三江平原草甸湿地土壤呼吸和枯落物分解的CO2释放

利用静态箱-碱液吸收法研究了三江平原草甸湿地土壤呼吸和枯落物分解的CO2释放速率,讨论了影响CO2释放的环境因素,估算了枯落物分解的CO2释放对于总释放的贡献.结果表明,生长季,小叶章沼泽化草甸和小叶章湿草甸各部分CO2释放均具有明显的时间变化特征,温度和水分是重要制约因素.两类草甸湿地的平均土壤呼吸速率分别为4.33g·m-2·d-1和6.15g·m-2·d-1,枯落物分解的CO2平均释放速率分别为1.76g·m-2·d-1和3.10g·m-2·d-1,枯落物分解的CO2释放占总释放量的31%和35%,说明在碳素由地上植物碳库转移到地下土壤碳库的过程中,湿地枯落物是一个不可忽略的碳损失源.     

三江平原草甸湿地土壤呼吸和枯落物分解的CO2释放

利用静态箱-碱液吸收法研究了三江平原草甸湿地土壤呼吸和枯落物分解的CO₂释放速率,讨论了影响CO₂释放的环境因素,估算了枯落物分解的CO₂释放对于总释放的贡献。结果表明,生长季,小叶章沼泽化草甸和小叶章湿草甸各部分CO₂释放均具有明显的时间变化特征,温度和水分是重要制约因素。两类草甸湿地的平均土壤呼吸速率分别为4.33g•m^-2•d^-1和6.15g•m^-2•d^-1,枯落物分解的CO₂平均释放速率分别为1.76g•m^-2•d^-1和3.10g•m^-2•d^-1,枯落物分解的CO₂释放占总释放量的31%和35%,说明在碳素由地上植物碳库转移到地下土壤碳库的过程中,湿地枯落物是一个不可忽略的碳损失源。     

三江平原典型湿地植物中汞的分布与库存量

分析了三江平原典型植物中的总Hg浓度．结果表明,各种植物中总Hg浓度差别较大,苔藓>藻类>苔草>禾草>灌木;干湿环境是影响总Hg浓度的重要因素;湿地植物总Hg浓度高于水稻和玉米等农作物．较高的土壤总Hg浓度是近地面大气中Hg的重要来源,间接地影响到植物中Hg的浓度．植物各构件中总Hg浓度具有立枯>根>叶>茎的特点．在植物整个生长季总Hg浓度先增加后减少．估算了三江平原湿地植物Hg的库存量．小叶章湿地植物地上部分库存量为24．9μg·m^-2;毛果苔草湿地植物地上部分库存量为35．8μg·m^-2,高于加拿大实验湖泊湿地．     

三江平原典型湿地枯落物早期分解过程及影响因素

枯落物分解是湿地物质循环和能量流动的关键环节,是维持湿地功能的重要过程之一。采用分解袋法对三江平原3种典型湿地植物枯落物分解过程及影响因素进行了研究。研究表明,在164d实验过程中乌拉苔草分解速率始终最快;在分解前103d中毛果苔草分解速率大于小叶章,但在103~164d间小叶章分解速率大于毛果苔草;分解164d,小叶章、乌拉苔草和毛果苔草枯落物的失重率分别为初始重的31.98%、32.99%和28.91%。分解过程中小叶章和毛果苔草枯落物中有机碳浓度波动较大,而乌拉苔草枯落物中持续下降;3种枯落物有机碳绝对含量都表现为净释放。小叶章枯落物中N浓度波动较大,绝对含量发生净释放;毛果苔草枯落物N浓度持续增加,绝对含量净增加;乌拉苔草枯落物N浓度先增加后减少,绝对含量发生净释放。3种枯落物中P浓度都先迅速下降后缓慢上升,绝对含量都表现为净释放。3种枯落物中C/N和C/P也相应的发生变化。小叶章和乌拉苔草枯落物分解速率与枯落物C/P显著相关,而毛果苔草枯落物与枯落物N浓度显著相关;对应3种枯落物分解速率的主要环境因子分别为土壤含水量、土壤容重和土壤温度。3种枯落物分解速率和营养物质含量动态受到枯落物自身质量和温湿条件、周围环境营养状况等自然环境条件的共同影响,相比而言,受枯落物质量的影响更大。     

三江平原小叶樟、毛果苔草枯落物中氮素变化分析

以三江平原沼泽湿地主要优势植物小叶樟(Deyeuxiaangustifolia)和毛果苔草(Carexlasiocarpa)枯落物为例,探讨了N素在枯落物中的季节变化、含量特征以及对维持生态系统物质平衡的作用．结果表明,枯落物N含量随气温升高和地上生物量增大而减少;枯落物失重率随时间延长而增大;小叶樟年累积失重率为32．2％,毛果苔草为27．7％;小叶樟群落N素年累积输入量为1478mg     

三江平原典型小叶章湿地土壤氮素净矿化与硝化作用

2004年6月—2005年7月,利用PVC顶盖原位培育法研究了三江平原典型草甸小叶章湿地和沼泽化草甸小叶章湿地土壤(0~15cm)无机氮库、净矿化/硝化速率动态、影响因素及年净矿化/硝化量.结果表明:两种湿地土壤的无机氮均呈明显的动态变化特征,其NH4 -N、NO3-N含量均表现为典型草甸小叶章湿地>沼泽化草甸小叶章湿地.两种湿地土壤的净矿化/硝化速率均呈明显的波动变化,生物固持作用、反硝化作用以及雨季较多降水是导致净矿化/硝化速率出现负值的主要原因.温度、降水、土壤有机质含量、C/N和pH是引起二者土壤无机氮库、净矿化/硝化速率存在明显差异的重要原因.典型草甸小叶章湿地的年净矿化量(19.41kg·hm-2)、年净硝化量(4.27kg·hm-2)以及净硝化量占净矿化量的百分比(22.00%)明显高于沼泽化草甸小叶章湿地(5.51kg·hm-2、0.28kg·hm-2和5.08%),说明前者的氮有效性以及维持可利用氮的能力明显高于后者.     

三江平原湿地小叶章生产力模拟模型

利用气象台站的常规观测资料,依据植物生长模拟理论,以d为步长,建立了湿地小叶章(Deyeuxia angustifolia)植被生产力动态模拟模型。该模型包括3个子模块:1)光合作用与呼吸作用;2)干物质积累;3)同化物分配,主要考虑了温度和积水因子对植物生长的影响。并利用实测资料对该模型进行了检验,结果表明:小叶章地上活体、枯落物、茎、叶各器官枯落物的模拟值与实测值之间均呈极显著的线性相关(R²分别为0.98、0.99、0.99和0.92)。在相邻区域的检验结果也表明,季节性积水沼泽化草甸小叶章的地上生物量明显高于常年积水沼泽。两类湿地小叶章地上生物量的模拟值与实测值之间均呈极显著线性相关(R²分别为0.66和0.79)。相近区域长期定位观测点连续2年的模拟结果与实测值之间也具有极显著的线性相关(R²分别为0.97和0.76)。     

河口湿地植物活体-枯落物-土壤的碳氮磷生态化学计量特征

碳(C)、氮(N)、磷(P)生态化学计量比是生态系统过程及其功能的重要特征.以闽江河口的芦苇(Phragmites australis)和短叶茳芏(Cyperus malaccensis var.brevifolius)湿地为对象,开展植物活体-枯落物-土壤系统的C、N、P季节动态研究.结果表明:芦苇和短叶茳芏植物活体、枯落物和土壤年均C、N、P含量为C＞N＞P,两种湿地系统C、N含量均为植物活体和枯落物高于土壤,但与土壤P含量大小关系因植物构件差异而不同;芦苇和短叶茳芏植物活体、枯落物和土壤的C、N、P生态化学计量比表现为C∶P＞C∶N＞N∶P;芦苇湿地C∶N为枯落物＞植物活体＞土壤,短叶茳芏为植物活体＞枯落物＞土壤,而C∶P和N∶P均为枯落物＞植物活体＞土壤;C、N、P化学计量比可以反映湿地C、N、P交换过程和植物群落的生态功能.     

三江平原典型湿地及其开垦后土壤中总硫变化的初步研究

以三江平原3种主要沼泽类型--小叶章(Calamagrostis angustifolia)沼泽、乌拉苔草(Carex meyeriana)沼泽、毛果苔草(Carex lasiocarpa)沼泽以及不同开垦年限的耕地为研究对象,对其土壤中总硫含量进行分析,3种沼泽中总硫量的顺序为小叶章沼泽(622．4mg·kg^-1)<乌拉苔草沼泽(820．5mg·kg^-1)、毛果苔草沼泽(1022．4mg·kg^-1),挠力河、鸭绿河、别拉洪河及浓江流域土壤中总硫量的顺序为挠力河(925．0mg·kg^-1)>鸭绿河(841．8mg·kg^-1)>浓江(636．5mg·kg^-1)>别拉洪河(520．8mg·kg^-1)沼泽湿地及耕地土壤总硫量在层次上具有明显的规律性,即由表土层向下,含量逐渐降低,1980～2000年开垦的耕地土壤中总硫含量平均值为180．5mg·kg^-1,而未开垦湿地中的总硫含量平均值为735．8mg·kg^-1。耕地中的总硫量显著低于湿地中的总硫量,并且开垦年限越长,土壤中的总硫量越低,表明湿地开垦导致土壤总硫明显流失。     

模拟氮沉降对湿地植物生物量与土壤活性碳库的影响

在两种水分条件下(W₁:非淹水,W₂:淹水)分4个氮处理(分别相当于氮沉降率0、1、3、5 g N·m^-2·a^-1)模拟了三江平原典型湿地植物湿草甸小叶章(Deyeuxia angustifolia)植株及土壤活性碳库对氮沉降的响应.结果表明：模拟氮沉降下小叶章的生物量(总生物量、地上生物量、根生物量)均高于对照,其中根生物量的增长程度最大;根中碳含量及分配比例均显著提高,而地上部位的碳含量则显著降低(P<0.05).氮沉降对土壤活性碳库具有显著影响,各活性碳库含量均以5 g N·m^-2·a^-1处理最高,氮沉降对各活性碳库的影响程度依次为CHC(碳水化合物碳)＞LBC(易氧化有机碳)＞DOC(水溶性有机碳)＞MBC(微生物量碳),氮沉降与淹水条件的耦合作用有利于活性碳的释放;回归分析表明,土壤活性碳库与小叶章相关参数间存在显著相关性.氮沉降显著提高了小叶章植株生物量及土壤的活性碳含量.     

Biogeochemical cycle of Sulfer in the Calamagrostis angustifolia wetland ecosystem in the Sanjiang Plain, China

To better understand the Sulfur (S) cycle in the wetland ecosystem, the S cycle and its compartmental distribution within an atmosphere-plant-soil system were studied using a compartment model in the Calamagrostis angustifolia wetland in the Sanjiang Plain, Northeast China. The results showed that the soil was the main S storage and flux hinge in which 97.78% S was accumulated. In the plant subsystem, the root was the main S storage, and it remained at 79.60% of the total S contents, which in the Calamagrostis angustifolia wetland ecosystem showed that the parts above the ground took up 0.75 g S/m², the S re-transferring biomass to the root was 0.24 g S/m², and to the litter was 0.51 g S/m²; the root took up 3.76 g S/m² and the S transferring biomass to the soil took up 3.07 g S/m²; the litter S biomass was 0.75 g S/(m²·a) and the S transferring biomass to the soil was more than 0.52 g S/(m²·a). The emission amount of H2S from the Calamagrostis angustifolia wetland ecosystem to the atmosphere was 1.42 mg S/m², whereas carbonyl sulfide (COS) was absorbed by the Calamagrostis angustifolia wetland from the atmosphere and the absorption amount was 1.83 mg S/m². The S input biomass from the rain to the ecosystem was 4.85mg S/m² during the growing season. The difference between input and output amounts was 5.26 mg S/m², which indicated that S was accumulated in the ecosystem and would lead to wetland acidification in the future.     

Biogeochemical cycle of Sulfer in the Calamagrostis angustifolia wetland ecosystem in the Sanjiang Plain, China

To better understand the Sulfur (S) cycle in the wetland ecosystem, the S cycle and its compartmental distribution within an atmosphere-plant-soil system were studied using a compartment model in the Calamagrostis angustifolia wetland in the Sanjiang Plain, Northeast China. The results showed that the soil was the main S storage and flux hinge in which 97.78% S was accumulated. In the plant subsystem, the root was the main S storage, and it remained at 79.60% of the total S contents, which in the Calamagrostis angustifolia wetland ecosystem showed that the parts above the ground took up 0.75 g S/m², the S re-transferring biomass to the root was 0.24 g S/m², and to the litter was 0.51 g S/m²; the root took up 3.76 g S/m² and the S transferring biomass to the soil took up 3.07 g S/m²; the litter S biomass was 0.75 g S/(m²·a) and the S transferring biomass to the soil was more than 0.52 g S/(m²·a). The emission amount of H2S from the Calamagrostis angustifolia wetland ecosystem to the atmosphere was 1.42 mg S/m², whereas carbonyl sulfide (COS) was absorbed by the Calamagrostis angustifolia wetland from the atmosphere and the absorption amount was 1.83 mg S/m². The S input biomass from the rain to the ecosystem was 4.85mg S/m² during the growing season. The difference between input and output amounts was 5.26 mg S/m², which indicated that S was accumulated in the ecosystem and would lead to wetland acidification in the future.     

三江平原4种典型湿地土壤碳氮分布差异和微生物特征

选择三江平原洪河湿地保护区4种典型湿地类型：小叶章+沼柳湿地、小叶章湿地、毛苔草湿地和芦苇湿地作为研究对象,分析了不同湿地土壤有机碳(SOC)、全氮(TN)含量和微生物活性指标(土壤蔗糖酶、纤维素酶、过氧化氢酶、微生物生物量碳MBC、微生物生物量氮MBN、微生物呼吸速率MBR、微生物商q_MB和代谢商q CO₂)的变化及其相互关系.结果表明： SOC和TN含量均随土层深度增加而减少,不同湿地类型之间具有极显著性差异(P<0.01).各湿地土壤酶活性(除过氧化氢酶)、MBC、MBN含量和MBR均以表层(0～10 cm)最高,并随着土层深度的增加而降低.在0～30 cm土层内,小叶章+沼柳湿地和小叶章湿地SOC、TN含量、土壤酶活性、MBC、MBN含量、MBR、q_MB和qCO₂均高于淹水区的毛苔草湿地和芦苇湿地.统计分析表明,SOC、TN与微生物活性指标(qCO₂除外)均存在极显著正相关关系(P<0.01).表明研究区土壤微生物特征对SOC、TN的变化具有重要的影响和指示作用.     

三江平原湿地小叶章群落磷素积累动态与生物量动态分析

采用野外定位观测结合室内分析的方法,对三江平原典型小叶章湿地两种类型小叶章生长季磷的积累及植物生物量的季节动态进行研究,以揭示三江平原湿地中磷在植物中积累的季节动态变化及其与植物生物量积累之间的关系,进一步认识磷在湿地系统中通过植物吸收迁移转化的机制。结果表明,两种小叶章群落地上、地下生物量以及植物体磷储量有明显的季节动态变化,但二者季节变化特征不同。此外,植物体地上、地下部分磷素积累量和生物量在整个植物体所占的比重两种类型也存在一定差异,这与植物所处的生境及其生态适应有一定关系。分析两种小叶章群落的生长速率(AGR)以及磷素的积累速率(Vp),表明在生长初期,磷是植物生长的重要营养元素。两种小叶章的AGR、Vp的变化曲线相似,说明对于这两种小叶章群落,生境不是磷积累速率的主要影响因素。     

Assessing the potential for cadmium phytoremediation with Calamagrostis epigejos: a pot experiment

A pot experiment was conducted for three vegetation periods on a sandy soil (pH 7.5) to study the uptake and distribution of Cd in plant tissues of Calamagrostis epigejos (L.) Roth. Cadmium was applied as CdCl2 (a total of 11 solution of 0, 20. 100, and 200 mg Cd l(-1)). HNO3- and water-extractable concentrations of Cd in 2- and 20-cm soil depths were correlated with the applied Cd showing that Cd was very mobile in the soil. The uptake of Cd from soil by Calamagrostis epigejos was directly related to the total soil Cd content and to the water-soluble pool of Cd. The concentrations of Cd in plant tissues (roots, rhizomes, leaves) and litter increased with increased applied Cd. Most of the Cd that was taken up was accumulated in roots (range from 1.88+/-0.42 to 40.96+/-16.71 mg kg(-1) dry mass), followed by rhizomes (0.52+/-0.13 to 25.70+/-6.35 mg kg(-1)) and leaves (0.30+/-0.06 to 9.20+/-1.93 mg kg(-1)). Cd concentrations of the litter were about twofold greater than the concentrations in the leaves (0.67+/-0.07 to 18.98+/-7.00 mg kg(-1)). The bioaccumulation factor (leaf/soil concentration ratio) increased significantly from 0.70+/-0.10 (control) to 1.1+/-0.17 (100 mg Cd l(-1)), but decreased again at the highest Cd level (200 mg Cd l(-1)) toward 0.74+/-0.34, which was not significantly different from the control. The low transfer of Cd from soil to above-ground organs at higher soil Cd concentrations indicates an exclusion mechanism. The leaf/root Cd concentration ratio (translocation factor) shows no significant relationship to increasing soil contamination. Only 4-7% of the total plant Cd was accumulated in the above-ground tissues. The phytoextraction potential (total Cd removed from soil) within three growing seasons ranged from 0.11 to 0.25% of the total soil Cd. Total output in above-ground living and dead plant material of C. epigejos would be approximately 20 g ha(-1) a(-1) for the lowest contamination level (+20 mg Cd per pot) and approximately 275 g ha(-1) a(-1) for the highest contamination level (+200 mg Cd per pot). This is within the range where an application for phytoextraction of Cd has been suggested by other authors. However, we conclude that the practical use of C. epigejos for phytoremediation is not mainly in the field of phytoextraction, but phytostabilization. C. epigejos has the capability to structurally stabilize the soil and reduce Cd contamination spread due to erosion. The uptake of the available Cd pool and accumulation in below-ground biomass may further prevent leaching into ground water.     

Early-stage litter decomposition and its influencing factors in the wetland of the Sanjiang Plain, China

Using the litter bag technique, the decomposition rates and their influencing factors were studied by investigating three wetland macrophytes, Calamagrostics angustifolia, Carex meyeriana and Carex lasiocapa, in Sanjiang Plain, Northeast China. It was revealed that C. lasiocapa lost 28.91% of its weight, C. angustifolia lost 31.98% and C. meyeriana lost 32.99% after 164 days. Another finding was that the amount of organic carbon in the litter of C. angustifolia and C. lasiocapa fluctuated, but continuously decreased in that of C. meyeriana. However, all the three types of litter released organic carbon. Nitrogen was released substantially from the litter of both C. angustifolia and C. meyeriana, but accumulated in the litter of C. lasiocapa. Phosphorus concentrations in all the three types of litter apparently decreased first and then slightly increased. Overall, P release was observed in all the three types of litter. The C/N and C/P ratios varied significantly in the decomposition process. The decomposition rates and nutrient content variations were simultaneously influenced by the quality of the litter as well as the environmental factors in the Sanjian Plain, but they were more strongly affected by the quality of the litter.