2%时,种子开始萌发;土壤含水量为12%时,其萌发率最高,达89%.长叶红砂种子适宜的沙埋深度为1 cm,＞5 cm沙埋不出苗.沙埋深度对出苗率和幼苗生长高度的影响显著,而对幼苗质量的影响不显著.水分条件和沙埋深度是制约长叶红砂种子萌发和出苗的主要因素,而种子的高萌发率增加了幼苗生存的风险,不利于其应对荒漠极端环境变化.这种特性是长叶红砂濒危的重要原因之一.     

荒漠植物种子萌发对积雪覆盖变化的响应

以古尔班通古特沙漠10种不同生活型植物种子为对象,研究3种不同积雪覆盖变化(自然降雪、加倍降雪和去除降雪)对荒漠植物种子萌发的影响。根据种子室内萌发结果,将种子可分为高萌速萌、高萌缓萌、低萌速萌和低萌缓型4种萌发类型。总体而言,加雪处理对荒漠植物的种子萌发率具有正效应或无效应,而去雪处理则具有负效应或者无效应。将野外不萌发的种子于室内重新培养,结果显示,积雪变化对总萌发率(野外萌发+室内萌发)具正、负或无3种效应。研究表明,在荒漠生态系统中,植物种子在萌发类型上具有多样性,这种多样性与植物的生存环境密切相关。积雪覆盖可以通过影响植物种子野外萌发率或总萌发率来影响植物生存。不同植物种子萌发对积雪覆盖变化的响应策略大都与生活型无关。这种多样化的种子萌发响应模式,有利于荒漠植物群落在环境剧烈变化中保持结构和功能的稳定,是对环境长期适应的结果。     

青藏高原东缘61种常见木本植物种子萌发特性及其与生活史的关联

为了评价亚高山地带木本植物种子萌发对策及其与生活史关联, 该文对青藏高原东缘61种常见木本植物的种子萌发特征以及种子萌发与种子大小、扩散方式、海拔及生境的关系进行了调查分析。结果表明: 1) 61种植物的种子萌发率呈现偏斜、双峰分布。6种植物(9.8%)的种子萌发率大于80%, 13种(21.3%)的萌发率在60%~80%之间, 9种(14.8%)的萌发率在40%~60%之间, 8种(13.1%)的萌发率在20%~40%之间, 25种(41%)的萌发率小于20%, 其中8种植物的种子萌发率为零, 显示了该生境中木本植物的种子以休眠、低萌发率或连续稳定的萌发对策占优势, 以避免不利的环境因素。2)种子扩散方式是决定61种木本植物种间萌发率变异(R² = 24.1%, p < 0.001) 和萌发开始时间变异(R ²= 21.3%, p < 0.01) 的主要因素; 种子大小、母体植株的海拔和生境对种子萌发率和萌发开始时间几乎没有影响(p > 0.05); 风扩散的种子比脊椎动物扩散和无助扩散的种子有更高的萌发率(F = 9.219, p < 0.001) 和较早的萌发开始时间(F = 6.772, p < 0.01)。说明植物生活史特征如种子萌发与扩散方式之间存在固有而紧密的联系, 扩散能力强的种子(如风扩散)由于能散布到较远而空旷的生境, 可能避免了各种有害因素或个体竞争, 因而种子以较强的萌发能力进行拓殖; 扩散能力弱的种子(如无助扩散)由于其散布距离较近, 种子以休眠或降低萌发的方式来避免个体或同胞竞争以及各种有害因素, 以获得最大的生态利益并确保物种延续。     

荒漠一年生植物异时萌发研究进展

荒漠一年生植物在严峻的环境条件下形成其特殊的萌发时间格局,即种子异时萌发:在特定条件下,同胞种子群形态一致的部分种子可以即时萌发,而另一部分仍保留在种子库中的现象。目前对荒漠一年生植物的异时萌发研究多集中在种子萌发特性、萌发后性状及繁殖分配等方面。该文系统总结了国内外种子异时萌发性的研究工作,主要内容包括:1)种子异时萌发的概念;2)具有异时萌发性的一年生植物种类及分布;3)异时萌发对植物生活史类型及模式的影响;4)异时萌发的植株在表型响应上的不同,如存活率、物候特征、繁殖产量、生物量分配等;5)异时萌发的生物学和环境因素。在综述文献的基础上,对今后的研究进行了展望,这有助于从更深层面理解荒漠一年生植物的异时萌发特性及其适应机制。     

环境因子对黄顶菊种子萌发的影响

黄顶菊是一种入侵性极强的外来杂草,其种子对环境的适应是其成功入侵的前提.通过室内条件下黄顶菊种子的物理特性、环境因子对其种子萌发及幼苗生长影响等方面的研究,可为探讨黄顶菊快速蔓延的原因与揭示黄顶菊成功入侵机制提供理论依据.结果表明,黄顶菊种子极多而轻与黄顶菊大面积扩散密切相关,温度、光照和种子埋藏深度是决定黄顶菊种子萌发的关键因素.黄顶菊种子萌发的温度范围为5～40℃,25℃最适于种子的萌发,25～35℃条件下有利于幼苗的生长;黄顶菊种子是光敏感型种子,在土壤表面的萌发率最高(74.44%),大于3cm的深层土壤中则不能萌发;pH 对黄顶菊种子的萌发影响不明显,但其幼苗在酸性条件下生长较好;黄顶菊种子的萌发能忍受一定的盐胁迫和干旱胁迫,但随着胁迫程度的加重,根长和苗长逐渐降低,50%的土壤含水量对黄顶菊种子萌发和幼苗生长比较适宜.     

外源激素ABA影响新疆荒漠盐生植物异子蓬异型种子萌发机制

以新疆荒漠盐生植物异子蓬(Suaeda aralocaspica)异型种子为材料,通过外源ABA直播(长时间)与浸种(短时间)处理分别研究不同浓度(0、0.5、1.0、5.0、10.0μmol/L)ABA对异型种子萌发、幼苗生长的影响,并通过定量PCR技术分析与萌发相关的ABC转运蛋白基因、丝裂原活化蛋白激酶激酶基因和DNA修复和转录因子基因在5.0μmol/L ABA处理下的表达规律,探讨外源ABA影响异子蓬异型种子萌发差异的机制。结果显示:(1)外源ABA直播处理下,褐色种子萌发及幼苗生长均受到明显抑制,黑色种子的萌发和幼苗生长在低浓度被促进,较高浓度被显著抑制;短时间浸种处理,能够同时促进异型种子的萌发及幼苗生长,且随ABA浓度增加促进效应增强。(2)直播萌发后,褐色种子中3个基因的表达量与对照相比均不变或降低表达(除了DNA修复和转录因子基因在8 h显著升高),黑色种子与对照相比均上调表达(除了ABC转运蛋白基因在8h显著下调);短时间浸种萌发后,褐色种子中3个基因的表达量均比对照显著升高,黑色种子中升高不明显。基因表达规律与种子萌发结果趋势一致,暗示ABA浸种可能触发了异子蓬种子萌发内在机制并对随后的萌发过程产生促进作用。而黑色种子对ABA处理表现出较好的萌发响应,可能是其幼苗能抵御荒漠地区逆境环境的重要原因。     

南亚热带森林木本植物种子萌发和储存

研究了南亚热带森林90种木本植物的种子和果实的大小、含水量等特征及种子萌发,并对其中有足够萌发个体的种(45种)进行了萌发分析和对有足够萌发个体和足够种子的种(41种)进行了种子或果实储存对萌发影响的研究.肉质果实种子和肉质种子萌发率较干燥种子高,两者差异显著.大多数种播种60 d内萌发.肉质果实的种子和肉质种子较干燥种子的休眠期长,留土萌发种子较出土萌发种子休眠期长.大种子种与小种子种之间、夏季成熟的肉质果实的种子与冬季和春季成熟的肉质果实的种子之间休眠期长短差异不显著.萌发率与新鲜种子含水量无显著的相关,但种子中水分含量的减少明显影响萌发率,尤其是在种子自然干燥的最初3 d.当种子的水分含量减至20%(约在种子自然干燥10～14 d)时,种子萌发率降至很低.萌发率随储存时间(密封,(4±1) ℃)而下降,但储存一个月下降不大(-8.3%),储存3个月后,显著下降.果实储存与种子储存之间、大种子种与小种子种储存之间、肉质果实的种子和肉质种子储存与干燥种子储存之间,萌发率差异一般不显著.     

温度、基质对泡泡刺种子萌发的影响

研究了温度、种子大小和基质对荒漠植物泡泡刺种子萌发的影响.结果表明:无论是滤纸还是沙子基质上,泡泡刺种子的萌发率、平均萌发时间和萌发率指数受温度的影响显著,而受种子大小的影响不显著.在沙子处理中,较高的萌发率发生在恒温25℃～35℃和变温20℃/30℃,10℃时萌发率较低.平均萌发时间随着温度的上升而呈下降趋势.在滤纸和沙子基质中,泡泡刺萌发的基本温度、最佳温度和最高温度分别为9.0℃、25.3℃、45.2℃和4.8℃、34.1℃、45.0℃.从4.8℃～45℃,泡泡刺种子可萌发的热量范围广,说明了泡泡刺定植的高度潜力.在荒漠生态系统恢复中,这种特性可使泡泡刺成为较好的候选者.     

霸王果翅及其浸提液对种子萌发的影响

在室内控制条件下,研究了霸王果翅对其种子萌发及果翅浸提液对霸王、红砂与无芒隐子草3种荒漠植物种子萌发的影响.结果表明:(1)果翅可完全抑制霸王种子的萌发.具有完整果翅的霸王种子萌发率为0;剥去果翅后霸王种子萌发率最高达91%;果翅刺破后其发芽率为4O%;而将种子与剥离后的果翅一起培养,其发芽率为88%.(2)果翅浸提液在低浓度条件下(0.025 g/Ml)对3种供试种子的萌发率均无显著影响.但高浓度浸提液(>0.025 g/Ml)则均显著降低种子萌发率;不同浓度浸提液均显著降低3种种子的萌发速率,对其胚根生长亦存在显著抑制作用;但对胚芽生长的影响则表现为低浓度(0.025 g/Ml)具促进作用,而高浓度具抑制作用.研究表明,霸王果翅可引起种子休眠,其浸提液中的萌发抑制物是引起种子休眠的主要方式.     

濒危植物多毛坡垒种子萌发的生理生态特性

研究了多毛坡垒（Hopea mollissima）种子在自然条件下的寿命及成熟度、温度、光照、土壤水分条件对多毛坡垒种子萌发的影响,结果表明：多毛坡垒种子适宜萌发的温度范围是20～30℃,最适宜温度为25℃;光照对多毛坡垒种子的萌发没有显著性影响,但在周期性光照条件下以25～30℃萌发结果最好,全黑暗条件下以20～25℃萌发结果最好;种子适宜萌发的土壤含水量为20％～60％,最适含水量为50％～60％;种子成熟后在树上长时间宿存明显降低了种子的发芽率和活力;在室内自然摊放条件下,10天后发芽率减半,16天后完全丧失发芽能力。研究认为,该物种对热带湿性季节性雨林原生境有很强的依赖性,目前多毛坡牟的濒危状态主要是由于滥砍乱伐和森林破坏造成的,由于其种子具有顽拗性种子的一些特点,日前该物种宜采取活体保仔的方法,以就地保护为主,活植物迁地保护为辅。     

冻融过程对荒漠短命植物种子萌发的影响

荒漠区冻融交替显著改变土壤温度和水分条件,并进一步影响荒漠植物种子萌发.为解析荒漠土壤冻融过程对植物种子萌发的影响,本研究以古尔班通古特沙漠4种典型短命植物[东方旱麦草(Eremopyrum orientale)、卵果鹤虱(Lappula patula)、尖喙拢牛儿苗(Erodiumoxyrrhychum)和条叶庭荠(...     

生物土壤结皮对荒漠土壤种子库和种子萌发的影响

研究了腾格里沙漠东南缘在不同自然条件（风、温度、水分）下,人工固沙植被区（24龄、41龄、50龄）和相邻天然植被区的两种生物土壤结皮对荒漠土壤种子库和种子萌发的影响。结果表明,荒漠土壤种子库在苔藓结皮上的储量显著高于藻类结皮。随着生物土壤结皮的发育,种子萌发量在苔藓结皮上增加,在藻类结皮上减少。生物土壤结皮层的含水量对种子萌发有显著的影响（p〈0.05）,植物种子在湿润处理的生物土壤结皮上的萌发量高于干燥处理的生物土壤结皮上的种子萌发量。生物土壤结皮表层温度和亚表层温度对荒漠植物种子萌发无显著影响（p〉0.05）,但总体而言,对于苔藓结皮,植物种子在较高温度下的萌发量略高于在较低温度下的萌发量,而对于藻类结皮,植物种子在较低温度下的萌发量略高。     

绒毛番龙眼种子萌发生态特性的研究

就温度、光照、土壤水分条件对绒毛番龙眼 ( Pometia tom entosa( Bl.) Teysm.et Binn.)种子萌发的影响及种子寿命进行了研究 ,结果表明 ,绒毛番龙眼种子萌发的适宜温度为 2 0～ 35°C,最适温度为 30°C;周期性光照条件下的萌发优于全黑暗条件 ;适宜土壤含水量为 2 0 %～ 70 % ,最适为 6 0 % ;在室内自然摊放条件下 ,9d后发芽率减半 ,16 d后完全丧失发芽能力。研究认为 ,目前绒毛番龙眼的濒危状态主要是由于滥砍乱伐和森林破坏造成的 ,由于其种子具有顽拗性种子的一些特点 ,该物种宜采取活体保存的方法 ,以就地保护为主 ,活植物迁地保护为辅。     

Ecology of Salix variegata seed germination: Implications for species distribution and conservation in the Three Gorges region

The Three Gorges Project in China has brought significant changes to the region's riparian environment, posing serious challenges to biodiversity conservation. Salix variegata is a native shrub distributed on riverbanks in the Three Gorges reservoir region, and has important ecological function in the community. In this study, we studied the ecology of seed germination of S. variegata as efforts to understand its spatial distribution and develop conservation strategies. We found that soil type, soil moisture content and temperature all had significant effects on seed germination in S. variegata. Germination rate increased with the increasing soil moisture, while decreased in over-saturated soil. The germination rate in riverbank sand was higher than in sandy soil and clay loam. The optimal temperature for seed germination was 24 °C, under which 100% of germination was reached in 7 days. Seed viability and germination declined significantly with time after being released from fruits. The results suggest that soil moisture is the determining factor on seed germination, and influenced distribution of S. variegata. The tributary riverbanks above 175 m in the Three Gorges reservoir region can be used for the conservation of the species, as their fluvial patterns should have not been disturbed by the hydropower project.     

喀什霸王的结实和种子萌发特性

喀什霸王(Zygophyllum kaschgaricum)是生长于中国新疆南部荒漠环境的稀有种及二级保护植物。当前, 该物种在自然种群中呈分散式及片段化分布, 且种群密度低, 种群老龄化较严重。因此, 为了了解该物种种子萌发特性及其对荒漠环境的响应, 该文采用室内控制实验方法, 对该物种的自然坐果率、结籽率、种子吸水特性、种子休眠和萌发特性及对干旱胁迫的响应进行了比较研究。结果表明: 喀什霸王在自然种群中的坐果率及结籽率较低, 且种子的败育率较高。不同干藏时间种子的吸水速率间存在显著差异; 随着干藏时间的延长, 种子的吸水率逐步增强。刚成熟的种子在不同温度及光周期下均可萌发; 其中高温(10/20 ℃, 20/30 ℃)及黑暗条件下的萌发率比低温(10/5 ℃, 5/2 ℃)及光照条件下的萌发率高。不同干藏时间的种子在不同浓度赤霉素(GA₃)下的萌发率均较高; 但低温储藏时间对该物种种子的打破休眠及萌发率没有促进作用。以上结果说明该物种存在非深度生理休眠; 而干藏时间、高温且黑暗及高浓度(50 mmoloL ^-1) GA₃是打破休眠及促进种子萌发的最合适条件。高温条件下的干旱胁迫对喀什霸王种子萌发具有抑制作用; 春季和秋季降水量决定种子的萌发率。总之, 喀什霸王种子在物候上表现出的春秋季萌动及非深度生理休眠以提高幼苗存活力及保障种群稳定性, 是一种对新疆南部干旱及高温胁迫荒漠环境的适应策略。     

Crop protection by seed coating

Providence of sufficient and healthy food for increasing human population clears the importance of notice to increasing crop production in company with environmental loss reduction. Growth and yield of every plant with sexual reproduction, depends on germination & emergence of sown seeds. Seed is a small alive plant that its biological function is protection and nutrition of embryo. Biological, chemical and physiological characteristics of seed, affect on plant performance & its resistance to undesirable environmental conditions, and even on its total yield. So attention to seed and try to increase its performance is so important. One of the factors that cause reduction in germination percentage and seedling establishment, is seed disease. It's possible to control these diseases by treating the seed before planting it. Coating the seed with pesticides, is one of the ways to gain this goal. Seed coating is a technique in which several material as fertilizers, nutritional elements, moisture attractive or repulsive agents, plant growth regulators, rhizobium inocolum, chemical & pesticide etc, add to seed by adhesive agents and cause to increase seed performance and germination. Seed coating, leads to increase benefits in seed industry, because seeds can use all of their genetic vigor. This technique is used for seeds of many garden plants, valuable crops (such as corn, sunflower, canola, alfalfa,...) and some of the grasses. In this technique that was first used in coating cereal seeds in 1930, a thin and permeable layer of pesticide is stuck on seed surface and prevent damage of seedborn pathogens. This layer is melted or splited after absorption of moisture and suitable temperature by seed, and let the radical to exit the seed. In this approach materials are used accurately with seed, evaporation & leakage of pesticide and also adverse effects of some pesticides on seeds are diminished, and these factors cause to increase the accuracy and performance of pesticide, decrease their consumption, environmental pollution and costs. This technique in new and there is a few information about it. So after searching and studying about this technique this paper is written to introduce it and its applications in crop protection.     

Fire,aridity and seed banks. What does seed bank composition reveal about community processes in fire‐prone desert?

Questions: The relationship between fire, aridity and seed banks is poorly understood in plant community ecology. We tested whether there was a close correspondence between the seed bank and standing vegetation composition with time‐since‐fire in a desert. We also examined whether longer‐lived species showed seed limitation relative to more ephemeral species, as this could influence grass‐woody ratios in a major biome. Location: Dune hummock grasslands/shrublands of central Australia. Methods: The effects of time‐since‐fire on floristic and functional group composition were examined by comparing plots unburned since 1984 against plots that had been burned in 2002. Three methods were used to quantify seed abundances: a germination trial using heat and smoke application, a flotation method, and a sieving method. Results: Seed bank densities were very low (<3000 m^?2). Species similarity between the seed bank and standing vegetation was high at sites recently burned (0.86) and low in sites long‐since burned (0.52). The relative abundance of ephemeral species in the seed bank peaked in recently burned plots, but the relative abundance of seeds of woody species did not match the pattern of abundance in the standing vegetation. Remarkably, the dominant perennial grasses and woody species were either absent from the seed bank or present at extremely low abundances. Discussion: Differences in the relative abundance of ephemeral species between standing vegetation and seed bank relate to the post‐fire succession process. The small soil pool of seed from woody species may be explained by allocation to belowground carbohydrate storage over seed production. Field observations suggest, however, that production of strongly dormant seed can be prolific and that high levels of seed predation make this system strongly seed‐limited. The discovery of this seed bank syndrome indicates that shifts in grass‐woody ratios can be driven by the juxtaposition of unpredictable seed rain and fire events in these desert dunes. However, estimates of grass‐woody ratios due to changing fire regimes will be difficult to predict.