水电梯级开发对河流生境质量及纵向连通性影响评价——以五布河和藻渡河为例

河流物理生境是维持河流生物多样性及生态功能的关键因素。生境质量的好坏能反应河流健康的程度。以我国西南地区的五布河和藻渡河为例,采用河流生境调查方法(RHS)和树状水系连通性指数(DCI)定量评估水电梯级开发和水坝建设对河流物理生境质量和河流纵向连通性的影响。结果表明,水电梯级开发后,五布河干流未受水坝明显影响河段、库区河段、减水河段分别为20.48、43.34、18.09 km,占总长度的25.0%、52.9%、22.1%。藻渡河干流河口至双河口段未受水坝明显影响河段、库区河段、减水河段分别为58.61、8.28、18.99 km,占总长度的68.2%、9.6%、占22.1%。水电梯级开发后,五布河干流河流片段由26个增至29个,藻渡河干流河流片段由2个增至5个。两条河流纵向连通性分别降低了7.8%和38.0%。五布河坝下减水河段生境质量降低14.1%,库区河段生境质量变化不明显。藻渡河减水河段生境质量与近自然河段无显著差异;两座坝后式电站库区河段生境质量明显低于近自然河段。水电梯级开发对两条河流物理生境的影响与水坝位置选择、建坝前的自然阻隔数量与分布、河流地貌特征、水电资源开发方式等密切相关。     

城市公园绿地对周边环境空气PM10和PM2.5的影响及效应场特征——以武汉市中山公园为例

选取武汉市中山公园及其周边建成环境作为研究对象,采用LUR模型、小尺度指标测试与空间插值相结合的技术方法,分析春、夏、秋、冬公园绿地周边建成环境空气PM10、PM2.5浓度时空效应场特征,旨在为公园绿地周边建成环境的规划与建设提供科学依据.结果表明:城市公园绿地周边建成环境500 m缓冲区范围对空气PM10、PM2.5...     

通量梯度法在温室气体及同位素通量观测研究中的应用与展望

通量梯度法与涡度相关法均是微气象学的物质和能量通量观测方法, 在没有高频气体分析仪或下垫面风浪区较小的情况下, 通量梯度法可以有效观测生态系统(或土壤)与大气之间的温室气体及其同位素通量, 同时也可以作为涡度相关法的配套观测和有益补充。该文回顾了通量梯度法的基本原理、概念和假设, 重点综述了温室气体浓度梯度以及相关湍流扩散系数的观测与计算的方法和理论, 概述了通量梯度法在森林、农田、草地、湿地和水体等生态系统观测温室气体通量的应用进展, 特别是在稳定同位素通量观测中的应用, 最后从影响温室气体和同位素的浓度梯度以及湍流扩散系数测定与计算等方面概述了应用注意事项及建议。     

鼎湖山针阔叶混交林地表温室气体排放的日变化

利用静态箱 -气相色谱法对鼎湖山针阔叶混交林地表 3种温室气体 CO2 、CH4 、N2 O通量进行了原位观测 .结果表明 ,鼎湖山针阔叶混交林地表为 CO2 、N2 O的排放源 ,为 CH4 的弱汇 ,通量日变幅分别是 4 88.99～ 70 0 .5 7,0 .0 4 9～ 0 .10 8mg/ (m2· h)和- 0 .0 2 5～ - 0 .0 5 3mg/ (m2 · h) ;地表凋落物分解释放 CO2 约占总排放的 1/ 3;凋落物层和林下灌木对 CH4 和 N2 O的通量无明显影响 ;CO2 、N2 O的 9∶ 0 0观测值与其日平均值有明显差异     

Effects of seasonality,transport pathway,and spatial structure on greenhouse gas fluxes in a restored wetland

Wetlands can influence global climate via greenhouse gas (GHG) exchange of carbon dioxide (CO₂), methane (CH₄), and nitrous oxide (N₂O). Few studies have quantified the full GHG budget of wetlands due to the high spatial and temporal variability of fluxes. We report annual open‐water diffusion and ebullition fluxes of CO₂, CH₄, and N₂O from a restored emergent marsh ecosystem. We combined these data with concurrent eddy‐covariance measurements of whole‐ecosystem CO₂ and CH₄ exchange to estimate GHG fluxes and associated radiative forcing effects for the whole wetland, and separately for open‐water and vegetated cover types. Annual open‐water CO₂, CH₄, and N₂O emissions were 915 ± 95 g C‐CO₂ m^?2 yr^?1, 2.9 ± 0.5 g C‐CH₄ m^?2 yr^?1, and 62 ± 17 mg N‐N₂O m^?2 yr^?1, respectively. Diffusion dominated open‐water GHG transport, accounting for >99% of CO₂ and N₂O emissions, and ~71% of CH₄ emissions. Seasonality was minor for CO₂ emissions, whereas CH₄ and N₂O fluxes displayed strong and asynchronous seasonal dynamics. Notably, the overall radiative forcing of open‐water fluxes (3.5 ± 0.3 kg CO₂‐eq m^?2 yr^?1) exceeded that of vegetated zones (1.4 ± 0.4 kg CO₂‐eq m^?2 yr^?1) due to high ecosystem respiration. After scaling results to the entire wetland using object‐based cover classification of remote sensing imagery, net uptake of CO₂ (?1.4 ± 0.6 kt CO₂‐eq yr^?1) did not offset CH₄ emission (3.7 ± 0.03 kt CO₂‐eq yr^?1), producing an overall positive radiative forcing effect of 2.4 ± 0.3 kt CO₂‐eq yr^?1. These results demonstrate clear effects of seasonality, spatial structure, and transport pathway on the magnitude and composition of wetland GHG emissions, and the efficacy of multiscale flux measurement to overcome challenges of wetland heterogeneity.     

Effects of nitrogen deposition on the greenhouse gas fluxes from forest soils

Nitrogen (N) deposition can alter the rates of microbial N- and C- turnover, and thus can affect the fluxes of greenhouse gases (GHG, e.g., CO₂, CH₄, and N₂O) from forest soils. The effects of N deposition on the GHG fluxes from forest soils were reviewed in this paper. N deposition to forest soils have shown variable effects on the soil GHG fluxes from forest, including increases, decreases or unchanged rates depending on forest type, N status of the soil, and the rate and type of atmospheric N deposition. In forest ecosystems where biological processes are limited by N supply, N additions either stimulate soil respiration or have no significant effect, whereas in “N saturated” forest ecosystems, N additions decrease CO₂ emission, reduce CH₄ oxidation and elevate N₂O flux from the soil. The mechanisms and research methods about the effects of N deposition on GHG fluxes from forest soils were also reviewed in this paper. Finally, the present and future research needs about the effects of N deposition on the GHG fluxes from forest soils were discussed.     

沙埋对干旱沙区生物结皮覆盖土壤温室气体通量的影响

以腾格里沙漠东南缘自然植被区生长的两种典型生物结皮——藓类和藻类-地衣混生结皮覆盖土壤为对象,通过设置0(对照)、1 mm(浅层)和10 mm(深层)沙埋处理,研究了沙埋对该区结皮覆盖土壤温室气体通量的影响,并通过测定沙埋后土壤温度、水分的变化,初步探讨了沙埋影响生物结皮覆盖土壤温室气体通量的环境机制.结果表明: 沙埋显著增加了两类结皮覆盖土壤的CO₂释放通量和CH₄吸收通量(P<0.05);但对N₂O通量的影响因沙埋厚度和结皮类型的不同而异:深层沙埋(10 mm)显著增加了两类结皮覆盖土壤的N₂O吸收通量,浅层沙埋(1 mm)仅显著降低了藓类结皮覆盖土壤的N₂O吸收通量,而对混生结皮覆盖土壤的N₂O通量影响不显著.沙埋显著增加了两类结皮覆盖土壤的表层温度和0~5 cm深土壤湿度,从而增加了其CO₂释放通量.但是沙埋引起的土壤温湿度的变化与CH₄和N₂O通量变化的相关性不显著,说明沙埋引起的土壤温湿度变化不是影响其CH₄和N₂O通量的关键因子.     

不同氮肥对东北春玉米农田温室气体周年排放的影响

为探明不同氮肥条件下高纬度农田土壤的温室气体排放特性,采用静态箱-气相色谱法研究了常规施氮(CN)、施用缓释肥(SLN)、尿素添加硝化抑制剂和脲酶抑制剂(NIUI)、不施氮肥(NN)对东北春玉米农田土壤温室气体排放的影响.结果表明: CN、SLN和NIUI处理产量分别为9618、9376和9645 kg·hm^-2.与CN处理相比,SLN促进了玉米生长季土壤N₂O的排放,降低了非生长季土壤N₂O的排放;NIUI处理N₂O累积排放量比CN降低了39.0%;各处理土壤CO₂周年累积排放通量无显著差异;东北春玉米田是大气中CH₄的弱汇,NIUI处理较CN促进了玉米生长季土壤对CH₄的吸收.综上,尿素添加脲酶抑制剂和硝化抑制剂可以在实现玉米高产的同时有效减少土壤温室气体排放.     

模拟盐度脉冲耦合潮汐过程对闽江河口湿地土壤含碳温室气体排放的影响

为了探究台风风暴潮导致的盐度脉冲、潮汐涨落以及两者的耦合作用对河口湿地土壤二氧化碳（CO₂）与甲烷（CH₄）排放产生的影响,选取闽江河口道庆洲短叶茳芏湿地土壤为研究对象,通过室内模拟实验,研究不同潮汐过程情景下由于盐度和潮水涨落变化,河口湿地CO₂与CH₄排放特征并分析其主要影响因子。研究结果表明：（1）潮汐淹水显著抑制CO₂排放,但促进CH₄排放（P<0.05）。盐度增加（0-8‰）促进了土壤CO₂排放（P>0.05）;0-2‰盐度促进土壤CH₄排放（P>0.05）,2‰-8‰盐度抑制土壤CH₄排放（P<0.05）。（2）盐度脉冲耦合潮汐过程显著抑制了CH₄排放（P<0.05）,且一定程度上抑制了CO₂排放（P>0.05）。（3） CO₂排放与孔隙水中的氨态氮（NH₄⁺-N）呈极显著正相关（P<0.01）,与硝态氮（NO₃^--N）、可溶性有机碳（DOC）和土壤pH呈显著负相关（P<0.05）。盐度脉冲耦合潮汐过程对CO₂与CH₄排放的影响是一个正负消长的博弈过程,在0-8‰的盐度内,潮汐淹水对CO₂排放的影响更大,而盐度在CH₄排放中起主导作用。相较于盐度,潮汐淹水是影响闽江河口湿地含碳温室气体全球增温潜势的主导因素。     

Enhanced CO2 uptake is marginally offset by altered fluxes of non-CO2 greenhouse gases in global forests and grasslands under N deposition

Despite the increasing impact of atmospheric nitrogen (N) deposition on terrestrial greenhouse gas (GHG) budget, through driving both the net atmospheric CO₂ exchange and the emission or uptake of non-CO₂ GHGs (CH₄ and N₂O), few studies have assessed the climatic impact of forests and grasslands under N deposition globally based on different bottom-up approaches. Here, we quantify the effects of N deposition on biomass C increment, soil organic C (SOC), CH₄ and N₂O fluxes and, ultimately, the net ecosystem GHG balance of forests and grasslands using a global comprehensive dataset. We showed that N addition significantly increased plant C uptake (net primary production) in forests and grasslands, to a larger extent for the aboveground C (aboveground net primary production), whereas it only caused a small or insignificant enhancement of SOC pool in both upland systems. Nitrogen addition had no significant effect on soil heterotrophic respiration (R_H) in both forests and grasslands, while a significant N-induced increase in soil CO₂ fluxes (R_S, soil respiration) was observed in grasslands. Nitrogen addition significantly stimulated soil N₂O fluxes in forests (76%), to a larger extent in grasslands (87%), but showed a consistent trend to decrease soil uptake of CH₄, suggesting a declined sink capacity of forests and grasslands for atmospheric CH₄ under N enrichment. Overall, the net GHG balance estimated by the net ecosystem production-based method (forest, 1.28 Pg CO₂-eq year⁻¹ vs. grassland, 0.58 Pg CO₂-eq year⁻¹) was greater than those estimated using the SOC-based method (forest, 0.32 Pg CO₂-eq year⁻¹ vs. grassland, 0.18 Pg CO₂-eq year⁻¹) caused by N addition. Our findings revealed that the enhanced soil C sequestration by N addition in global forests and grasslands could be only marginally offset (1.5%–4.8%) by the combined effects of its stimulation of N₂O emissions together with the reduced soil uptake of CH₄.     

中国氮磷钾肥制造温室气体排放系数的估算

通过收集、整合国内相关数据,推算了符合中国目前情况的各种氮肥、磷肥和钾肥的制造过程中的温室气体排放系数(从原料到工厂大门)。结果显示,我国平均水平的氮肥制造碳排放系数为:合成氨(液氨)1.672 t CE/t N,尿素2.041 t CE/t N,碳铵1.928 t CE/t N,硝酸铵4.202 t CE/t N,氯化铵2.220 t CE/t N,氮肥综合系数为2.116 t CE/t N。我国一般水平的磷肥制造碳排放系数为:重钙0.467 t CE/t P2O5,磷酸二铵1.109 t CE/t P2O5,磷酸一铵0.740 t CE/t P2O5,普钙0.195 t CE/t P2O5,钙镁磷肥2.105 t CE/t P2O5,磷肥综合系数为0.636 t CE/t P2O5。我国先进水平的钾肥制造碳排放系数为:氯化钾0.168 t CE/t K2O,硫酸钾0.409 t CE/t K2O(其中罗钾法硫酸钾0.443 t CE/t K2O、曼海姆法硫酸钾0.375 t CE/t K2O),钾肥综合系数为0.180 t CE/t K2O。我国大部分氮磷钾肥的温室气体排放系数普遍为欧美平均水平的2倍左右,因此利用国外系数来估算我国的农业温室气体排放量将严重低估化肥施用的影响。     

Effects of biochar application on soil greenhouse gas fluxes: a meta‐analysis

Biochar application to soils may increase carbon (C) sequestration due to the inputs of recalcitrant organic C. However, the effects of biochar application on the soil greenhouse gas (GHG) fluxes appear variable among many case studies; therefore, the efficacy of biochar as a carbon sequestration agent for climate change mitigation remains uncertain. We performed a meta‐analysis of 91 published papers with 552 paired comparisons to obtain a central tendency of three main GHG fluxes (i.e., CO₂, CH₄, and N₂O) in response to biochar application. Our results showed that biochar application significantly increased soil CO₂ fluxes by 22.14%, but decreased N₂O fluxes by 30.92% and did not affect CH₄ fluxes. As a consequence, biochar application may significantly contribute to an increased global warming potential (GWP) of total soil GHG fluxes due to the large stimulation of CO₂ fluxes. However, soil CO₂ fluxes were suppressed when biochar was added to fertilized soils, indicating that biochar application is unlikely to stimulate CO₂ fluxes in the agriculture sector, in which N fertilizer inputs are common. Responses of soil GHG fluxes mainly varied with biochar feedstock source and soil texture and the pyrolysis temperature of biochar. Soil and biochar pH, biochar applied rate, and latitude also influence soil GHG fluxes, but to a more limited extent. Our findings provide a scientific basis for developing more rational strategies toward widespread adoption of biochar as a soil amendment for climate change mitigation.