65 resultados para kobresia


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以青海省果洛州藏族自治州甘德县青珍乡高山嵩草Kobresia pygmaea草甸轻度退化草地和重度退化草地为研究对象,通过植物地上部分主要功能群(禾草类、杂类草、莎草类)、植物根系和土壤碳、氮浓度及储量动态研究,结果表明:高寒小嵩草草甸轻度退化草地地上部分主要功能群碳、氮浓度和C∶N比值明显高于重度退化草地的浓度。同一草地类型主要功能群比较,碳、氮浓度依次为杂类草〉禾草类〉莎草类;植物地上部分的碳、氮浓度明显高于地下根系的碳、氮浓度。重度退化草地植物根系碳、氮浓度高于轻度退化草地植物根系碳、氮浓度。重度退化草地土壤总有机碳浓度显著低于轻度退化草地土壤总有机碳浓度,随着土层的加深碳、氮浓度有减少的趋势。江河源区高山嵩草草甸的土壤有机碳、氮储量最大,植物根系碳、氮储量居中,植物地上部分碳、氮储量最小。重度退化草地总有机碳储量(13554.3g/m~2)较轻度退化草地储量(14669.2g/m~2)下降7.60%。其中,0-40cm土壤层碳储量下降4.10%,植物根系碳储量下降59.97%,植物地上部分碳储量下降15.39%;重度退化草地总氮储量(3780.6g/m~2)较轻度退化草地储量(3352.7g/m~2)高12.76%,其中,0-40cm土壤中总氮储量高13.07%,植物根系全氮储量下降55.09%,植物地上部分全氮下降16.00%。由于草地退化损失有机碳11149kg/hm~2,而全氮增加4278kg/hm~2。

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This paper provides information about the distribution, structure, and ecology of the world's largest alpine ecosystem, the Kobresia pygmaea pastures in the southeastern Tibetan plateau. The environmental importance of these Cyperaceae mats derives from the extremely firm turf, which protects large surfaces against erosion, including the headwaters of the Huang He, Yangtze, Mekong, Salween, and Brahmaputra. The emphasis of the present article is on the climate-driven evolution and recent dynamics of these mats under the grazing impact of small mammals and livestock. Considering pedological analyses, radiocarbon datings, and results from exclosure experiments, we hypothesize that the majority of K. pygmaea mats are human-induced and replace forests, scrub, and taller grasslands. At present, the carrying capacity is increasingly exceeded, and reinforced settlement of nomads threatens this ecosystem especially in its drier part, where small mammals become strong competitors with livestock and the removal of the turf is irreversible. Examples of rehabilitation measures are given.

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Alpine Kobresia meadows are major vegetation types on the Qinghai-Tibetan Plateau. There is growing concern over their relationships among biodiversity, productivity and environments. Despite the importance of species composition, species richness, the type of different growth forms, and plant biomass structure for Kobresia meadow ecosystems, few studies have been focused on the relationship between biomass and environmental gradient in the Kobresia meadow plant communities, particularly in relation to soil moisture and edaphic gradients. We measured the plant species composition, herbaceous litter, aboveground and belowground biomass in three Kobresia meadow plant communities in Haibei Alpine Meadow Ecosystem Research Station from 2001 to 2004. Community differences in plant species composition were reflected in biomass distribution. The total biomass showed a decrease from 13196.96 +/- 719.69 g/m(2) in the sedge-dominated K. tibetica swamp to 2869.58 +/- 147.52 g/m(2) in the forb and sedge dominated K. pygmaea meadow, and to 2153.08 +/- 141.95 g/m(2) in the forbs and grasses dominated K. humilis along with the increase of altitude. The vertical distribution of belowground biomass is distinct in the three meadow communities, and the belowground biomass at the depth of 0-10 cm in K. tibetica swamp meadow was significantly higher than that in K. humilis and K. pygmaea meadows (P < 0.01). The herbaceous litter in K. tibetica swamp was significantly higher than those in K. pygnaeca and K. humilis meadows. The effects of plant litter are enhanced when ground water and soil moisture levels are raised. The relative importance of litter and vegetation may vary with soil water availability. In the K. tibetica swamp, total biomass was negatively correlated to species richness (P < 0.05); aboveground biomass was positively correlated to soil organic matter, soil moisture, and plant cover (P < 0.05); belowground biomass was positively correlated with soil moisture (P < 0.05). However, in the K. pygnaeca and K. humilis meadow communities, aboveground biomass was positively correlated to soil organic matter and soil total nitrogen (P < 0.05). This suggests that the distribution of biomass coincided with soil moisture and edaphic gradient in alpine meadows.

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We examined the CO2 exchange of a Kobresia meadow ecosystem on the Qinghai-Tibetan plateau using a chamber system. CO2 efflux from the ecosystem was strongly dependence on soil surface temperature. The COZ efflux-temperature relationship was identical under both light and dark conditions, indicating that no photosynthesis could be detected under light conditions during the measurement period. The temperature sensitivity (Q(10)) of the COZ efflux showed a marked transition around -1.0 degrees C; Q(10) was 2.14 at soil surface temperatures above and equal to -1.0 degrees C but was 15.3 at temperatures below -1.0 degrees C. Our findings suggest that soil surface temperature was the major factor controlling winter COZ flux for the alpine meadow ecosystem and that freeze-thaw cycles at the soil surface layer play an important role in the temperature dependence of winter CO2 flux. (c) 2005 Elsevier Ltd. All rights reserved.

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A nutrient amendment experiment was conducted for two growing seasons in two alpine tundra communities to test the hypotheses that: (1) primary production is limited by nutrient availability, and (2) physiological and developmental constraints act to limit the responses of plants from a nutrient-poor community more than plants from a more nutrient-rich community to increases in nutrient availability. Experimental treatments consisted of N, P, and N+P amendments applied to plots in two physiognomically similar communities, dry and wet meadows. Extractable N and P from soils in nonfertilized control plots indicated that the wet meadow had higher N and P availability. Photosynthetic, nutrient uptake, and growth responses of the dominants in the two communities showed little difference in the relative capacity of these plants to respond to the nutrient additions. Aboveground production responses of the communities to the treatments indicated N availability was limiting to production in the dry meadow community while N and P availability colimited production in the wet meadow community. There was a greater production response to the N and N+P amendments in the dry meadow relative to the wet meadow, despite equivalent functional responses of the dominant species of both communities. The greater production response in the dry meadow was in part related to changes in community structure, with an increase in the proportion of graminoid and forb biomass, and a decrease in the proportion of community biomass made up by the dominant sedge Kobresia myosuroides. Species richness increased significantly in response to the N+P treatment in the dry meadow. Graminoid biomass increased significantly in the wet meadow N and N+P plots, while forb biomass decreased significantly, suggesting a competitive interaction for light. Thus, the difference in community response to nutrient amendments was not the result of functional changes at the leaf level of the dominant species, but rather was related to changes in community structure in the dry meadow, and to a shift from a nutrient to a light limitation of production in the wet meadow.

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嵩草属隶属于莎草科苔草亚科苔草族,主要分布于北半球温带地区,少数种类为环北极分布,有一种产于泰国清迈,一种产于苏门达腊岛北部高山。本‘文在形态学、微形态学、解剖学和胚胎学研究的基础上,对嵩草属植物进行了全面的分类学修订,根据属内各类群之间的系统演化关系建立了一个新的属下分类系统,确认了世界范围内53种3亚种嵩草属植物,并做出5个种上等级的新组合,描述了一个新亚组。 作者研究了国内外14家标本馆(室)的3000多份腊叶标本并进行多次野外的实地观察,对嵩草属植物的形态学性状进行了详细的比较和分析,评价了它们的系统学价值及其演化趋势。在嵩草属中,花序是由小穗排列成的圆锥花序或穗状花序,花序各部分的形态性状是种及种上等级分类的基础;花序的演化趋势是由圆锥花序到穗状花序,小穗是从由数朵雄花与1朵雌花组成简化到由1朵雌花组成。但是,花序和小穗由复杂到简单的进化在嵩草属中平行地发生于不同的类群中。先出叶的性状状态是分种的主要特征之一,通常认为边缘开裂的先出叶是原始的,边缘合生而为囊状的先出叶是进化的。同样,先出叶由开裂到合生的进化也是多次发生的。此外,根状茎、秆、叶鞘、叶片、柱头及小坚果等的性状状态对于种及种上等级的分类都具有重要的意义。 应用扫描电子显微镜对38种(或亚种)嵩草属植物的小坚果表面进行了观察,证明小坚果纹饰在种及种上等级的分类中具有重要的参考价值,并能揭示种及种下等级的亲缘关系。例如,分布于喜马拉雅东部至横断山地区的3种植物,K.clarkeana、K.curvata和K.fragilis外部形态非常相似,难于区分,而其小坚果的微形态特征却可以提供3种之间关系的证据。K.clarkeana与K.fragilis果实表面的特征完全一致,且与其它植物有显著区别,应为同种植物;K.curvata与它们明显不同,也与其它种有较大差异,应为独立的种。K.gramini folia,K.cercostach ys和K. nepalensis果实表面纹饰具有一些共同的特征,说明它们之间的亲缘关系较近。K.filicina和K.duthiei也存在同样的情形。 通过对秆和叶片的横切面和表皮的解剖学观察比较,发现嵩草属植物秆的横切面表现出由三角形到圆形的一系列变化。秆的横切面明显地分两个区域,中部的髓由较大而无色的细胞组成,其中心常碎裂形成大的气腔;外围的绿色部分,由绿色组织及分布其中的气腔和外韧维管束及与其相伴的厚壁组织组成。秆的表皮与叶片下表皮非常相象。叶片横切面的外形为V形、新月形或半圆形。V形的叶片具有明显发育的中脉并且在远轴面凸起,形成脊;新月形和半圆形的叶片中脉发育不明显,也无脊。叶片的表皮细胞均为长方形,垂周壁波纹状;平列型的气孔器纵向成行排列,多局限于下表皮;上表皮近边缘及脉附近的细胞常常在细胞的一端形成乳突。秆和叶片横切面的形态对于分种及种上等级的划分具有参考价值。 胚胎学研究表明小孢子、胚囊和胚的发育与莎草科其它类群一致。花粉为假单体花粉( pseudomonad),成熟花粉三核。胚珠倒生,厚珠心,双层珠被,珠孑L由内珠被形成。胚囊的发育为蓼型,原胚的发育为柳叶菜型灯芯草变型。首次观察到,在大孢子四分体时期,合点端和珠孔端两个大孢子细胞开始时体积都增大,而中部两个很快退化,稍后珠孔端一个也退化,合点端一个为功能大孢子,发育成为胚囊。根据胚胎学证据,不支持将嵩草属与苔草族一起另立为嵩草科。 嵩草属中较原始的一个亚属subg. Compositae主要分布于西喜马拉雅至横断山地区,还有一种见于泰国,一种产于苏门达腊,而后2种植物还具有一些最原始的形态性状。结合地史的变化推测,嵩草属可能在第三纪早期起源于古地中海的东部和北部。 根据形态学和解剖学性状的分析表明,许多性状在嵩草属中是平行演化的,如花序和小穗由复杂到简单、秆由圆柱形到三棱形、叶片横切面由V形到半圆形等。该属的属下分类应该追溯这些平行的演化线,而不能像以前的分类那样,将它们横向地划分为几个组或亚属。作者认为嵩草属有3个大的进化分支,据此将其划分为3个亚属。Subg. Compositae,12种,是较原始的一个分支。叶近基生,叶片扁平;花序多疏松圆锥状,少穗状,苞片多为叶状;小穗两性到单性,先出叶多为囊状,少边缘分离,退化小穗轴明显、扁平、较长。Subg. Blysmocarex,仅2种,是较早分化而相对隔离的一个分支。根状茎匍匐状;花序由圆锥状到穗状,小穗两性或单性;柱头2。Subg. Kobresia,种类最多。叶片扁平或内卷;秆三棱形到圆柱形;花序紧密,复杂到简单,苞片不为叶状;小穗两性或单性,先出叶由开裂到合生,退化小穗轴较小而不显著。根据该亚属呈现出的不同的性状演化系列,可以分为3个组。Sect. Kobresia花序圆锥状至穗状,小穗多为两性,少为单性,先出叶边缘分离。含3个亚组:subsect. Kobresia,8种2亚种.植株纤细,秆与叶均为丝状;subsect. Royleanae,8种l亚种,植株较粗壮,叶片扁平或对折;subsect. Sibiri-cae,4种,秆较粗,叶片内卷。Sect. Psmmostachys,仅2种,小穗两性,先出叶完全合生为囊状。Sect.Hemicarex花序一般为穗状,稀圆锥状,小穗多为单性,少两性。分为四个亚组:subsect. Forexeta,6种,叶片内卷或对折,先出叶线形,边缘分离或合生;subsect. Chlorostachys,3种,叶片扁平,小穗两性;subsect. Holmia,4种,叶片扁平,小穗单性;subsect.Utriculatae,5种,叶片丝状,先出叶完全合生为囊状,不为线形。嵩草属的属下分类纲要如下: Subgenus 1. Compositae (Clarke) Kukkonen Type: K. laxa Nees. Subgenus 2. Blysmocarex (Ivanova) S. R. Zhang Type: K. macrantha Boeck. Subgenus 3. Kobresia Section 1. Kobresia Subsection 1. Kobresia Type: K. simpliciuscula (Wahl. ) Mack. Subsection 2. Royleanae (Ivanova) S. R. Zhang Type: K. royleana (Nees) Boeck. Subsection 3. Sibiricae (Ivanova) Egorova Type: K. sibirica (Turcz. ex Ledeb. ) Boeck. Section 2. Psmmostachys Ivanova Type: K. robusta Maxim. Section 3. Hemicarex (Bentham) Clarke Subsection 4. Forexeta (Raffin. ) S. R. Zhang Type: K. cercostachys (Franch. ) C. B. Clarke. Subsection 5. Chlorostachys (Ivanova) S. R. Zhang Type: K. duthiei C B. Clarke. Subsection 6. Holmia (Boern. ) S. R. Zhang Type: K. esenbeckii (Kunth) Noltie. Subsection 7. Utriculatae S. R. Zhang Type: K. prainii Kukenthal.

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本研究针对川西北高山草甸缺乏科学管理,过度放牧导致草场退化,并由此引发的一系列生态环境问题,选取红原县瓦切乡1996 年草地承包后形成的四个放牧强度草场,即不放牧、轻度(1.2 头牦牛hm-1)、中度(2.0 头牦牛hm-1)和重度放牧(2.9 头牦牛hm-1),作为研究对象,研究了不同放牧强度对草地植物-土壤系统中碳、氮这两个最基本物质的分布格局和循环过程的影响,并探讨了放牧干扰下高山草甸生态系统的管理。 1.放牧对草地植物群落物种组成,尤其是优势种,产生了明显的影响。不放牧、轻度、中度和重度放牧草地群落物种数分别为22,23,26,20 种,群落盖度分别是不放牧96.2%>中度93.6%>轻度89.7%>重度73.6%。随放牧强度的增加, 原植物群落中的优势种垂穗鹅冠草( Roegneria nutans )、发草(Deschampsia caespitosa)和垂穗披碱草(Elymus nutans)等禾草逐渐被莎草科的川嵩草(Kobresia setchwanensis)和高山嵩草(Kobresia pygmaea)所取代成为优势种。同时,随放牧强度的增加,高原毛茛(Ranunculus brotherusii)、狼毒(Stellera chamaejasme)、鹅绒委陵菜(Potentilla anserina)和车前(Plantagodepressa)等杂类草的数量也随之增加。 2.生长季6~9 月份,草地植物地上和地下生物量(0~30cm)都是从6 月份开始增长,8 月份达到最高值,9 月份开始下降。每个月份,通常地上生物量以不放牧为最高,重度放牧总是显著小于不放牧;地下生物量随放牧强度的增加表现为增加的趋势,通常重度和中度放牧显著高于不放牧和轻度放牧草地。不放牧、轻度、中度和重度放牧草地6~9 月份4 个月的植物总生物量平均值分别是1543、1622、2295 和2449 g m-2,但随放牧强度的增加越来越来多的生物量被分配到了地下部分,地下生物量占总生物量比例的大小顺序分别是重度88%>中度82%>轻度76%>不放牧69%。生物量这种变化主要是由于放牧使得群落优势种发生改变而引起的,其分配比例的变化体现了草地植物对放牧干扰的适应策略。 3.植物碳氮贮量的季节变化类似与生物量的变化。每个月份,不同放牧强度间植物地上碳氮的贮量有所不同,一般重度放牧会显著减少植物地上碳氮贮量。植物根系(0~30cm)碳氮贮量随放牧强度的增加表现为增加的趋势,通常重度和中度放牧显著高于不放牧和轻度放牧草地。不放牧、轻度、中度和重度放牧草地6~9 月份4 个月的植物总碳平均值分别是547、586、847 和909 g m-2,根系碳贮量占植物总碳的比例大小顺序分别是重度88%>中度82%>轻度76%>不放牧69%;放牧、轻度、中度和重度放牧草地6~9 月份4 个月的植物总氮平均值分别是17、17、23 和26 g m-2,根系氮贮量占植物总氮的比例大小顺序分别是重度79%>轻度71%>中度70%>不放牧65%。 4. 土壤有机碳贮量(0~30cm)的季节变化表现为7 月份略有下降,8 月开始增加,9 月份达到的最大值。土壤氮贮量的季节变化表现为随季节的推移逐渐增加的趋势。增加的放牧强度不同程度的增加土壤有机碳氮的贮量。不放牧、轻度、中度和重度放牧6~9 月份4 个月的土壤有机碳贮量的平均值分别是9.72、10.36、10.62 和11.74 kg m-2,土壤氮贮量分别为1.45、1.56、1.66 和1.83 kg m-2。土壤中有机碳(氮)的贮量都占到了植物-土壤系统有机碳(氮)的90%以上,但不同放牧强度之间的差异不明显。 5. 土壤氮的总硝化和反硝化,温室气体N2O 和CO2 的释放率的季节变化表现为从6 月份开始增加,7 月份达到最大值,8 月份开始下降,9 月份降为最小值。增加的放牧强度趋向于增加土壤氮的总硝化和反硝化作用,温室气体N2O和CO2 的释放率,通常情况下,中度放牧和重度放牧显著地加强了这些过程。 6.垂穗鹅冠草(Roegneria nutans)和川嵩草(Kobresia setchwanensis)凋落物在不同放牧强度下经过1 年的分解,两种凋落物的失重率及其碳氮的损失率3都随放牧增加表现为增加的趋势。在同一放牧强度下,川嵩草凋落物的失重率和碳氮的损失率都高于垂穗鹅冠草凋落物。 7. 尽管重度放牧显著增加了土壤碳氮的贮量,但同时也显著降低了植被群落盖度,降低了植物地上生物量,因此,久而久之会减少植物向土壤中的碳氮归还率;与不放牧和轻度放牧相比,重度放牧又显著增加了土壤CO2 和NO2 的排放量,这是草地生态系统碳氮损失的重要途径。由此可见,对于这些地处青藏高原的非常脆弱的高山草甸生态系统,长期重度放牧不仅导致植物生产力降低,而且将导致草地生态系统退化,甚至造成土壤中碳氮含量减少。 Long-term overgrazing has resulted in considerable deterioration in alpine meadowof the northwest Sichan Province. In order to explore management strategies for thesustainability of these alpine meadows, we selected four grasslands with differentgrazing intensity (no grazing-NG: 0, light grazing-LG: 1.2, moderate grazing-MG: 2.0,and heavy grazing-HG: 2.9 yaks ha-1) to evaluate carbon, nitrogen pools and cyclingprocesses within the plant-soil system in Waqie Village, Hongyuan County, Sichuan Province. 1. Grazing obviously changed the plant species composition, especially ondominant plant species. Total number of species is 22, 23, 26, and 20 for NG, LG, MGand HG, respectively. Vegetation coverage under different grazing intensity ranked inthe order of 96.2% for HG>93.6% for MG>89.7% for LG>73.6% for NG. Thedominator of HG community shifted from grasses-Roegneria nutans andDeschampsia caespitosa dominated in the NG and LG sites into sedges-Kobresiapygmaea and K. setchwanensis. At the same time, with the increase of grazingintensity, the numbers of forbs, such as Ranunculus brotherusii, Stellera chamaejasme,Potentilla anserine and Plantago depressa, increased with grazing intensity. 2. Over the growing season, aboveground and belowground biomass showed a 5single peak pattern with the highest biomass in August. For each month, abovegroundbiomass usually was the highest in the NG site and lowest in the HG site.Belowground biomass showed a trend of increase as grazing intensity increased and itwas significantly higher in the HG and MG site than in the NG and LG sites. Totalplant biomass averaged over the growing season is 1543, 1622, 2295 and 2449 g m-2for NG, LG, MG and HG, respectively. The proportion of biomass to total plantbiomass for NG, LG, MG and HG is 88%, 82%, 76% and 69%, respectively. Higherallocation ratio for is an adaptive response of plant to grazing. 3. Carbon and nitrogen storage in plant components followed the similar seasonalpatterns as their biomass under different grazing intensities. Generally, heavy grazingsignificantly decreases aboveground biomass carbon and nitrogen compared to nograzing. Carbon and nitrogen storage in root tended to increase as grazing increasedand they are significantly higher in the HG and MG sites compared to the LG and NGsite. Total Carbon storage in plant system averaged over the growing season is 547,586, 847 and 909 g m-2 for NG, LG, MG and HG, respectively, while 17, 17, 23 and 26g m-2 for nitrogen. The proportion of carbon storage in root to total plant carbon forNG, LG, MG and HG is 88%, 82%, 76%, 69%, respectively, while 65%, 71%, 70%and 79% for nitrogen. 4. Carbon storage in soil (0-30cm) decreased slightly in July, then increased inAugust and peaked in September. Nitrogen storage in soil tended to increase withseason and grazing intensity. Total Carbon storage in soil averaged over the growingseason is 9.72, 10.36, 10.62 and11.74 kg m-2 for NG, LG, MG and HG, respectively,while 1.45, 1.56, 1.66 and 1.83 for nitrogen. The proportion of carbon (nitrogen)storage in soil to plant-soil system carbon (nitrogen) storage for NG, LG, MG and HGis more than 90%, which is not markedly different among different grazing intensities. 5. Gross nitrification, denitrification, CO2 and N2O flux rates in soil increasedfrom June to July and then declined until September, all of which tended to increasewith the increase of grazing intensity. Generally, heavy and moderate grazing intensitysignificantly enhanced these process compared to no and light grazing intensity. 6. After decomposing in situ for a year, relative weight, carbon and nitrogen loss in the litter of Roegneria nutans and Kobresia setchwanensis tended to increase asgrazing intensity increased. Under the same grazing intensity, relative weight, carbonand nitrogen loss in the litter of Kobresia setchwanensis were higher than these in thelitter of Roegneria nutans. 7. Although heavy grazing intensity resulted in higher levels of carbon andnitrogen in plant and soil, it decreased vegetation coverage and aboveground biomass,which are undesirable for livestock production and sustainable grassland development.What is more, heavy grazing could also introduce potential carbon and nitrogen lossvia increasing CO2 and N2O emission into the atmosphere. Grazing at moderateintensity resulted in a plant community dominated by forage grasses with highaboveground biomass productivity and N content. The alpine meadow ecosystems inTibetan Plateau are very fragile and evolve under increasing grazing intensity by largeherbivores; therefore, deterioration of the plant-soil system, and possible declines insoil C and N, are potential without proper management in the future.

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若尔盖高原湿地位于青藏高原东北部地区,平均海拔3,400-3,600m,是长江和黄河的自然分水区,区内发育了大面积的草本沼泽以及高寒沼泽化草甸、高寒湖泊。由于它所处的位置海拔高、气候波动较大,并处于我国三大自然区的交错过渡带,因而被认为是我国最为典型的脆弱湿地生态系统之一。由于地处偏远、自然环境条件恶劣等多方面的原因,针对若尔盖湿地的科学研究资料一直以来还非常缺乏。本文对国内外近年来在湿地生态系统甲烷排放过程、研究方法,以及关于湿地生态系统甲烷排放的影响因素进行了综述,并采用静态箱-气相色谱法,从湿地环境格局、湿地甲烷排放等方面,对若尔盖高原典型高寒湖泊湖滨不同类型湿地甲烷排放特征进行了研究,并进一步探讨了影响若尔盖高原高寒湖泊湖滨带甲烷排放的因素。得到如下结果:1.若尔盖高原花湖湖滨湿地在植物生长季(6 至8 月),甲烷排放平均速率为0.315 mg·m-2·h-1;不同月份间甲烷排放速率存在差异,分别为:-0.054、0.471、0.493 mg·m-2·h-1。不同类型湿地甲烷排放速率亦表现出差异,两栖蓼(Polygonum amphibium)湿地、滩涂和藏嵩草(Kobresia tibetica)草甸甲烷排放速率分别为:0.464、0.477、0.005mg·m-2·h-1。2.若尔盖高原花湖湖滨湿地甲烷排放速率与土壤10cm 温度显著相关。土壤温度是影响若尔盖高原花湖湖滨不同类型湿地甲烷排放的重要因素之一。随着土壤温度的升高,土壤微生物活性增强,使土壤中的氧消耗加快,氧化还原电位下降,有利于产甲烷菌的生长,从而增加土壤的甲烷产生量。3.地表水位与若尔盖高原花湖湖滨湿地甲烷排放速率相关性不显著。地表水覆盖,使得湿地土壤缺氧状况得到加强,增强了土壤中产甲烷菌的活性,促进甲烷形成,再通过植物、气泡或扩散的形式释放出土壤。但水层的加深,也使土壤中已产生的甲烷在通过气泡或扩散形式穿越水层时,被氧化的量增加,从而减少了甲烷向大气中的排放。4.植被高度以及植被地上生物量与若尔盖高原花湖湖滨带甲烷排放速率的相关性不显著。植物主要通过凋落物以及根系分泌物的输入为产甲烷菌提供基质,并作为土壤与大气之间的甲烷气体交换的传输途径;与其他环境因素共同影响湿地生态系统甲烷排放。The Zoige wetland on the eastern fringe of Qinghai-Tibetan Plateau, with averagealtitude between 3,400 and 3,600m, is the watershed of Yangtze River and YellowRiver. There are large area of peatland, subalpine meadow and lakes in this region.Due to its high elevation, transitional topology and high fluctuation of climate, theZoige wetlands represent one of the most fragile wetland ecosystems in China. And asa result of remote location and harsh environment conditions, the researches on theZoige wetland are relatively rare, especially the researches on the methane emissionfrom littoral zone of alpine lakes. Variations of methane emission rates as measuredby the method of static chamber – gas chromatography (GC) were detected fromlittoral zone of alpine lake on the Zoige Plateau. Relationships between methaneemission rates and environmental factors were analyzed. It is concluded that:1.The average methane emission rate in the littoral zone of Huahu Lake, ZoigePlateau is 0.315 mg·m-2·h-1, with evident spatial and temporal variations. The littoralzone has different methane effluxes with -0.054, 0.471, and 0.493 mg·CH4·m-2·h-1in June, July and August respectively. Different types of wetland have differentmethane emission rates, with value of 0.464, 0.477, and 0.005 mg·CH4·m-2·h-1 forPolygonum amphibium wetland ( PA ), Shoal ( S ) and Kobresi tibetica meadow ( KT ), respectively.2. The soil temperature at 10cm is significantly correlated with the methane effluxesin littoral zone of Huahu Lake, Zoige Plateau, and which is one of the most important factors influencing the methane emission from this region. The activities of soilmicroorganisms rise under higher soil temperature and increases oxygen consumptionand decreases Eh, which is in favor of the methanogensis, and enhances theproduction of methane in soil.3. The correlation between the standing water and methane effluxes from littoralzone of Huahu Lake is not significant. Because of the standing water, the anaerobicconditions of wetland soil have been enhanced, and are favor to the decomposition oforganic matter. And the anaerobic conditions strengthen the methanogensis’ activities,thus the methane production, which release to the atmosphere by diffusion, ebullitionand aerenchymal plants. With the water level’s increase, more methane produced insoil which is transferred by ebullitions or diffusion are oxidated, thus reduce themethane release to the atmosphere.4. The height and aboveground biomass of vegetation are not significant related tothe methane effluxes from littoral zone of Huahu Lake, Zoige Plateau. The vegetationprovides substrates for methanogensis by litter and root exudates; act as thetransportation way of methane between soil and atmosphere; influence the methaneemission of wetland ecosystems with other environment factors.

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瑞香狼毒(Stellera chamaejasme L.)是瑞香科(Thymelaeaceae)狼毒属的一种多年生野草,有毒。据调查,从20 世纪60 年代开始至今,狼毒在青藏高原东缘的高寒草甸上不断蔓延、密度不断变大,在一些地段甚至成为优势物种。有关狼毒在高寒草甸蔓延的生态系统效应的研究尚未见报道。本文从系统碳、氮循环的角度,分别研究狼毒在生长和非生长季节对高寒草甸生态系统的影响。同时,从花粉化感的角度,深入研究狼毒对当地同花期物种有性繁殖的影响。系统地研究高寒草甸生态系统物质循环过程,特别是非生长季节微生物和土壤碳氮库的动态变化,有助于揭示狼毒在系统物质循环方面的“物种效应”以及这种效应的季节变化,为丰富有关高海拔生态系统,特别是其非生长季的物质循环的科学理论做出贡献。同时,碳氮循环和花粉化感的研究还有助于深刻地理解狼毒作为一种入侵性很强的杂草的特殊的蔓延机制,从而为狼毒的有效防治、高寒草甸的科学管理提供依据。 针对狼毒在青藏高原高寒草甸上蔓延的生态系统碳氮循环方面的影响,开展以下2 方面的研究:(1)在生长季,研究松潘县尕米寺附近(北纬32°53',东经103°40',海拔3190 m)的两种地形(平地和阳坡)条件下狼毒对土壤碳氮循环影响及可能的原因。狼毒和其它几个主要物种(圆穗蓼(Polygonummacrophyllum D. Don var. Macrophyllum),草地早熟禾(Poa pretensis L.),四川嵩草(Kobresia setchwanensis Hand.-Maizz.),鹅绒委陵菜(Potentilla anserina L.var. anserine)和鳞叶龙胆(Gentiana squarrosa Ledeb.)的地上凋落物产量以及地上凋落物和根的化学组成被测量。在有-无狼毒斑块下,各种土壤的库(比如,铵态氮、硝态氮、无机磷和微生物生物量)和周转率(包括净矿化、净硝化、总硝化、反硝化和微生物呼吸速率)被测量和比较。(2)在非生长季节,尤其是春季冻融交替期,选取了两个研究地点——尕米寺和卡卡沟(北纬32°59',东经103°41',海拔3400 m),分别测定有狼毒和无狼毒斑块下土壤微生物生物量碳和氮、可溶性有机碳和氮以及铵态氮和硝态氮的动态变化。同时,分别在上述两个地点有-无狼毒的样地上,研究6 个主要物种(狼毒、圆穗蓼、草地早熟禾、四川嵩草、鹅绒委陵菜和鳞叶龙胆)从秋季开始、为期1 年的凋落物分解过程。 针对狼毒花粉化感对同花期其它物种可能的花粉化感作用开展以下工作:在实验室中,用一系列浓度的狼毒花粉水浸提液对与它同花期的其它物种以及自身花粉进行测试,测定花粉萌发率;在野外自然条件下的其它物种的柱头上施用上述浓度的狼毒花粉水浸提液,观测种子结实率,同时,观察狼毒花粉的种间花粉散布数量。 生长季节的研究结果表明,狼毒地上凋落物氮含量比其它几个主要物种更高,而木质素-总氮比更低。狼毒显著地增加其斑块下表层土壤中有机质的含量,而有-无狼毒的亚表层土壤在有机碳和总磷方面没有显著差异。狼毒表土中硝态氮含量在平地和阳坡比无狼毒土壤分别高113%和90%。狼毒表土中微生物生物量碳和氮量显著高于无狼毒表土。无论是平地还是阳坡,狼毒土壤的总硝化和微生物呼吸速率显著高于无狼毒土壤;而它们的反硝化速率只在平地有显著的差异。狼毒与其它物种间地上凋落物的产量和质量的差异可能是导致有-无狼毒土壤碳氮循环差异的原因。我们假设,狼毒可能通过增加贫氮生态系统土壤中的有效氮含量提高其入侵能力。 非生长季的研究结果表明,在青藏高原东缘的高寒草甸上,土壤微生物生3物量在11 月的秋-冬过渡期达到第一个峰值;在春季的冻融交替期,微生物生物量达到第二个峰值后又迅速降低。无机氮以及可溶性有机碳氮与微生物生物量有相似的变化过程。微生物碳氮比呈现显著的季节性变化。隆冬季节的微生物生物量碳氮比显著高于生长旺季的微生物碳氮比。这种变化可能暗示冬、夏季微生物的群落组成和对资源的利用有所不同。有-无狼毒斑块下土壤微生物和土壤碳、氮库一般只在秋-冬过渡期有显著差异,有狼毒土壤微生物生物量和土壤碳、氮库显著高于无狼毒土壤;而在之后的冬季和春季没有显著差异。所有6 个物种凋落物在非生长季分解率为24%-50%,均高于生长季的10%到30%。其中在秋-冬过渡期,凋落物开始埋藏的两周时间内,分解最快,达10%-20%。不同物种凋落物全年的分解率和分解过程有显著差异。圆穗蓼在全年的分解都较缓慢(非生长季26%,生长季15%),草地早熟禾和四川嵩草等全年的分解速率比较均匀(非生长季和生长季均为30%,非生长季略高),而狼毒在非生长季分解较快(约50%),而在接下来的生长季分解变得缓慢(约12%)。所有物种的凋落物氮含量在非生长季下降,而在随后的生长季上升。 实验室的花粉萌发试验证明,狼毒花粉对自身花粉萌发没有自毒作用,而其它受试的所有物种(圆穗蓼,秦艽(Gentiana macrophylla Pall. var. fetissowii),湿生扁蕾(Gentianopsis paludosa (Hook. f.) Ma var. paludosa),鳞叶龙胆,椭圆叶花锚(Halenia elliptica D. Don var. elliptica),蓝钟花(Cyananthus hookeri C. B.Cl. var. grandiflorus Marq.),小米草(Euphrasia pectinata Ten.),川西翠雀花(Delphinium tongolense Franch.),高原毛茛(Ranunculus tanguticus (Maxim.)Ovcz. var. tanguticus)和鹅绒委陵菜)的花粉萌发率随着狼毒花粉浸提液浓度的增加呈显著的非线性降低。大约3 个狼毒花粉的浸提液就可以抑制受试的多数物种的50%的花粉萌发。在鳞叶龙胆和小米草柱头上狼毒花粉的数量分别为5.76 个和3.35 个。狼毒花粉散布数量的差异最可能的原因在于是否有共同的传粉昆虫。花的形状(辐射对称VS 左右对称)、植株或花的密度以及花期重叠性可以部分解释这种差异。在野外试验中,我们发现6 个物种(秦艽、湿生扁蕾、鳞叶龙胆、椭圆叶花锚、蓝钟花和小米草)的种子结实率随狼毒花粉浸提液浓度的增加呈显著的非线性降低。鳞叶龙胆和小米草柱头上狼毒花粉的数量(分别是5.76 个和3.35 个)分别达到了抑制它们63%和55%种子结实率的水平。因此,狼毒对鳞叶龙胆和小米草可能存在明显的花粉化感抑制作用。狼毒周围的物种可能通过花期在季节或昼夜上的分异避免受到狼毒花粉化感的影响或者通过无性繁殖来维持种群繁衍,因此狼毒通过花粉化感作用对其周围物种繁殖的影响程度还需要进一步地研究。如果狼毒的花粉化感抑制作用确实存在,那么它可能成为一种自然选择压力,进而影响物种的进化。 Stellera chamaejasme L., a perennial toxic weed, has emerged and quicklydominated and spread in the high-frigid meadow on the eastern Tibetan Plateau ofChina since the 1960s. In the present study, effects of S. chamaejasme on carbon andnitrogen cycles on the high-frigid meadow on the eastern Qinghai-Tibetan Plateau ingrowing and non-growing season, and its pollen allelopathic effects on the sympatricspecies were determined. The present study that focused on carbon and nitrogencycles, especially on microbial biomass and pools of carbon and nitrogen innon-growing season, could profoundly illuminate plant-species effects on carbon andnutrient cycles and its seasonal pattern and help to understand spread mechanism ofS. chamaejasme as an aggressive weed. The present study also contributed to furtherunderstand carbon and nutrient cycles on alpine regions in non-growing season andprovide a basis on weed control of S. chamaejasme and scientific management in thehigh-frigid ecosystem. Effects of S. chamaejasme on carbon and nitrogen cycles on the high-frigidmeadow on the eastern Qinghai-Tibetan Plateau were determined. The study couldbe divided into two parts. (1) In the growing season, we quantified the effects of S.chamaejasme on carbon and nitrogen cycles in two types of topographic habitats, theflat valley and the south-facing slope, where S. chamaejasme was favored to spreadlitter and root were measured to explain the likely effects of S. chamaejasme on soilcarbon and nutrient cycles. The sizes of various soil pools, e.g. nitrite, ammonium,inorganic phosphorus and microbial biomass, and turnover rates including netmineralization, gross nitrification, denitrification and microbial respiration weredetermined. (2) In the non-growing season study, microbial biomass carbon andnitrogen, soluble organic carbon and nitrogen, ammonium and nitrate weredetermined through the non-growing season, especially in the processes offreeze-thaw of spring in two high-frigid sites, i.e. Kaka valley and Gami temple, onthe eastern Qinghai-Tibetan Plateau. Meanwhile, litter decomposition of six commonspecies, including Stellera chamaejasme L., Polygonum macrophyllum D. Don var.Macrophyllum, Poa pretensis L., Kobresia setchwanensis L., Potentilla anserina L.var. anserine and Gentiana squarrosa Ledeb., were also examined under theabove-mentioned experimental design through one whole-year, which began in theautumn in 2006. In the study of pollen allelopathy, several work, including in vitro study oneffects of extract of pollen from S. chamaejasme on sympatric species and pollenfrom itself, field experiments on effects of pollen extract with the same regime ofconcentrations on seed set and field observation on heterospecific pollen transfer ofS. chamaejasme to six of those sympatric species has been done. The results in the growing season showed that aboveground litter of S.chamaejasme had higher tissue nitrogen and lower lignin: nitrogen ratio than thoseco-occurring species. S. chamaejasme significantly increased topsoil organic matter,whereas no significant differences were found for organic C and total P in subsoilbetween under-Stellera and away-Stellera locations. The nitrate in Stellera topsoilwas 113% and 90% higher on the flat valley and on the south-facing slope,respectively. Both microbial biomass C and N were significantly higher in Stelleratopsoil. Gross nitrification and microbial respiration were significantly higher inStellera topsoil both on the flat valley and on the south-facing slope, whereassignificant differences of denitrification were found only on the flat valley. Thedifferences in the quantity and quality of aboveground litter are a likely mechanismresponsible for the changes of soil variables. We assumed that S. chamaejasme couldenhance their spread by increasing nutrient availability in N-deficient ecosystems. The results in the non-growing season showed that microbial biomass achievedthe first summit in late autumn and early winter on the eastern Qinghai-TibetanPlateau. In the stages of freeze-thaw of spring, microbial biomass firstly achieved thesecond summit and subsequently sharply decreased. Inorganic nitrogen, solubleorganic carbon and nitrogen had a similar dynamics with that of microbial biomass.Ratio of microbial biomass carbon and nitrogen had an obviously seasonal pattern.The highest microbial C: N were in the non-growing season, which weresignificantly higher than those in the growing season. The seasonal pattern inmicrobial biomass C: N suggested that large changes in composition of microbialpopulation and in resources those used by microbes between summer and winter.Generally, microbial biomass and pools size of carbon and nitrogen in Stellera soilwere significantly higher than those under adjacent locations in late autumn andearly winter, but there were not significant differences in winter and in spring. Litterof all the focal species (Stellera chamaejasme L., Polygonum macrophyllum D. Donvar. Macrophyllum, Poa pretensis L., Kobresia setchwanensis Hand.-Maizz.,Potentilla anserina L. var. anserine and G. squarrosa Ledeb.) decomposed about24%-50% in the non-growing season, which were higher than those in the growingseason (ranged from 10% to 30%). Litter decomposed 10%-20% within the first twoweeks in late autumn and early winter. Significant differences in the whole-yeardecomposition rate and in the processes of decomposition were found among species.Polygonum macrophyllum decomposed slowly through the whole year (26% and15% in the non-growing season and in the growing season, respectively). Certainspecies, such as P. pretensis L. and K. setchwanensis, decomposed at a similar rate(30% both in the non-growing and in the growing season, slightly higher in the8growing season than those in the growing season), whereas S. chamaejasmedecomposed more rapidly (about 50%) in the non-growing season and subsequentlydecomposition became slow (about 12%) in the growing season. Litter nitrogencontents of all the focal species firstly decreased in the non-growing season and thenincreased in the growing season. In vitro experiments of pollen allelopathy, the results showed that pollen from S.chamaejasme was not autotoxic, whereas pollen germination in all the sympatricspecies (Polygonum macrophyllum D. Don var. Macrophyllum, Gentianamacrophylla Pall. var. fetissowii, Gentianopsis paludosa (Hook. f.) Ma var. paludosa,Gentiana squarrosa Ledeb., Halenia elliptica D. Don var. elliptica, Cyananthushookeri C. B. Cl. var. grandiflorus Marq., Euphrasia pectinata Ten., Delphiniumtongolense Franch., Ranunculus tanguticus (Maxim.) Ovcz. var. tanguticus andPotentilla anserina L. var. anserina) decreased nonlinearly as the increasingconcentrations of extract of pollen from S. chamaejasme. Pollen Extract of threepollens from S. chamaejasme generally inhibited 50% pollen germination of most ofthe focal species. 5.76 and 3.35 pollens from S. chamaejasme were observed in fieldon stigmas of G. squarrosa and E. pectinata, respectively. Differences inheterospecific pollen transfer of S. chamaejasme could be attributed to the primaryreason whether they shared common pollinators. Flower morphology (e.g.zygomorphic or actinomorphic), plant or floral density and concurrence in floweringphonologies could explain, in part, the differences in heterospecific pollen transfer.In field experiments, the results showed that seed set in six sympatric species(Gentiana macrophylla Pall. var. fetissowii, Gentianopsis paludosa (Hook. f.) Mavar. paludosa, Gentiana squarrosa Ledeb., Halenia elliptica D. Don var. elliptica,Cyananthus hookeri C. B. Cl. var. grandiflorus Marq. and Euphrasia pectinata Ten.)decreased nonlinearly as the increasing concentrations of extract of pollen from S.chamaejasme. According to the nonlinear curves, the amounts of pollens from S.chamaejasme on stigmas of G. squarrosa and of E. pectinata (i.e. 5.76 grains and3.35 grains, respectively) could reduce 63% and 55% seed set of G. squarrosa and ofE. pectinata, respectively. Thus, allelopathic effects of S. chamaejasme on G.squarrosa and E. pectinata could be realistic. The sympatric species of S.chamaejasme could avoid pollen allelopathy of S. chamaejasme to sustainthemselves. This highlights the need to study how much pollen allelopathy in S.chamaejasme influences the sympatric species through divergence in seasonal ordiurnal flowering phonologies or through asexual reproduction. If pollen allelopathyin S. chamaejasme was confirmed, it could be as a pressure of natural selection andthus play an important role in species evolution.

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通过研究围栏封育1年后中度退化的矮嵩草草甸(夏季牧场)群落结构的变化,探讨主要植物种群在小尺度(50 cm×50 cm)上的空间分布格局,并从生活史特征和生态适应对策等角度探讨产生和维持这些格局的机理。结果表明,围封1年显著降低了群落中主要种群矮嵩草(Kobresia humilis)、高山唐松草(Thalictrum alpinum)和雪白委陵菜(Potentilla nivea)的重要值,而增加了线叶龙胆(Gentiana farreri)的重要值;显著增加了群落的地上生物量和总生物量,但对地下生物量和群落多样性的影响不显著。围封使退化矮嵩草草甸主要种群矮嵩草、高山唐松草、珠芽蓼(Polygonum viviparum)、线叶嵩草(Kobresia capillifolia)和金露梅(Potentilla fruticosa)等空间分布格局从放牧后的随机分布向聚集分布发展,而雪白委陵菜、重齿风毛菊(S.katochaeteMaxim)、矮火绒草(Leonto-podium nanum)和美丽风毛菊(Saussurea pulchra)等种群的空间分布格局没有发生改变;但黑褐苔草(Carex atro-fusca)的空间格局从放牧后的聚集分布转向随机分布。因此,退化的矮嵩草草甸在围封的初始阶段,由于避免了家畜的选择性采食及其践踏作用,首先可能是使主要种群的空间分布格局有从随机分布向聚集分布变化的趋势,从而使小尺度的种间隔离来降低种间的竞争强度,从而改变了不同物种对资源和空间的竞争能力,进而推动群落物种组成和结构的恢复演替。

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选择江河源区玛多、曲麻莱、同德3地区的典型紫花针茅(Stipa purpurea)草原为研究对象,采用样线和样方相结合的方法调查群落,初步分析了江河源区紫花针茅草原的群落特征。结果表明:1)所调查紫花针茅草原群落是物种组成比较简单、北温带分布的属为主体的草原群落。2)所有样线经聚类分析可归为3个群落类型:紫花针茅十二裂委陵菜(Potentilla bifurca)群落(Ⅰ)、紫花针茅+高山嵩草(Kobresia pygmaea)群落(Ⅱ)、紫花针茅+川青早熟禾(Poa indattenuata)群落(Ⅲ),且各群落分布于不同区域。虽然这3个群落类型都是典型的紫花针茅群落,但各自的群落结构还是存在一定差异,群落相似性分析结果表明群落Ⅰ和Ⅱ的相似性较高,群落Ⅰ和Ⅲ的相似性较低。3)紫花针茅草原的群落分布呈现出小尺度区域同质性和人尺度异域异质性的特点。4)所调查紫花针茅草原群落的均匀度指数、Shannon-Wiener指数和Simpson指数间以及它们和纬度间均呈显著相关。各α多样性指数在3个地区的群落间表现出基本一致的变化规律,按均匀度指数、Shannon-Wiener指数和Simpson指数从大到小的顺序依次是:群落Ⅱ〉群落Ⅲ〉群落Ⅰ。

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通过研究自然条件下模拟平流层臭氧破坏5%时近地表面增加的太阳UV-B辐射对高寒草甸4种典型植物(矮嵩草Kobresia humilis、垂穗披碱草Elymus nutans、麻花艽Gentiana straminea和鹅绒委陵菜Po-tentilla anserina)的抗氧化系统的影响表明,尽管各植物的抗氧化系统组分变化不同,但4种植物的膜脂过氧化程度没有加剧,长期增强UV-B辐射没有对膜系统造成损伤。在自然长期增强UV-B条件下,4种植物的膜脂过氧化产物——丙二醛(MDA)含量与对照相比无显著差异。垂穗披碱草、鹅绒委陵菜的谷胱甘肽(GSH)含量增加,麻花艽的超氧化物歧化酶(SOD)活性与鹅绒委陵菜的过氧化氢酶(CAT)活性上升,同时麻花艽的类胡萝卜素(Car)含量亦显著增加。可见这些植物已能很好地适应UV-B强辐射,其抗氧化能力除了与抗氧化系统各组分的协同作用有关外,也可能与种的适应性有关。

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以青海省达日县高寒草甸原生高寒嵩草(Kobresia)草甸封育系统为对照,研究了土地退化对植被生产力的影响,检验了不同人工重建措施(两个人工种植处理:混播(HB)、翻耕单播(DBF)和1个退化草地封育自然恢复处理(NR)及1个退化草地自然状态(SDL))对植被生产力的相对影响程度。结果表明,原生植被封育处理(YF)地上总生物量为265.1g•m~(-2),混播(HB)和翻耕单播(DBF)处理中地上总生物量分别为原生植被封育处理的116%和68%。退化草地封育自然恢复处理(NR)和重度退化自然状态下地上总生物量分别为原生植被封育的76%和53%。YF处理根系生物量远大于其它处理。原生植被封育系统中植被地上部分碳储量为110.14g•m~(-2),地下根系(0~30cm)碳储量为2957g•m~(-2),植被总碳储量为3067.14g•m~(-2);重度退化草地系统中植被地上部分碳储量为57.07g•m~(-2),地下根系(0~30cm)碳储量为357g•m~(-2),植被总碳储量为414.07g•m~(-2)。由此可见,高寒草甸严重退化后,通过植物组织流失的碳达到2653.35g•m~(-2),即86.5%的碳损失;原生植被封育系统植被总氮储量为56.85g•m~(-2),而重度退化草地植被总氮储量为18.02g•m~(-2),高寒草甸严重退化使植物组织68.30%氮损失。与重度退化地相比,由于恢复重建措施增加了植物的生物量输入和群落组成,除翻耕单播处理外,其它恢复重建措施均能恢复系统植被的碳氮储量。这些恢复重建措施将会逐步改善土壤的物理和化学特性,最终使这些生态系统逐步由碳源向碳汇方向的转变成为可能。

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以海北高寒草甸生态系统定位站的涡度相关系统连续观测的CO_2通量数据为基础,分析了青藏高原的高寒矮嵩草(Kobresia humilis)草甸、高寒金露梅(Potentilla fruticosa)灌丛草甸和高寒藏嵩草(Kobresia tibetica)沼泽化草甸等3种主要植被类型在2005年植物生长季(6-9月)的表观量子产额(a)、最大光合速率(Pmax)和呼吸速率(Reco)的变化特征.结果表明:3种植被类型白天的净生态系统CO_2交换量(NEE)和光量子通量密度(PPFD)存在明显的直角双曲线关系(P<0.05),其a、Pmax和Reco呈现出相似的季节变化趋势,在生长季初期(6月)最小,在7月或8月份达到最大;高寒矮嵩草草甸的a、Pmax和Reco大于灌丛草甸和沼泽化草甸,而后两者差别不大.