121 resultados para open top chamber

em Chinese Academy of Sciences Institutional Repositories Grid Portal


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自工业革命以来,大气的C02浓度以前所未有的速度增加,已经由280μmol mol-1升高到了360μmol mol-l。据预测,到下个世纪中/末期,C02浓度将为目前的二倍。C02浓度升高及其引起的全球气候变化必将影响到植物的生长发育,进而对整个生态系统产生巨大影响。因此,有关C02浓度升高对各类生态系统的影响的研究引起了广泛关注,成为近年来的研究热点。早期的研究多数集中于考察C02浓度升高对植物个体水平生长发育的影响。然而,高C02对植物的效应严重依赖于具体物种和具体环境条件,使得基于由短期盆栽实验获得的研究结果不能够有效地预测自然生态系统的行为。因此,长期、原位处理实验越来越受到重视。由于原位研究的难度较大,目前这方面的研究还不是很多。有限研究结果显示,由于生境条件和种间关系方面的巨大差异,自然生态系统对C02浓度升高的反应迥异。 草原生态系统由于C02浓度控制上比较容易实现,而且其物质循环相对较快,因而一直是C02富集实验研究最多的一类植被,生态系统水平的研究更是如此。然而涉及的区域和草原类型并不多,不足以进行可靠预测。目前,关于C02升高效应,研究比较系统的草原生态系统主要集中在:美国Kansas的高草草原、美国California的一年生草原、瑞士西北部的石灰质草原、美国Colorado的矮草草原和一些牧场。我国总土地面积的40%为草地,类型丰富,然而相关研究不多,尤其是对自然生态系统的原位研究几乎为空白。 为揭示C02浓度升高对羊草草原生产力和碳平衡的效应,我们在中国科学院内蒙古草原生态系统定位研究站的永久羊草样地开展了两年的C02倍增实验(2001,2002)。在羊草样地选择相对均匀地段设置12个开顶式气室(直径1.8m),每个气室内分成4个小样方(0.5m×0.5m),其中6个气室在生长季给予加倍C02处理(约600μmol mol-l),另6个气室不补充C02(约300μmol moI-l)。地上部分用收割法取样,分种记录数量、高度和重量等指标,地下部分取样用环刀法。用Li-cor6400光合系统测定群落光合和呼吸速率。野外实验结束后,统一分析植物和土壤样品中的C、N等元素含量。另外,在内蒙古草原站院内设置了两组桶培实验,一组是取自羊草样地的带苗原状土,一组是取自羊草样地的混匀土,种上冰草(Agropyron cristatum)、紫花苜蓿(Medicago sativa)和无芒雀麦(Bromus inermis)的种子。2组桶培实验分别用两个水分梯度和两个C02梯度处理。水分处理分别为:浇水处理——每4天浇lOOOml水,相当于平均降雨量的160%;干旱处理——持续干旱,适时补水以保持植物不萎蔫,共浇水4000ml水。C02处理和取样方法与样地原位实验相同。主要研究结果和结论如下: 1)两年的C02加倍处理没有使羊草草原的生物量、植物种和功能型组成发生显著改变,桶培实验中,浇水处理显著促进了植物生长,原状土植物、种子苗实验的冰草和无芒雀麦对C02加倍处理同样不敏感,而种子苗实验的豆科植物紫花苜蓿在C02加倍处理下生物量显著提高。以上结果显示,由于水分和养分(特别是N)的限制,以及优势植物对C02的相对不敏感,C02浓度升高对羊草草原地上生物量和结构的效应相对不大。 2)羊草草原的根垂直分布在加倍C02条件下发生显著改变,但根生物量对C02加倍处 理相对不敏感。在4次取样中只有一次对C02加倍处理表现出显著变化,根长的变化与根生物量的变化不完全一致,根的比根长在加倍C02条件下增加。根垂直分布的变化趋势与降雨的时间分布相适应,干旱少雨时期C02使下层根量增加,多雨时期C02则使上层根量增加。以上结果显示,根的空间分布比根生物量对C02加倍处理更敏感。水分是根空间分布变化的驱动因子,加倍C02条件下,根空间分布的变化趋势倾向于优化对水分的充分利用。 3)加倍C02处理使羊草草原的群落光合速率显著提高,群落呼吸速率显著降低,因而使群落碳净输入量增加。土壤碳贮量占羊草草原碳总贮量的70%以上,碳总贮量及其组分(包括地上碳贮量、根碳贮量、土壤碳贮量)在两个C02浓度处理之问均没有显著差异。另外,加倍C02处理使羊草草原群落及其优势植物羊草的c:N比增加。以上结果显示,在加倍C02条件下羊草草原的碳净输入量增加,这意味着在未来高 C02条件F,羊草草原将作为碳汇对大气C02起反馈调节作用。其碳贮量对加倍C02 处理的不敏感与许多以前的研究结果相似,一般认为是由于土壤碳贮量本底太大, 掩盖了C02效应,这还有待于更长期原位实验的证实。羊草草原群落c:N比在高C02 浓度下的变化将影响凋落物降解、N素循环和动植物营养关系等,进而对生态系统 功能产生深远影响。

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臭氧属于二次污染物,它是由机动车、工厂等人为源以及天然源排放的氮氧化物(NOx)和挥发性有机物(VOCs)等一次污染物在大气中经过光化学反应形成的。O3 是光化学烟雾的主要成分,可对植物生长产生抑制。近几十年来,全球O3 污染的格局正在发生着巨大改变。由于北美及西欧等经济发达地区采取了有效控制臭氧形成前体物的措施,其空气中的O3 浓度在减少,而亚洲等经济发展中地区的O3 形成前体物的排放却在急剧攀升,导致大气中O3 浓度显著增加。中国经济的快速发展以及汽车保有量的迅猛增加导致O3 前体物的大量排放,许多经济较发达的地区空气中的O3 浓度超过了75ppb。由于O3 污染将导致农作物产量显著降低,因此,亚洲尤其是中国O3 污染对本地区农业生产的影响引起了国内外科学家的广泛关注。然而,在中国开展的关于O3 对植物生长及生产影响的研究相对较少,但已有的几篇研究报道确实指出目前中国部分地区的O3 浓度可导致冬小麦产量大幅下降,并预测到2020 年由O3 污染将引起小麦产量进一步降低。 植物对臭氧的反应或敏感性取决于诸如叶片导度、叶片结构及生化解毒等很多方面。首先,由于高叶片导度将吸收较多的臭氧量,因此,叶片导度通常被认为是决定抗性最为重要的因子。处于湿润条件下的植物,通常具有较高叶片导度,受到臭氧危害的程度一般也较大。其次,植物抗氧化胁迫能力的大小也决定着其对臭氧的敏感性。同一植株的老叶首先表现出伤害症状,这是由于老叶的抗氧化能力差于新叶,体现在抗坏血酸和谷胱甘肽含量及抗坏血酸氧化物酶和谷胱甘肽还原酶活性低于新叶。另外,叶片对臭氧的敏感程度与其叶片结构关系密切,拥有较大的细胞间隙对抗污染特性至关重要,由于叶片上表面的栅栏组织较海绵组织致密,因此通常较早表现出伤害症状。 影响植物对臭氧反应的环境因子很多,诸如光照、水气压亏、温度等。由于臭氧主要通过气孔进入植物体内,因此目前的研究主要集中在能显著调节气孔导度的环境因子,如土壤水分状况和在未来可能会与大气中臭氧浓度同步增加的CO2 浓度。CO2 浓度升高可降低植物的气孔导度,因此,CO2 浓度升高可减少叶片对O3 的吸收量。同时,大气CO2 浓度升高可提高净同化速率,可导致气孔的部分关闭而减少蒸腾,从而显著提高植株的水分利用效率,最终促进作物生长并提高产量。然而,二者对作物产量的交互影响尚不明确。水分胁迫被认为是影响O3 对植株伤害的一个重要环境因子。与正常供水相比,水分胁迫常常伴随着气孔导度的降低,导致进入到植株体内的O3 量相对较少而减轻植株受到的伤害程度。然而水分供应不足本身将导致小麦生长降低及产量下降。因此,水分亏缺可能会保护植株免受O3 伤害,同时也可能会加剧对植株的胁迫。 高浓度臭氧环境下,植物表现出较低的气孔导度。但研究表明,对臭氧敏感性不同的植物其气孔导度对臭氧的反应程度不同。臭氧对气孔的作用将影响植物生产力,同时也将影响植物对其它环境胁迫如干旱等的反应。短时间臭氧熏蒸小麦导致叶片细胞膜系统受损、光合产物输出受阻;而长期受臭氧污染后,小麦叶片的光合速率、光化学效率、叶绿素含量和蔗糖含量均显著降低,并与臭氧剂量的大小和峰值出现的早晚有关。O3 浓度升高将抑制光合作用,减少气孔导度,加强呼吸作用,改变C 同化物分配,加快叶片的衰老。众多研究表明,O3 导致的光合能力下降主要是由Rubisco 最大羧化效率降低导致;而O3 对光合器官捕获光的能力及光合电子传递速率的影响是光合作用下降的另一个原因。 尽管已有不少关于不同物种间对O3 敏感性的种间差异研究,然而育种方法或育种地点对中国不同冬小麦品种的O3 敏感性的影响尚不清楚。因此,我们假设育种年代、育种方法及地点将交互影响冬小麦品种对O3 的生长及生理响应。为进一步明确基因对冬小麦O3 敏感性的控制,研究了普通六倍体冬小麦的近缘体对O3 敏感性的差异。CO2 浓度升高及干旱胁迫对小麦臭氧敏感性的影响也进行了研究。论文主要从生理生化、生长及产量水平上来阐释O3 浓度升高、CO3加倍、干旱对冬小麦生长及生产影响的机理。 本研究主要是在温室中的上部开口的生长箱(open-top chamber, OTC)中进行。先后开展了四个盆栽实验研究,主要目的是确定中国不同基因型冬小麦种或品种对臭氧的敏感性及其反应机理;确定CO2 浓度升高及干旱在减轻O3 伤害方面的作用及其机理。实验材料为中国不同年代选育出的小麦品种,即1745年至2004 年间选育出的20 个品种和7 个小麦材料。主要评价指标包括相对生长速率、异速生长系数、叶绿素荧光、抗氧化活性、可溶性蛋白质含量、膜酯过氧化、气体交换、光合能力、叶绿素含量、暗呼吸、生物量及籽粒产量。实验研究得到的主要结果如下: 1) O3 升高显著降低整株及地上和地下部分的相对生长速率,显著降低异速生长系数、可变荧光、最大光化学效率、量子产额、光化学淬灭系数以及电子传递速率,但提高了非光化学淬灭系数。冬小麦不同品种对O3 的敏感性随育种年代的增加而增大,并与对照植株相对生长速率呈正相关。尽管近年来环境中的O3 浓度比过去显著增加,但新近育出的品种对臭氧的抗性却没有表现出协同进化效应。通过杂交选育的品种对臭氧的敏感性大于通过引进的和重选的品种。从生长和光合生理上来看,不同小麦品种对臭氧的敏感性与育种地点没有相关性,表明冬小麦品种对臭氧的适应能力与其生长环境下的臭氧浓度无关。因此,对臭氧相对敏感的冬小麦品种主要是由培育中较高相对生长速率或较高光合能力的杂交育种方式决定的,而与选育地点环境中的臭氧浓度无关。 2) 臭氧显著降低叶片中抗坏血酸(AsA)和可溶性蛋白的含量,但提高了过氧化物酶(POD)的活性和膜酯过氧化物(MDA)的含量。臭氧浓度升高抑制饱和光强下的净光合速率(Asat),降低气孔导度(gs)和总叶绿素含量,而显著提高暗呼吸速率(Rd)和胞间CO2 浓度(Ci)。臭氧导致总生物量降低,但地下部生物量受到的影响大于地上部。不同基因型小麦对臭氧的潜在敏感性与实际观察到的抗臭氧能力存在很大差异。冬小麦品种对臭氧的敏感性与臭氧环境下植株气孔导度和暗呼吸速率相关。臭氧导致Ci 浓度升高以及膜酯过氧化,由此得出臭氧导致的净光合速率主要是由于臭氧降低了叶肉细胞活性及细胞膜的完整性。新品种对臭氧相对敏感,主要是由于其具有较高的气孔导度抗氧化能力下降幅度较大以及较低的暗呼吸速率,从而对蛋白和细胞膜完整性造成较高的氧化伤害。 3) 臭氧对冬小麦光合和生长的影响存在着显著的种间差异。原初栽培种表现出最大的抗性,当代品种次之,而野生种对臭氧最为敏感。在普通冬小麦不同基因组供体中,钩刺山羊草(Aegilops tauschii,DD)对臭氧最敏感,其次为栽培一粒小麦(T. monococcum,AA),而圆锥小麦(Triticum turgidum ssp.Durum,AABB)对臭氧的抗性最大。因此,当代冬小麦品种对臭氧的敏感性可能是与其D 染色体供体-钩刺山羊草对臭氧敏感有关,而与其A、B 染色体供体-圆锥小麦的关系相对较小。 4) CO2 浓度升高提高了老品种和新品种的Asat,最大羧化速率(Vcmax),最大电子传递速率(Jmax)、光和CO2 饱和光合速率(Amax)。与之相反,臭氧显著降低了这些生理参数。虽然两品种对CO2 的响应没有显著性差异,但CO2浓度升高均有效保护了臭氧对它们的伤害。这种效应与CO2 浓度升高引起的气孔导度降低无关,而与代谢活性的提高有关。 5) 水分胁迫和臭氧分别都显著降低了 Asat 和gs。干旱显著降低Vcmax 和羧化效率(CE),而对Jmax 和暗呼吸(R)的影响不显著。臭氧显著降低冬小麦不同基因型的Vcmax,Jmax,R 和CE。二者均降低了生物量的积累及最终籽粒产量。与六倍体小麦相比,四倍体小麦对干旱相对敏感,但对臭氧却表现出较高抗性。干旱降低了气孔导度从而显著减少了植株对臭氧的吸收量,但两基因型的反应截然不同。干旱使臭氧对六倍体小麦产量和收获指数的伤害分别减少了约16%和50%,而干旱对该四倍体小麦的保护效应不大。

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氮素是影响内蒙古温带典型草原植物生长和初级生产力的主要因素之一,土壤氮素的可利用性及其对全球环境变化的响应对于预测生态系统碳氮平衡显得尤为重要。空气中的游离氮和土壤中的有机氮必须通过固氮作用和矿化作用,转化为无机氮才能被绝大多数高等植物直接利用,氮素转化决定土壤氮素有效性。因此,研究环境变化对草原灌丛豆科固氮植物小叶锦鸡儿和草原优势植物种羊草土壤氮素转化重要生物过程的影响,对于进一步了解草原氮库变化及其对环境变化的可能响应有重要意义。 在中国科学院内蒙古草原生态系统定位站,利用开顶式生长室(Open-top chamber,OTC)控制实验模拟环境变化,经过三年的实验处理,研究氮素、水分和CO2浓度变化对小叶锦鸡儿根瘤生长和共生固氮、小叶锦鸡儿和羊草土壤净氮矿化速率的影响。观察小叶锦鸡儿根瘤形态和数量、测定根瘤长度和生物量以及固氮酶活性、测定土壤净氮矿化速率和土壤酶活性,探讨小叶锦鸡儿和羊草土壤氮素转化对环境变化响应机理。 结果表明,三年生桶培小叶锦鸡儿根瘤多着生于侧根,以浅黄色的小型球状根瘤为主,其次是棕褐色的棒状和纺锤状根瘤,较大型的褐色Y状根瘤相对较少。添加氮素极显著地抑制根瘤生长发育及其固氮酶活性,这种抑制效应随着水分增加和CO2浓度升高有所减缓。随着水分的增加,根瘤形态多样,根瘤着生部位由主根渐向侧根再向须根发展,根瘤数量和重量也显著增加。水分和CO2浓度升高,固氮酶活性增加但是未达到显著水平。小叶锦鸡儿根瘤生长及其固氮酶活性在加水条件下最好,水分可能是限制内蒙古半干旱草原小叶锦鸡儿固氮能力的关键因素。 环境变化影响小叶锦鸡儿土壤无机氮库。添加氮素处理,土壤无机氮库显著增加。添加氮素后,土壤脲酶活性显著降低,铵态氮和无机氮都出现明显的氮固持,但硝化速率增加,可能是由于添加氮素后土壤化学性质改变更利于硝化细菌进行硝化活动。随着水分和CO2浓度的升高,由于植物生长需求更多氮素的供应,土壤无机氮库显著降低。水分和CO2浓度处理对小叶锦鸡儿土壤脲酶活性和净氮矿化速率没有显著影响,但是能一定程度上减缓了氮素的负效应,促使无机氮的转化,使土壤微生物对铵态氮和无机氮的固持减少。但是蛋白酶活性和硝酸还原酶活性对三种环境因子响应均不敏感,脲酶对环境因子的变化最为敏感。小叶锦鸡儿土壤氮素转化与土壤理化性质密切相关,环境因子通过影响土壤脲酶活性以及土壤酸碱度等影响土壤矿化速率,进而影响土壤无机氮浓度和植物可利用氮。 羊草土壤无机氮库与小叶锦鸡儿土壤无机氮库对环境变化的响应较为一致,添加氮素羊草土壤无机氮含量显著增加,水分增加土壤无机氮含量显著降低。添加氮素使硝化速率显著增大,氨化速率和净氮矿化速率降低,但是未达到显著水平,铵态氮和无机氮出现固持现象。水分的增加降低土壤无机氮库,刺激脲酶活性,微生物对铵态氮的矿化作用增加,但是硝态氮的矿化作用受抑制,对净氮矿化没有影响。CO2浓度升高对羊草土壤无机氮库和土壤氮素矿化都没有显著地影响,但是CO2浓度升高在适宜水分下通过刺激土壤微生物活性,促进脲酶活性和无机氮的转化。羊草土壤酶活性对氮素和CO2浓度的响应与小叶锦鸡儿土壤酶活性的响应一致。 综上,不同环境因子对氮素转化过程影响不同,氮素添加抑制小叶锦鸡儿根瘤及其固氮酶活性,降低小叶锦鸡儿和羊草土壤净氮矿化速率。水分和CO2浓度升高一定程度上缓解了氮素对固氮酶活性以及土壤净氮素矿化速率的抑制作用,有利于土壤氮素转化。

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以小麦品种‘小偃6号’(氮高效品种)和‘长旱58’(氮低效品种)为材料,采用开顶式气室和土培实验研究了大气NH3浓度升高对生长于高、低两种供氮介质下小麦植株不同生育期叶片净光合速率(Pn)、气孔导度(Gs)、叶绿素含量、叶绿素荧光参数(Fv/Fm、Fv/F0)和可溶性糖含量的影响。结果显示:两小麦品种高氨低氮处理植株的Pn、Fv/F0和可溶性糖含量均高于高氨高氮和低氨低氮处理,并在生育后期差异达显著水平(P<0.05),氮低效品种的Gs也符合上述规律且不同处理间差异显著(P<0.05);小麦各生育期高氨高氮处理下植株的Pn均显著低于低氨高氮处理,且两处理间灌浆期的叶绿素含量和灌浆期以前的可溶性糖含量的差异显著(P<0.05),而两处理灌浆期以前的叶绿素荧光参数Fv/Fm在各处理条件下均无显著差异;不同处理间及品种间各项光合特征指标差异缺乏规律性。可见,大气中NH3浓度升高有利于改善低供氮介质条件下小麦植株的氮营养状况,但不同氮效率品种间的响应存在差异。

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  由大气CO2浓度升高导致的气候变化是全球变化的重要研究内容之一。大气 CO2浓度升高会对植物的生理活动产生深刻的影响。本论文以开顶箱(Open top chamber)法控制 CO2浓度,在长期野外实地模拟基础上,研究三个树种资源分配模式的变化,揭示了长白山地区三个主要树种—红松(Pinus koraiensis)、长白松(Pinus sylvestriformis)和蒙古栎(Quercus mongolica)叶含碳结构物质和次生代谢物(CBSSCs)含量的变化动态及植物各器官内碳-防卫物质分配模式对CO2浓度升高的响应,这对预测未来CO2浓度升高条件下树木的适应性提供了科学依据。研究结果如下: 1)红松和长白松针叶总非结构性碳水化合物含量在生长季呈现先升高后降低的变化趋势,生长季末期稍有升高,休眠季含量较稳定。脂肪和结构性物质如半纤维素、纤维素和木质素含量在生长季和休眠季中含量比较稳定。 2)CBSSCs在植物叶中的含量存在显著的种间差异性,CBSSCs含量在生长季变化较大,休眠季变化很小。 3)从三个树种叶CBSSCs浓度的年平均值来看,植物对高浓度CO2没有持续和明显的反应,叶内不会出现较高浓度的酚类物质和其它CBSSCs物质。 4)高浓度CO2对植株氮总量没有影响,但由于生长导致的稀释效应使得红松叶、茎全氮浓度显著降低。 5)长期高浓度CO2处理使得红松生长和光合能力都有提高,碳向酚类物质和结构物质的分配提高。由高浓度CO2诱导的植物的这种碳向防卫物质的分配格局符合生长分化平衡模型(GDBe)的预测结果。

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探讨全球气候变化的生物学和生态学效应是当今生态学中的热点,研究大气CO2浓度升高对植物-昆虫相互作用关系的影响具有重要的理论和实践意义。本文使用开顶式气室(Open-top chamber,OTC)在野外条件下研究了CO2浓度升高对三种树木(小青杨、白桦和蒙古栎)叶片化学成分含量的影响,以及树木叶片品质变化对一种广食性森林昆虫(舞毒蛾)幼虫取食、生长发育和取食偏嗜性的影响。得出如下结果:(1)CO2浓度升高对3个受试树种叶片中的营养成分及次生代谢物含量均有显著影响,总体表现为氮含量降低,而碳氮比、非结构性碳水化合物、总酚和缩合丹宁含量增加。叶片中的化学成分含量可随时间发生显著变化,不同树种、甚至同一树种不同冠层高度的叶片对CO2浓度升高的响应强度也是不同的。叶片的干物质含量和比叶重对CO2浓度升高的响应不显著。(2)室内非选择性取食实验、室内选择性取食实验以及上树取食饲养方式下的多龄期取食实验,均发现高浓度CO2处理组内舞毒蛾幼虫的生长发育受到显著抑制。但对四龄舞毒蛾幼虫所进行的短期生物测定并未发现不同CO2浓度处理下幼虫的生长发育速率、对食物的取食率和转化率等昆虫营养指标存在显著差异。(3)叶片品质的降低是导致舞毒蛾幼虫生长发育受抑制的主要原因。但是总体上,CO2浓度升高导致的叶片品质变化并未显著影响幼虫的取食率和取食量。(4)舞毒蛾幼虫对不同叶片种类表现出清晰的取食选择性,这种选择性在其幼龄期就可表现出来。幼虫对小青杨上层叶片有最显著的偏嗜性,对蒙古栎下层叶片有最明显的拒食性。但是CO2浓度升高导致的叶片品质变化对舞毒蛾幼虫的取食选择性和寄主偏嗜行为并未产生显著影响。(5)检测出高浓度CO2处理组内舞毒蛾幼虫虫粪中含有浓度更高的植物次生代谢物质(总酚和缩合单宁),这很可能是昆虫整体生长发育受抑制的重要原因之一。

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界面是不同物相之间物质交换和能量流动最活跃的区域,植物通过植物体与环境之间的界面进行生命活动,其中以植物基本代谢物质COZ为媒介的界面过程研究是界面生态学研究的核心部分。本论文以开顶箱(Open toP chamber)法控制CO2浓度,在长期野外实地模拟基础上,研究针叶/大气界面和土壤/大气界面过程,揭示了红松(Pinus koraiensis)和长白松(Pinussylveslriformis)在高浓度CO2下生理生态功能的动态变化,这对预测未来COZ浓度倍增条件下树木的适应性提供了科学依据。研究结果表明:①长期700和500μmolmol-1 CO2处理,红松和长白松发生光合适应现象,但净光合速率仍比空气条件下对照组植株的净光合速率高;②高浓度CO2没有改变两树种的气孔敏感性,Ci/Ca比值增加,气孔响应与光合适应不同步;③红松和长白松的净光合速率与RuBPcase活性、光响应参数、针叶淀粉和全氮含量、相对生长速率具有明显相关性;④红松和长白松的暗呼吸对高浓度CO2的响应是瞬间反应与长期适应性的结合;⑤高浓度CO2提高了两树种的光合水分利用效率;⑥红松和长白松地上、地下部分的生物量分配模式在高浓度CO2下改变;⑦高浓度CO2改变了两树种单位叶面积重量、根体积、主根长、分枝等形态结构方面的特征,叶重比和根重比随CO2处理时间而变化;⑧施放高浓度CO2开顶箱内的土壤温度、土壤有机碳和全氮含量升高,土壤/大气间的CO2交换受到抑制;⑨红松和长白松对高浓度CO2的响应有很多不同之处,开顶箱本身的环境对长白松的生长有一定影响,对红松的影响相对较小;⑩红松和长白松对700和500μmolmol-1 CO2的生理生态响应随植物体的生长和CO2处理时间是动态变化的。

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由于人类活动所引起的地球大气层中温室气体的富集已导致全球地表平均温度在20世纪升高了0.6 ℃,并预测在本世纪将上升1.4-5.8 ℃。气候变暖对陆地植物和生态系统影响深远,并已成为全球变化研究的重要议题。高海拔、高纬度地带的生态系统对气候变化最敏感。而在高原和高山极端环境影响下所形成的高寒草甸生态系统极其脆弱,对由于温室效应引起的全球气候变化极其敏感,对这些变化的响应更具有超前性。 本研究以川西北高寒草甸植物群落及几种主要物种为研究对象,采用国际山地综合研究中心(ITEX)普遍所采用的增温方法-----开顶式生长室(OTC)模拟气候变暖来研究增温对高寒草甸植物群落结构、物质分配及其主要物种生长和生理的影响,以探讨高寒草甸植物响应与适应气候变暖的生物学和生态学机制。主要研究结论如下: 1、OTC的增温效果 由于地温、地表温度和气温的平均值在OTC内分别高出对照样地0.28℃、0.46℃和1.4℃,这说明本研究所采用的开顶式生长室(OTC)起到了增温的作用;同时,由于温室内与温室外接受的降水量相同,温室内由于热量条件的改善,土壤蒸发和植被的蒸腾作用增强,直接导致了OTC内土壤表层相对湿度的减少。 2、群落结构对增温的响应 由于增温时间较短,增温内外样地的物种组成并未发生改变;但增温后一定程度上改变了植物群落的小气候环境,从而导致物种间的竞争关系被破坏,种间竞争关系的破坏引起群落优势种组成发生相应的改变,在对照样地,鹅绒委陵菜、甘青老鹳草、遏蓝菜和蚤缀是占绝对优势的物种,而在OTC内,小米草、尼泊尔酸模、垂穗披碱草、发草和羊茅的重要性显著增加。 禾草和杂草由于对增温的生物学特性及其资源利用响应的不同,加之增温造成土壤含水量下降等环境因子的改变。与对照样地相比较,OTC内禾草的盖度及生物量都显著增加,而杂草的盖度和生物量则显著下降。 3、植物生长期对增温的响应 OTC内立枯和调落物的生物量在生长季末(10月份)都要小于对照样地的立枯和调落物生物量,而OTC内的地上鲜体生物量在10月份却略高于对照样地。这说明OTC内植物的衰老或死亡得以延缓,而植物的生长期得以延长。 4、群落生物量及分配对增温的响应 OTC内的地上鲜体生物量(10月份除外)和地下0-30cm的根系生物量与对照样地相比较,都出现了不同程度的减少;土壤根系的分配格局也发生了明显的改变,其中,OTC内0-10cm土层的生物量分配比例增加,而20-30cm土层生物量分配比例的减少。 5、群落碳、氮对增温的响应 增温后,OTC内植物群落地上活体和地下活根的碳浓度不同程度的高于对照样地,植物群落的碳库在OTC内也略高于对照样地;而OTC内植物群落地上活体和地下活根的氮浓度不同程度的低于对照样地,其植物群落的氮库与对照样地相比也略有下降。 6、几种主要植物的生长及物质分配对增温的响应 垂穗披碱草在增温后株高、比叶面积和地上生物量均显著地增加;尼泊尔酸模在增温后比叶面积和单株平均生物量积累显著地增加,而各组分中,增温处理使叶的生物量显著增加,而根的生物量却显著下降;鹅绒委陵菜在增温后株高、比叶面积和单株平均生物量积累显著地减少,而各组分中,增温处理使叶和茎的生物量显著减少,根的生物量却显著地增加。 尼泊尔酸模的LMR、RMR、R/S、根部碳含量、碳和氮在叶片与根部的分配比例在增温后显著地增加,而SMR、根部氮含量、碳和氮在茎部的分配比例在增温后却显著地降低;鹅绒委陵菜的RMR、R/S、碳和氮在根部的分配比例在增温后显著地增加,而SMR、LMR、碳在叶片的分配比例在增温后却显著地降低 7、几种主要植物的光合生理过程对增温的响应 增温使垂穗披碱草和尼泊尔酸模叶片中的叶绿素a、叶绿素b、总叶绿素含量显著增加;而鹅绒委陵菜叶片的叶绿素a、叶绿素b、总叶绿素含量在增温后显著减少,类胡萝卜素含量在增温后却显著增加。 增温对3种植物的气体交换产生了显著影响。其中,垂穗披碱草和尼泊尔酸模叶片的光响应曲线在增温后明显高于对照处理,A、E、gs、Pmax、、Rday、AQY和LSP显著增加,而LCP则显著降低;鹅绒委陵菜的光响应曲线在增温后则明显的低于对照处理,A、E、gs、Pmax、、Rday、AQY和LSP显著减少,而LCP则显著增加。 增温后垂穗披碱草和尼泊尔酸模叶片的Fv/Fm、Yield和qP显著增加;而鹅绒委陵菜叶片的Fv/Fm、Yield和qP则显著减少,qN却显著地增加。 8、几种主要植物的抗氧化酶系统对增温的响应 增温使垂穗披碱草和尼泊尔酸模体内抗氧化酶活性和非酶促作用有所提高,植物膜脂过氧化作用降低;鹅绒委陵菜叶片中酶促反应和非酶促反应在增温后也显著提高,但可能由于增温后的土壤干旱超过了鹅绒委陵菜叶的抗氧化保护能力,抗氧化酶活性及非酶促反应(脯氨酸、类胡萝卜素)的提高不足以完全清除干旱诱导形成的过量活性氧,因此叶片的膜脂过氧化程度仍然显著提高。 Enrichment of atmospheric greenhouse gases resulted from human activities such as fossil fuel burning and deforestation has increased global mean temperature by 0.6 ℃ in the 20th century and is predicted to increase in this century by 1.4-5.8 ℃. The global warming will have profound, long-term impacts on terrestrial plants and ecosystems. The ecoologcial consequences arising from global warming have also become the very important issuses of global change research. The terrestrial habitats of high-elevation and high-latitude ecosystems are regarded as the most sensitive to changing climate. The alpine meadow ecosystme, which resulted from the composite effects of mountain extreme climatic factors in Tibetan Plateau, is thus thought to be especially vulnerable and sensitive to global warming. In this paper, the response of plant community and several main species in the alpine meadow of Northewst Sichuan to experimemtal warming was studied by using open-top chambers (OTC). The aim of the this study was to research the warming effects on plant community structure, substance allocation, growth and physiological processes of several mian species, and to explore the biological and ecological mechanism of how the alpine meadow plants acclimate and adapt to future global warming. The results were as follows: 1. Warming effects of OTC The mean soil temperature, soil surface temperature and air temperature in OTC manipulation increased by 0.28℃、0.46℃ and 1.4℃ compared to the control during the growing season. This suggested that the OTC used in our study had increased temperature there. Meanwhile, the OTC manipulation slightly altered thermal conditions, but the same amount of precipitation was supplied to both the OTC manipulation and the control, so higher soil evaporation and plant transpiration in OTC manipulation directly lead to the decrease of soil surface water content. 2. The reponse of community structure to experimental warming The species richness was not changed by the short-term effect of OTC manipulation. However, experimental warming changed the microenvironment of plant community, therefore competitive balances among species were shift, leading to changes in species dominance. In the present study, the dominant plant species in the control plots were some forbs including Potentilla anserine, Geranium pylzowianum, Thlaspi arvense and Arenaria serpyllifolia, however, the importance value of some gramineous grasses including Elymus nutans, Deschampsia caespitosa, Festuca ovina, and some forbs including Euphrasia tatarica and Rumex acetosa significantly increased in OTC. The different biology characteristics and resource utilizations between gramineous grasses and forbs, and enhanced temperature caused change in some environment factors such as soil water content. As a result, the coverage and biomass of gramineous grasses significantly increased in OTC compared to the control, however, the coverage and biomass of forbs singnifciantly decreased in OTC compared to the control. 3. The reponse of plant growing season to experimental warming Both the standing dead and fallen litter biomass in OTC were lower than those in the control in October, and the biomass of aboveground live-vegetation in OTC was higher than that of the control. The results indicated that the senescence of plants was postponed, and the growing season was prolonged in our research. 4. The reponse of community biomass accumulation and its allocation to experimental warming Experimental warming caused the decrease of aboveground live biomass and belowground root biomass except for the aboveground live biomass in October. Experimental warming also had pronounced effects on the pattern of root biomass allocation. In the present study, the root biomass in 0-10cm soil layer increased in OTC manipulation compared to the control, however, the root biomass in the 20-30cm soil layer decreased in OTC manipulation compared to the control. 5. The reponse of community C and N content to experimental warming The C concentration and stock in aboveground live and belowground root both increased in OTC manipulation compared to the control. However, the N concentration and stock in aboveground live and belowground root both decreased in OTC manipulation compared to the control. 6. The reponse of gowth and biomass, C and N alloction of several species to experimental warming Experimental warming significantly increased the height, SLA (specific leaf area) and aboveground biomass of Elymus nutans in OTC manipulation compared to the control. The SLA and total biomass of Rumex acetosa also significantly increased in OTC manipulation compared to control, among the different components of Rumex acetosa, leaf biomass significantly increased, but root biomass significantly decreased in OTC manipulation compared to the control. However, the height, SLA and total biomass of Potentilla anserina significantly decreased in OTC manipulation compared to the control, among the different component of Potentilla anserina, leaf and stem biomass significantly decreased, but root biomass significantly increased in OTC manipulation compared to the control. The LMR (leaf mass ratio), RMR (root mass ratio), R/S (shoot/root biomass ration) and root C concentration of Rumex acetosa significantly increased in OTC manipulation compared to outside control, also, Rumex acetosa allocated relatively more C and N content to leaf and root in response to experimental warming, however, the SMR (stem mass ration) and root N concentration of Rumex acetosa significantly decreased in OTC manipulation compared to outside control, also, Rumex acetosa allocated relatively less C and N content to stem in response to experimental warming. The RMR and R/S of Potentilla anserina significantly increased in OTC manipulation compared to outside control, also, Potentilla anserina allocated relatively more C and N content to root in response to experimental warming, however, the SMR and LMR of Potentilla anserina significantly decreased in OTC manipulation compared to outside control, also, Potentilla anserina allocated relatively less C and N content to leaf in response to experimental warming. 7. The reponse of physiological processes of several species to experimental warming Experimental warming significantly increased chlorophyll a, chlorophyll b and total chlorophyll of Elymus nutans and Rumex acetosa in OTC manipulation compared to outside control. However, chlorophyll a, chlorophyll b, total chlorophyll and carotenoid of Potentilla anserina in OTC manipulation significantly decreased compared to outside control. Experimental warming had pronounced effects on gas exchange of Elymus nutans, Rumex acetosa and Potentilla anserine. In the present study, warming markedly increased the light response curves of Elymus nutans and Rumex acetosa in OTC manipulation compared to outside control, and also singnificantly increased A (net photosynthesis rate), E (transpiration rate), gs (stomatal conductance), Pmax (maximum net photosynthetic rate), Rday (dark respiration rate), AQY (apparent quantum yield) and LSP (light saturation point), but LCP (photosynthetic light compensation) of Elymus nutans and Rumex acetosa in OTC manipulation singnificantly decreased compared to outside control. However, warming markedly decreased the light response curves of Potentilla anserina in OTC manipulation compared to outside control, and also singnificantly decreased A, E, gs, Pmax, Rday, AQY and LSP, but LCP of Potentilla anserina in OTC manipulation singnificantly increased compared to outside control. Experimental warming singnificantly increased the chlorophyll fluorescence kinetics parameters such as Fv/Fm, Yield and qP of Elymus nutans and Rumex acetosa and qN of Potentilla anserina in OTC manipulation, but Fv/Fm, Yield and qP of Potentilla anserina in OTC manipulation singnificantly decreased. 8. The reponse of antioxidative systems of several species to experimental warming Experimental warming tended to increase the activities of antioxidative enzymes and stimulate the role of non-enzymes of Elymus nutans and Rumex acetosa. As a result, MDA content of Elymus nutans and Rumex acetosa decreased. The activities of antioxidative enzymes and non-enzymes of Potentilla anserina also significantly increased in OTC manipulation, but more O2- was produced because of lower soil water content, and the O2- accumulation exceeded the defense ability of antioxidative systems and non-enzymes fuctions. As a result, MDA content of Potentilla anserine still increased in OTC manipulation compared to outside control.

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Open-top chambers were used to estimate the possible effects of global warming on delta C-13 of seven plant species grown in alpine meadow ecosystem. The delta C-13 values of plant species were lower after long-term growth in open-top chambers. In the course of experiment, temperature significantly increased inside the chambers by 4 degrees C. Plant species grown at a lower elevation above sea level had higher delta C-13 values as compared to those grown at a higher elevation. This was in accordance with the effect of open-top chamber on delta C-13 values in plants. Greater availability of CO2 and lower water vapor as indicated by an increase in discrimination against (CO2)-C-13, probably result in more negative delta C-13 values of plants because higher stomatal conductance increases availability of CO2 and causes greater discrimination against (CO2)-C-13. The plant species studied could be the indicator species for testing global warming by the change in carbon isotope ratios at the two growth temperatures.

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Following the quantitative determination of dust cloud parameters, this study investigates the flame propagation through cornstarch dust clouds in a vertical duct of 780 mm height and 160 x 160 mm square cross section, and gives particular attention to the effect of small scale turbulence and small turbulence intensity on flame characteristics. Dust suspensions in air were produced using an improved apparatus ensuring more uniform distribution and repeatable dust concentrations in the testing duct. The dispersion-induced turbulence was measured by means of a particle image velocimetry (PIV) system, and dust concentrations were estimated by direct weighing method. This quantitative assessment made it possible to correlate observed flame behaviors with the parameters of the dust cloud. Upward propagating dust flames, from both closed/open bottom end to open/closed top end of the duct, were visualized by direct light and shadow photography. From the observation of propagation regimes and the measurements of flame velocity, a critical value of the turbulence intensity can be specified below which laminar flame propagation would be established. This transition condition was determined to be 10 cm/s. Laminar flames propagated with oscillations from the closed bottom end to the open top end of the testing duct, while the turbulent flames accelerated continuously. Both laminar and turbulent flames propagated with steady velocity from the open bottom end to the closed top end of the duct. The measured propagation velocity of laminar flames appeared to be in the range of 0.45-0.56 m/s, and it was consistent with the measurements reported in the literature. In the present experimental study, the influence of dust concentration on flame propagation was also examined, and the flame propagation velocity was found weakly sensitive to the variations in dust concentration. Some information on the flame structure was revealed from the shadow records, showing the typical heterogeneous feature of the dust combustion process.

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基于长期观测资料,众多大气环流模型预测在二十一世纪末大气中二氧化碳浓度将达到700μmolmol'I,地球表面年平均温度也将升高1.5-4.OoC。水稻是亚洲的主要粮食作物,为世界近三分之一的人口提供食物能源。这项工作的目的,是利用人工模拟环境,预测在未来全球气候变化,二氧化碳及温度升高的条件下,水稻的光合生理反应及随之而来的对其产量的影响。本研究是美国环境署( EPA)与国际水稻研究所(IRRI)合作研究项目“Effects of UV-B and Global Climate Change on Rice”的一部分. 在这项研究中,采用了特殊设计并直接建立在水稻田间的开顶式气室(open-top chambers)。在此之前还没有这样大规模的在水稻主产区的此类模拟研究,水稻在气室中渡过了从萌发到收获的整个生长过程。模拟环境条件有三个浓度的二氧化碳(包括现有大气浓度,在此基础上升高200及300 μmolmol-l)和两个温度(即:现有大气温度及升高4度)共六个处理。供试水稻品种四个:IR72,IR65598-112-2,IR65600-42-5-2-BSI-313和N22。在实验中我们发现,水稻品种(如:1R72)单叶光合速率(以二氧化碳气体交换速率计)受二氧化碳浓度促进,在水稻营养生长期,二氧化碳及温度对其光合有协同促进作用.然而,随着花期的到来,在高温条件下,叶片光合能力(photosynthetic capacity)下降,出现光合适应现象(Photosynthetic acclirnation).水稻群体光合作用同样受到二氧化碳浓度促进,但在后期(Grain fill stage)这种促进作用消失;在高浓度二氧化碳下生长的大多数水稻品种的叶片中有较多的碳水化和物(可溶性糖和淀粉)积累.耐高温品种N22叶片中淀粉积累较少:叶片中氮素含量降低,同时发现Rubisco总活性相应降低,这与NCi曲线所示光合效率降低相吻合;通过叶片叶绿素荧光动力学测定,没有发现光系统光能转化效率的变化;水稻籽粒产量随二氧化碳浓度升高而增加,但温度升高使产量降低12.8-36.8%;不同品种对二氧化碳浓度的反应没有显著差别;在高温条件下,耐高温品生长在高二氧化碳浓度下表现良好。 本文系统地研究了水稻光合作用在二氧化碳及温度条件影响下,对二氧化碳浓度及光强变化的反应曲线,初次对水稻单叶与群体光合对二氧化碳浓度变化的反应做了实验性对比;讨论了温度升高对水稻在高浓度二氧化碳下发生光合适应的影响,对光合适应现象的可能机制做了探讨,并提出对未来大气二氧化碳浓度及温度升高条件下水稻适应品种筛选的可能方向。

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以长白山原始阔叶红松林和连续多个生长季500ppmCO2处理的红松幼苗为研究对象,采用TECO模型及参数的优化,结合长白山阔叶红松林生态系统的碳通量多年连续监测数据、开顶箱系统(Open-Top-Chambers,高浓度CO2处理)的实地连续监测数据以及相关研究结论的比较,定量模拟生态系统群落水平和个体水平的碳收支(碳通量和碳密度)、碳分配格局和蒸发散等年际变化。模拟结果显示: 1)生态系统群落水平的碳通量和碳密度模拟结果与通量塔监测数据对比发现:长白山阔叶红松林生态系统目前仍是个大气的碳 “汇”。碳汇强度的季节变化波动较大。土壤碳密度占整个阔叶红松林生态系统总密度的67.9%。 2) 开顶箱的个体水平的模型模拟与实地观测显示:CO2升高显著提高红松幼苗的总初级生产力和净初级生产力;地上生物量受到抑制,地下生物量显著增加。 3) CO2对红松幼苗蒸发量和蒸腾量的影响要高于生态系统,CO2提高红松幼苗蒸发量,但对幼苗的蒸腾量影响不大。

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随着工业化的发展,大气中二氧化碳的浓度(CO2)预测从现在的平均350μmol·mol-1升高到2030年的570μmol·mol-1,其增温作用将持续多个世纪。植被在大气二氧化碳减排以及调控区域水热状况过程中起重要作用,而其机理过程目前十分不清楚。本实验应用自控、封闭、独立生长室,研究了CO2浓度和温度升高对红桦根、茎、叶和枝可溶性蛋白含量和分配的影响,从蛋白水平上来解释川西亚地区的建群种-红桦对CO2升高和温度升高及其交互作用的响应规律,为全球气候变暖川西亚高山的植被保护和恢复提供理论依据。研究结果表明: 1. CO2浓度升高增加了可溶性蛋白的总量,改变了可溶性蛋白分配模式,即,可溶性蛋白分配到根的比例增加,分配到茎、枝、叶的比例减少。可能意味:在CO2浓度升高条件下,红桦根系的生长和营养物质吸收功能将会增强。 2. CO2浓度升高增加了根和茎的清蛋白含量,降低了叶片的清蛋白含量,叶片的球蛋白含量、醇溶蛋白含量和谷蛋白含量均增加。表明CO2浓度升高增加了清蛋白在根中积累,球蛋白、醇溶蛋白和谷蛋白大量在叶片中积累;前人研究所指出的CO2浓度升高使植物叶片可溶性蛋白的含量降低可能仅仅是由于清蛋白含量的降低造成的。 3. 温度升高使红桦幼苗整株所含可溶性蛋白总量增加,但可溶性蛋白总量的分配因红桦幼苗器官的不同而异。温度升高下根、茎、叶和枝的分配量分别占总可溶性蛋白的27.74%、35.57%、23.00%、13.68%,即茎>根>叶>枝。对照的根茎叶枝的分配量分别占总可溶性蛋白的21.01%、41.41%、23.08%、14.50%,即茎>叶>根>枝。表明温度升高使可溶性蛋白分配到根的比例增加,有利于根的可溶性蛋白的积累,增强了根吸收水分和矿质营养的能力,从而有利于根系的生长。 4. 温度升高处理下清蛋白和球蛋白在根中含量升高,在茎、叶和枝中含量下降,但没有达到显著水平;醇溶蛋白在根和叶中含量显著增加;谷蛋白在茎中的含量显著降低。表明温度升高增加清蛋白和球蛋白在红桦幼苗根部的积累,也有利于根和叶醇溶蛋白的积累,但不利于谷蛋白在茎的积累;温度升高条件下叶片可溶性蛋白升高是醇溶蛋白在叶片中积累的结果。 5. CO2浓度和温度同时升高条件下红桦幼苗的可溶性蛋白总量增加很少,只有分配到茎的可溶性蛋白比例增加,并且对可溶性蛋白分配规律没有影响。CO2和温度同时升高下红桦幼苗枝的可溶性蛋白含量的降低是可溶性蛋白总量的降低而不是碳水化合物稀释的结果,并且CO2和温度同时升高对红桦幼苗的生长没有明显的促进作用。 6. CO2和温度同时升高处理对可溶性蛋白含量有显著影响。清蛋白含量在根、茎、叶和枝中均降低,球蛋白含量在根中显著降低,醇溶蛋白含量在根、茎、叶和枝中均降低,谷蛋白含量在根中显著降低。表明CO2浓度和温度同时升高对根的影响显著,即降低了根的可溶性蛋白含量,可能导致根的吸收能力下降。 7. 因此,CO2和温度同时升高对可溶性蛋白影响不能简单地通过CO2和温度单因子影响机理来解释。 It is well known that atmospheric CO2 concentration and temperature are increasing as a consequence of human activities. Atmospheric CO2 concentration are predicted to increase from 350μmol·mol-1 now to 570μmol·mol-1 2030. And temperature will continue to increase for several centuries as a result of CO2 enrichment. Vegetation play a key role in reducing atmospheric CO2 and adapting and controlling warter and energy process in a certain region, while the underlying mechanism are not clear, yet. Betula albo-sinensis, as the dominating tree species of subalpine dark coniferous forest in west Sichuan province, play an important role in determing structure and function of forest ecosystem. In our study, effects of elevated atmospheric CO2 concentration (ambient±350±25μmol·mol-1), increased temperature (ambient±2.0±0.5℃) and their combination on contents and allocation of soluble protein were studied in independent and enclosed-top chamber system under high-frigid conditions. Chambers with ambient CO2 concentration and temperature are taken as control. The results are as the following, 1) Elevated atmospheric CO2 increased the accumulation of total weight of soluble protein in whole plant and changed allocation of soluble protein in red birch by increasing its allocation to roots and reducing its allocation to stem. This caused much more accumulation of soluble protein in roots which might help to prompt growth, development and nutrient absorption ability of roots. 2) Treatment EC increased content of albumin in roots and stems, reduced the content of albumin in leaves, and increased the content of globulin, promalin and glutenin in leaves. That is to say EC increased the accumulation of albumin in roots and accumulation of globulin, promalin and glutenin in leaves. The reduced soluble protein contents in plant leaves by EC, as reported by former researchers, are mainly resulted from the reduced content of albumin in leaves. 3) Elevated temperature increased the total of soluble proteins, but its allocation was dependent on organs. In treatment ET, roots, stems, leaves and branches take 27.74%, 35.57%, 23.00% and 13.68% of total weight of soluble protein. In treatment CK, roots, stems, leaves and branches take 21.01%, 41.41%, 23.08% and 14.50%. Elevated temperature changed allocation of soluble proteins in that it stimulated soluble proteins accumulation in roots and improved the uptake of water in roots. 4) Treatment ET increased the content of albumin and globulin in roots, and reduced the content of albumin and globulin in stems, leaves and branches. The content of promalin in roots and leaves was increased significantly, and the content of glutenin in stems was reduced significant. This suggested that ET stimulated the accumulation of albumin and globulin in roots and accumulation of promalin in leaves and roots; that treatment ET increased content of soluble protein in leaves was mainly resulted from the increased promalin content in leaves. 5) Regarding treatment ETC, the total of weight of soluble proteins increased, but not significantly; but increased in stems. So the combination of elevated atmospheric CO2 and temperature had not changed the allocation of soluble proteins in red birch seedling and reduced soluble proteins in branches were not the result of increased carbohydrate. 6) Treatment ETC reduced the content of albumin and promalin in roots, stems, leaves and branches, reduced the content of globulin and glutenin in roots significantly. That is to say elevated atmospheric CO2 and temperature reduced the content of soluble proteins in roots significantly which might help to prompt growth, development and nutrient absorption ability of roots. 7) The effects of elevated atmospheric CO2 and temperature on soluble protein cannot be simply interpreted through their mechanism that obtained when they were imposed on plant separately.

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土壤微生物(Soil microbes)是生态系统的重要组成部分,它参与土壤中复杂有机物质的分解和再合成,也参与C、N、S、P等的循环。土壤酶(Soil enzyme)是土壤中具有生物活性的蛋白质,它与微生物一起推动着土壤的生物化学过程,并在树木营养物质的转化中起着重要的作用。鉴于土壤微生物和土壤酶对环境变化的敏感性,它们在CO2浓度和温度升高时的反应将在很大程度上影响森林生态系统的结构和功能。因此,要全面评价大气CO2浓度和温度升高对整个生态系统的影响,有必要对CO2浓度和温度升高条件下的土壤微生物的反应进行深入的研究与探讨。本文应用自控、封闭、独立的生长室系统,研究了川西亚高山岷江冷杉(Abies faxoniana)根际、非根际土壤微生物数量,红桦(Betula albosinensis)根际微生物数量以及根际、非根际土壤酶活性对大气CO2浓度(环境CO2浓度+350±25μmol·mol-1,EC)和温度(环境温度+2.0±0.5℃,ET)升高及两者同时升高(ECT)的响应。结果表明: 1) EC和ET显著增加岷江冷杉根际微生物数量,但不同微生物种类对EC和ET的反应有所差异。6、8和10月,岷江冷杉根际微生物数量与对照(CK)相比,EC处理的根际细菌数量分别增加了35%、164%和312%,ET处理增加了30%、115%和209%;EC和ET处理对根际放线菌和根际真菌数量影响不显著。ECT处理的根际放线菌数量分别增加了49%、50%和96%,根际真菌数量增加了151%、57%和48%;而ECT对根际细菌数量影响不显著。EC、ET和ECT处理对岷江冷杉土壤微生物总数的根际效应明显,其R/S值分别为1.93、1.37和1.46(CK的R/S值为0.81)。 2) 红桦根际微生物数量对EC、ET和ECT的响应不同。生长季节(5~10月),高密度的红桦根际细菌数量与CK 相比,EC的根际细菌数量分别增加28%、33%、423%、65%、43%和79%,而低密度的红桦根际细菌数量增加不显著。ET能显著增加根际细菌数量(7~10月),其中高密度的根际细菌数量分别增加了377%、107%、35%、22%,而低密度的根际细菌数量分别增加了27%、27%、64%、48%;ECT对两个密度水平下根际细菌数量均未产生有显著的影响。高、低密度的红桦根际放线菌和根际真菌数量与 CK 相比,EC显著增加了低密度的红桦根际放线菌数量,而对高密度的根际放线菌数量无显著影响;ET和ECT对高低密度的红桦根际放线菌数量均未产生显著影响。EC和ET对高低密度的根际真菌数量也无显著影响,而ECT却显著增加了高低密度的根际真菌数量。 3) EC、ET和ECT处理的低密度红桦根际微生物(细菌、放线菌和真菌)数量没有显著高于或低于高密度根际微生物数量,表明短期内密度对红桦根际微生物数量不产生影响。 4) 不同种类的氧化还原酶对EC、ET和ECT的响应不同。5~10月,EC的红桦根际过氧化氢酶活性是CK 的1.44、1.06、1.11、1.10、1.12和1.24倍,差异显著(6月除外);ET和ECT处理根际过氧化氢酶活性无显著增加。EC的红桦根际多酚氧化酶活性比CK显著增加;ET的根际多酚氧化酶活性显著高于CK(8月除外)。ECT的根际多酚氧化酶活性高于CK,差异不显著。EC的根际脱氢酶活性分别增加了46%、40%、133%、48%、17%和26%,差异显著。5~7月,ET和ECT的根际脱氢酶活性高于CK的脱氢酶活性,而8~9月则相反,差异性均不显著。 5) EC、ET和ECT对不同种类的水解酶的影响不同。EC能显著增加红桦根际脲酶活性,5~10月分别增加了29%、42%,、70%、67%、59%和57%。ET和ECT 对根际脲酶活性未产生显著影响。EC显著提高根际转化酶活性,5、6和9月EC的根际转化酶活性分别比CK高51%、42%和40%。5和10月,ET的根际转化酶活性低于CK,而其余月份却高于CK,但均具有显著性差异。ECT的根际转化酶活性与CK的根际转化酶活性有显著性差异(9月除外),5、6和7月的根际转化酶活性分别提高了94%、198%和67%。 6) 与CK相比,EC、ET和ECT的非根际土壤微生物数量以及非根际土壤酶活性均无显著提高。EC、ET和ECT的过氧化氢酶、脲酶的根际效应明显,而多酚氧化酶和脱氢酶根际效应不明显。EC和ECT的转化酶根际效应明显,而ET的转化酶根际效应不明显。 It is well known that atmospheric CO2 concentration and temperature are increasing as a consequence of human activities. In past decades, considerable efforts had been put into investigating the effects of climate change on processes of forest ecological system. In general, studies had been mainly focused on the effects of elevated atmospheric CO2 on plant physiology and development, litter quality, and soil microorganisms. Studies showed that there was variation in the responses of root development and below-ground processes to climate between different plant communities. Since the concentration of CO2 in soil was much higher (10~50 times) than in the atmosphere, increasing levels of atmospheric CO2 may not directly in fluence below ground processes. Betula albosinensis and Abies faxoniana, as the dominated tree species of subalpine dark coniferous forest in the western Sichuan province, which play an important role in the structure and function of this kind of forest ecosystem. In our study, effects of elevated atmospheric CO2 concentration (350±25μmol·mol-1), increased temperature (2.0±0.5℃) and both of the two on the number of rhizospheric microbe and rhizospheric enzyme activity were studied by the independent and enclosed-top chamber’ system under high-frigid conditions. Responses of rhizospheric bacteria, actinomycetes and fungi number of Betula albosinensis and Abies faxoniana under different densities(high density with 84 stems·m-2, low density with 28 stems·m-2 ), and rhizospheric enzyme activity of Betula albo-sinensis to elevated CO2 concentration and increased temperature were analyzed and discussed. The results are as the following, 1) In comparion with the control, the numbers of rhizospheric bacteria of Abies faxoniana were increased by 35%, 164% and 312% significantly in June, August and October respectively of EC, and were increased by 30%, 115% and 209% respectively of ET.However the effect of EC and ET on rhizospheric actinomycetes and fungi was not significant. The number of rhizospheric actinomycetes of ECT were increased significantly by 49%, 50% and 96% respectively, and the increment of rhizospheric fungi were 151%, 57% and 48% respectively .The effect of ECT on rhizospheric bacteria was not significant. Rhizospheric effect of soil microbe for all treatments was significant, with the R/S of 1.93, 1.27 and 1.46 for EC, ET and ECT, respectively. 2) Treatment EC improved the number of rhizospheric bacteria of Betula albosinensis under high density significantly in comparison with the control, over the growing season, the greatest increment of rhizospheric bacteria was from July. However, EC had no effect on the number of rhizospheric bacteria under low density. Except May and June, treatment ET improved the number of rhizospheric signifcantly. The effect of treatment ECT on the number of rhizospheric bacteria under different densities was not significant. Of treatment EC, the number of rhizospheric actinomycetes of Betula albosinensis under low density were increased significantly, however, treatment EC did not stimulate the number of rhizospheric actinomycetes under high density. Simultaneously, treatment ET and ECT did not stimulate the number of rhizospheric actinomycetes. Finally, in treatment ECT, the number of rhizospheric fungi under high density were increased significantly, however treatment EC and ET did not stimulate the number of rhizospheric fungi under different densities. 3) Of treatment EC, ET and ECT, the number of rhizospheric microbe of Betula albosinensis under low density were not more or fewer than that of microbe under hign density along the growing season, which showed that plant density had no effect on the nmber of microbe. 4) From May to October, 2004,rhizospheric catalase activity of Betula albosinensis of treatment EC was 1.44, 1.06, 1.11, 1.10, 1.12 and 1.24 times as treatment CK respectively, and the difference was statistically significant(except June). Treatment ET and ECT did not increase rhizospheric catalase activity significantly. In treatment EC, the rhizospheric pohyphenol oxidase activity was higher than treatment CK significantly. The rhizospheric pohyphenol oxidase activity of treatment ET was higher than CK significantly (except August). The rhizospheric pohyphenol oxidase activity of treatment ECT was higher than CK, but the difference was not statistically significant. Over the growing period, the rhizospheric dehydrogenase activity were increased 46%, 40%, 133%, 48%, 17% and 26% respectively by treatment EC, and the difference was statistically significant. From May to July, the rhizospheric dehydrogenase activity in treatment ET and ECT was higher than CK, but from August to October, the rhizospheric dehydrogenase activity was lower than CK, the difference was not significant. 5) Treatment EC increased rhizospheric urease activity significantly, from May to October, rhizospheric urease activity were increased 29%, 42%, 70%, 67%, 59% and 57% respectively by EC. Treatment ET and ECT had no effect on rhizospheric urease activity. Treatment EC improved rhizospheric invertase activity significantly, in May, June and September, the rhizospheric invertase activity of treatment EC were increased 51%, 42% and 40% in comparison with the control. Except May and October, the rhizospheric invertase activity of treatment ET was markly higher than CK. The rhizospheric invertase activity of treatment ECT was significantly different from CK (except September), in May, June and July treatment ECT increased rhizospheric invertase activity by 94%, 198% and 67% respectively. 6) In comparison with the control, treatment EC, ET, and ECT had no effect on the number of non-rhizospheric microbe and non-rhizospheric enzyme activity. Rhizospheric effect of catalase and urease for all treatments was significant, but rhizospheric effect of pohyphenol oxidase and dehydrogenase was not significant. Rhizospheric effect of invertase of EC and ECT was significant, but rhizospheric effect of invertase of ET was not significant.

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由于人类活动所引起的地球大气层中温室气体的富集已导致全球地表平均温度在20 世纪升高了0.6 ¡æ,并预测在本世纪将上升1.4-5.8 ¡æ。气候变暖对陆地植物和生态系统产生深远影响,并已成为全球变化研究的重要议题。位于青藏高原东部的川西亚高山针叶林是研究气候变暖对陆地生态系统影响的重要森林类型。森林采伐迹地和人工云杉林下作为目前该区人工造林和森林更新的两种重要生境,二者截然不同的光环境对亚高山针叶林不同物种更新及森林动态有非常重要的影响。 本文以青藏高原东部亚高山针叶林几种主要森林树种为研究对象,采用开顶式增温法(OTCs)模拟气候变暖来研究增温对生长在两种不同光环境下(全光条件和林下低光环境)的几种幼苗早期生长和生理的影响,旨在从更新角度探讨亚高山针叶林生态系统不同树种对气候变暖在形态或生理上的响应差异,其研究结果可在一定程度上为预测气候变暖对亚高山针叶林物种组成和演替动态提供科学依据,同时也可为未来林业生产管理者提供科学指导。 1、与框外对照相比,OTCs 框内微环境发生了一些变化。OTCs 框内与框外对照气温年平均值分别为5.72 ¡æ和5.21 ¡æ,而地表温度年平均值分别为5.34 ¡æ和5.04 ¡æ,OTCs 使气温和地表年平均温度分别提高了0.51 ¡æ和0.34 ¡æ;OTCs框内空气湿度年平均值约高于框外对照,二者分别为90.4 %和85.3 %。 2、增温促进了三种幼苗生长和生物量的积累,但增温效果与幼苗种类及所处的光环境有关。无论在全光或林下低光条件下,增温条件下云杉幼苗株高、地径、分支数、总生物量及组分生物量(根、茎、叶重)都显著地增加;增温仅在全光条件下使红桦幼苗株高、地径、总生物量及组分生物量(根、茎、叶重)等参数显著地增加,而在林下低光条件下增温对幼苗生长和生物量积累的影响效果不明显;冷杉幼苗生长对增温的响应则与红桦幼苗相反,增温仅在林下低光条件下对冷杉幼苗生长和形态的影响才有明显的促进作用。 增温对三种幼苗的生物量分配模式产生了不同的影响,并且这种影响也与幼苗所处的光环境有关。无论在全光或林下低光环境下,增温都促使云杉幼苗将更多的生物量分配到植物地下部分,从而导致幼苗在增温条件下有更高的R/S 比;增温仅在林下低光条件下促使冷杉幼苗将更多的生物量投入到植物叶部,从而使幼苗R/S 比显著地降低;增温在全光条件下对红桦幼苗生物量分配的影响趋势与冷杉幼苗在低光条件下相似,即增温在全光条件下促使红桦幼苗分配更多的生物量到植物同化部分—叶部。 3、增温对亚高山针叶林生态系统中三种幼苗气体交换和生理表现的影响总体表现为正效应(Positive),即增温促进了几种幼苗的生理活动及其表现:(i)无论在全光或林下低光环境下,增温使三种幼苗的光合色素含量都有所增加;(ii)增温在一定程度上提高了三种使幼苗的PSII 光系统效率(Fv/Fm),从而使幼苗具有更强的光合电子传递活性;增温在一定程度使三种幼苗潜在的热耗散能力(NPQ)都有所增强,从而提高幼苗防御光氧化的能力;(iii)从研究结果来看,增温通过增加光合色素含量和表观量子效率等参数而促进幼苗的光合作用过程。总体来说增温对幼苗生理过程的影响效果与幼苗种类及所处的光环境有关,增温仅在全光条件下对红桦幼苗光合过程的影响才有明显的效果,而冷杉幼苗则相反,增温仅在低光条件下才对幼苗的生理过程有显著的影响。 4、增温对三种幼苗的抗氧化酶系统产生了一定的影响。从总体来说,增温使几种幼苗活性氧含量及膜脂过氧化作用降低,从而在一定程度上减轻了该区低温对植物生长的消极影响;增温倾向表明使三种幼苗体内抗氧化酶活性和非酶促作用有所提高,从而有利于维持活性氧代谢平衡。但增温影响效果与幼苗种类所处的光环境及抗氧化酶种类有关,增温对冷杉幼苗抗氧化酶活性的影响仅在林下低光环境下效果明显,而对红桦幼苗抗氧化酶活性的影响仅在全光条件下才有明显的效果。 总之,增温促进了亚高山针叶林生态系统中三种幼苗的生长和生理表现,但幼苗生长和生理对增温的响应随植物种类及所处的光环境不同而变化,这种响应差可能异赋予了不同植物种类在未来气候变暖背景下面对不同环境条件时具有不同的适应力和竞争优势,从而对亚高山针叶林生态系统物种组成和森林动态产生潜在的影响。 Enrichment of atmospheric greenhouse gases resulted from human activities suchas fossil fuel burning and deforestation has increased global mean temperature by 0.6¡æ in the 20th century and is predicted to increase it by 1.4-5.8 ¡æ. The globalwarming will have profound, long-term impacts on terrestrial plants and ecosystems.The ecoologcial consequences arising from global warming have also become thevery important issuses of global change research. The subalpine coniferous forests inthe eastern Qinghai-Tibet Plateau provide a natural laboratory for the studying theeffects of climate warming on terrestrial ecosystems. The light environment differssignificantly between clear-outs and spruce plantations, which is particularlyimportant for plant regeneration and forest dynamics in the subalpine coniferous forests. In this paper, the short-term effects of two levels of air temperature (ambient andwarmed) and light (full light and ca. 10% of full light regimes) on the early growthand physiology of Picea asperata, Abies faxoniana and Betula albo-sinensis seedlingswas determined using open-top chambers (OTCs). The aim of the present study wasto understand the differences between tree species in their responses to experimentalwarming from the perspective of regeneration. Our results could provide insights intothe effects of climate warming on community composition and regeneration behavior for the subalpine coniferous forest ecosystem processes, and provide scientificdirection for the production and management under future climate change. 1. The OTCs manipulation slightly altered thermal conditions during the growingseason compared with the outside chambers. The annual mean air temperature andsoil surface temperature was 5.72 and 5.34 ¡æ (within the chambers), and 5.21 and5.04 ¡æ (outside the chambers), respectively. The OTCs manipulation increased airtemperature and soil surface temperature by 0.51 and 0.34 ¡æ on average, respectively.Air relative humidity was slightly higher inside the OTCs compared with the controlplots, with 90.4 and 85.3 %, respectively. 2. Warming generally stimulated the growth and biomass accumulation of thethree tree species, but the effects of warming on growth and development variedbetween light conditions and species. Irrespective of light regimes, warmingsignificantly increased plant height, root collar diameter, total biomass, componentbiomass (stem, foliar and root biomass) and the number of branches in P. asperataseedlings; For A. faxoniana seedlings, significant effects of warming on all the tested parameters (plant height, root collar diameter, total biomass, and component biomass) were found only under low light conditions; In contrast, the growth responses of B.albo-sinensis seedlings to warming were found only under full light conditions. Warming had pronounced effects on the pattern of carbon allocation. Irrespectiveof light regimes, the P. asperata seedlings allocated relatively more biomass to rootsin responses to warming, which led to a higher R/S. Significant effects of warming onbiomass allocation were only found for the A. faxoniana seedlings grown under lowlight conditions, with significantly increased in leaf mass ratio (LMR) and decreasedin R/S in responses to warming manipulation. The carbon allocation responses of B.albo-sinensis seedling to warming under full light conditions were similar with theresponse of A. faxoniana seedlings grown under low light conditions. Warmingsignificantly decreased root mass ratio (RMR), and increased leaf mass ratio (LMR)and shoot/root biomass ratio (S/R) for the B. albo-sinensis seedlings grown under full light conditions. 3. Warming generally had a beneficial effect on physiological processes of dominant tree species in subalpine coniferous forest ecosystems: (i) Warming markedincreased the concentrations of photosynthetic pigments in both tree species, but theeffects of warming on photosynthetic pigments were greater under low lightconditions than under full light conditions for the two conifers; (ii) Warming tended toenhance the efficiency of PSII in terms of increase in Fv/Fm, which was related tohigher chloroplast electron transport activity; and enhance non-radiative energydissipation in terms of in increase in NPQ, which may reflect an increased capacity inpreventing photooxidation; (iii) Warming may enhance photosynthesis and advancephysiological activity in plants by increasing photosynthetic pigment concentration,the efficiency of PSII and apparent quantum yield (Φ) etc. From the results, theeffects of warming on seedlings’ physiological performance varied between lightenvironment and species. The effects of warming on photosynthesis performance of B.albo-sinesis seedlings were pronounced only under full light conditions, while thephysiological responses of A. faxoniana seedlings to warming were found only underthe 60-year plantation. These results provided further support for the observationsabove on growth responses of seedlings to warming. 4. Warming had marked effects on antioxidative systems of the three seedlings.Warming generally decreased H2O2 accumulation and the rate of O2- production, andalleviated degree of lipid peroxidation in terms of decreased MDA content, whichalleviated to some extent the negative effects of low temperature on the plant growthand development in this region; Warming tended to increase the activities ofantioxidative enzymes and stimulate the role of non-enzymatic AOS scavenging,which helped to create an balance in maintaining AOS metabolites for the threeseedlings. Nevertheless, the effects of warming on antioxidative defense systems werepronounced only under the 60-year plantation for the A. faxoniana seedlings. Incontrast, the marked effects of warming on antioxidative defense systems for the B.albo-sinesis seedlings were found only under the full light conditions. In sum, warming is considered to be generally positive in terms of growth andphysiological process. However, the responses of growth and physiology performanceto warming manipulation varied between species and light regimes. Competitive and adaptive relationships between tree species may be altered as a result of responsedifferences to warming manipulation, which is one mechanism by which globalwarming will alter species composition and forest dynamics of subalpine coniferousforest ecosystems under future climate change.