温湿度和外源有机质对茶园土壤基础呼吸作用的影响

采用室内培养法研究了不同温度、水分和添加外源有机质对茶园土壤基础呼吸作用的影响。结果表明:土壤呼吸速率随着培养时间的变化而变化;温度对土壤呼吸的影响显著,在25℃条件下土壤呼吸碳积累量最大;水分对土壤呼吸速率的影响不显著,土壤水分为田间持水量的60%时,土壤呼吸碳积累量最大;添加外源有机质可以显著地增加土壤呼吸速率,且不同类型有机质对土壤呼吸速率的激发效应不同,土壤呼吸碳积累量表现为菜饼尿素腐熟猪粪茶树枯落物CK;土壤呼吸速率随着有机质添加量的增加而增大,且在一定范围内与有机质添加量呈显著的线性正相关。     

外源有机碳和温度对土壤有机碳分解的影响

研究凋落物等外源有机碳输入和温度变化对土壤有机碳分解的影响对我们深入理解森林土壤碳动态具有非常重要的意义。以亚热带天然次生林和杉木人工林土壤为研究对象,向土壤中添加13C标记的杉木凋落物和葡萄糖,研究不同温度下外源有机碳添加对原有土壤有机碳(SOC)分解的影响。结果显示:外源有机碳添加使原有SOC分解速率显著提高,表现出显著的正激发效应。葡萄糖引发的激发效应强度显著高于杉木凋落物,并且杉木人工林土壤的激发效应强度显著高于天然次生林。激发效应强度随着培养温度升高呈下降趋势。此外,由于外源有机碳的加入,SOC分解的温度敏感性显著降低。研究表明:凋落物输入及温度在亚热带森林SOC周转过程中发挥重要作用。     

添加^14C标记稻草对喀斯特典型土壤有机碳矿化的影响

为了研究有机物质对喀斯特地区典型土壤有机碳积累与转化的影响,采集两种喀斯特典型土壤（棕色石灰土、黑色石灰土）和一种对照土壤（红壤）的表层土壤（0～15cm）,设置不添加外源物质（CK）和添加14C标记的稻草（T1）的处理,进行为期100d的土壤培养试验及矿化试验。测定并分析了这3种典型土壤类型的微生物生物量碳（MBC）表观周转时间和田间周转时间、外源有机物质对土壤原有有机碳的激发效应以及CO2释放量。结果表明：MBC表观周转时间和田间周转时间依次分别为（71±2）d、（243±20）d、（254±45）d和0.29、1.0、1.04a。添加标记的14C有机物质后,土壤原有有机质的激发效应大小依次为红壤〉棕色石灰土〉黑色石灰土。在相同条件下,红壤不利于土壤有机质的累积,而棕色石灰土和黑色石灰土有利于土壤有机质的累积。     

秸秆还田下土壤有机质激发效应研究进展

土壤有机质是农田肥力的基础与核心，对作物产量、农业环境，甚至地球碳循环意义重大。作物秸秆作为农田土壤有机碳库的重要外部补充，其还田过程对土壤有机碳周转和碳库平衡具有显著影响。激发效应是一种因新鲜有机质输入而导致土壤本底有机质矿化速率发生改变的现象。秸秆还田导致的土壤有机质分解激发，不仅涉及到秸秆资源化高效利用，还直接关系到农田土壤碳库的平衡及其功能，因此备受科学界关注。尽管对外源有机质输入引起的土壤有机质激发效应的理论研究已取得了较大进展，但如何结合最新的理论结果到秸秆还田固碳减排的生产实践中仍面临着较大的挑战，这主要归结于对农田土壤有机质分解激发效应的发生特点和规律，及其背后的土壤、气候、管理等相关的驱动因子和过程还未完全明确。据此，本文首先对土壤有机质分解激发效应发生的理论研究进展（包括：共代谢理论、氮矿化理论、化学计量比和微生物残体再利用）进行了系统综述。其次，结合已有的研究证据和理论假设进一步概述了秸秆还田过程中影响激发强度和方向的潜在驱动因素，如：秸秆类型和数量、还田方式、水肥管理、土壤属性、气候因子等。最后，从秸秆还田的高效性、农田碳库的可持续和农业环境的友好性出发，对秸秆还田土壤有机质分解激发的潜在研究方向进行了展望，并就秸秆还田改善土壤碳库的优化措施提出了建议。     

易利用态有机物质对水稻土甲烷排放的激发作用

为探讨外源有机物质对淹水稻田土壤CH4排放的激发作用,对比不同外源有机物质对土壤CH4排放的贡献差别,本研究选取3种标记的易利用态有机物(葡萄糖、乙酸和草酸)分别加入水稻土,进行了为期1个月的培养。结果表明:培养30 d后不同处理CH4的累计排放量差异显著(P0.05),其中,乙酸葡萄糖草酸对照;双因素方差分析结果显示,外源有机物质的添加加速了土壤易利用态有机质的矿化(即产生正激发效应);不同处理条件下激发作用产生的CH4分别占各处理CH4总累计排放量的73.3%(葡萄糖处理)、71.5%(乙酸处理)和40.9%(草酸处理),且CH4排放量与CH4激发效应之间极显著正相关关系说明土壤CH4排放主要要来自于土壤原有机质的分解,外源有机物质可能主要对土壤微生物活性及代谢途径有影响。     

养分化学计量比对稻田土壤葡萄糖矿化及其激发效应的影响

选择13C-葡萄糖作为稻田土壤典型易利用态外源有机碳,通过室内培养试验,研究不同C/N/P/S计量比条件下,葡萄糖分解矿化的动态规律及其激发效应。结果表明,稻田土壤中葡萄糖-碳(C)快速矿化,60 d培养实验后,有65.5%~74.6%的葡萄糖-C矿化。养分元素的添加使土壤中葡萄糖-C快速转化碳库的比例逐渐由58%增加至65%,从而使葡萄糖-C矿化率提高了3.9%~12.5%,养分元素的添加量与葡萄糖-C快速转化碳库的比例和矿化率均表现出显著的正相关关系(R2=0.63,p0.05;R2=0.83,p0.05)。葡萄糖-C矿化过程中,导致稻田土壤碳的累积负激发效应为-370~-570 mg kg-1,养分元素添加比例越大,其负激发效应越强,二者呈显著的负相关性(R2=0.66,p0.05)。研究表明,稻田土壤中易利用态碳的矿化受C/N/P/S元素计量比的影响,高比例养分元素的添加,促进土壤中易利用态碳的矿化,抑制土壤原有有机质的分解,增强负激发效应。本研究可为深入了解稻田生态系统碳循环、实现农田土壤肥力提升和温室气体减排提供理论依据。     

针铁矿吸附态和包裹态有机碳在稻田土壤中的矿化及其激发效应

南方水稻土富含铁氧化物,土壤有机碳通过与铁氧化物结合的形式长期固存于土壤中;由于土壤中氧化铁和有机碳主要通过吸附、键和与包裹等形式存在,所以不同的碳铁复合物的稳定性存在一定的差异。尽管已有较多研究分析了土壤中有机碳与铁矿的结合与赋存形式,但是有机碳与铁矿间的结合方式对有机碳在水稻土中矿化及其激发效应的影响机制尚不明确。以葡萄糖为典型小分子外源有机碳,通过制备针铁矿吸附态葡萄糖和包裹态葡萄糖,采用室内模拟培养实验,研究了两种铁矿结合态葡萄糖在淹水水稻土中的矿化特征及其激发效应。结果表明：与单独添加葡萄糖处理相比,碳铁复合物的添加分别使CO2和13CO2释放量增加了0.39倍~0.53倍和0.87倍~1.07倍,却使CH4和13CH4释放量分别降低了0.44倍~0.59倍和0.25倍~0.44倍。相对于针铁矿吸附态葡萄糖,针铁矿包裹态葡萄糖显著抑制了CH4释放。而且,碳铁复合物的添加均在一定程度上促进了土壤原有有机碳矿化释放CO2,但抑制了来源于土壤原有有机碳的CH4释放。其中,针铁矿包裹态葡萄糖对来源于土壤原有有机碳的CH4释放量是针铁矿吸附态葡萄糖的1.33倍。针铁矿包裹态葡萄糖的快速矿化的碳库比例显著高于针铁矿吸附态葡萄糖,且其半衰期（T1/2）比针铁矿吸附态葡萄糖大10.85倍,其快库转化速率（k1）和慢库转化速率（k2）比铁矿吸附态葡萄糖的小10.74倍和19倍。其次,针铁矿包裹态葡萄糖对土壤有机质CO2累积激发效应表现为较弱的正激发(6.44 mg?kg-1),而对土壤有机质CH4累积激发效应则表现为负激发(-15.49 mg?kg-1),即针铁矿包裹态葡萄糖的添加抑制了土壤原有有机碳的矿化(-9.05 mg?kg-1),从而增强了土壤有机碳的固持潜力。因此,不同结构碳铁复合物的添加抑制了土壤原有有机碳的矿化,且针铁矿包裹态有机碳比针铁矿吸附态有机碳在水稻土中具有更强的稳定性和固碳效应。该研究结果也表明,水稻土中与铁氧化结合的小分子有机碳相对于游离态的有机碳,具有更强的生物稳定性,更低的矿化速率,而且能够抑制土壤有机碳的矿化,产生负激发效应,有利于增加土壤的长期固碳效应。     

外源碳输入对华北平原农田和湿地土壤有机碳矿化及其温度敏感性的影响

研究外源碳输入和气候变暖对土壤有机碳矿化的影响,对于深入理解土壤有机碳的稳定和积累机制以及其对全球变化的响应具有重要意义。通过为期35 d的室内培养试验,利用~(13)C稳定同位素标记技术,研究了华北平原典型农田和湿地土壤在15℃和25℃下的土壤有机碳矿化及激发效应。结果表明,土地利用类型(农田/湿地)、温度(15℃/25℃)和葡萄糖添加[0.4mg(C)·g~(-1)]对土壤有机碳矿化均具有显著影响。在相同培养温度下,未添加葡萄糖的农田和湿地土壤有机碳矿化无显著差异,而添加葡萄糖处理下农田土壤有机碳矿化显著高于湿地土壤。除湿地土壤在15℃下培养外,添加葡萄糖显著促进了农田和湿地土壤有机碳矿化,农田土壤有机碳矿化的激发效应显著高于湿地土壤。温度升高显著促进了农田和湿地土壤有机碳矿化,培养过程中土壤有机碳矿化温度敏感性Q10为1.2～1.6,土地利用类型和葡萄糖添加对土壤有机碳矿化温度敏感性的影响都不显著。在温度升高和外源碳输入的共同作用下,农田土壤有机碳矿化显著高于湿地土壤。     

氮磷添加对毛竹林土壤有机碳矿化及其激发效应的影响

摘 要：【目的】养分输入会显著影响土壤有机碳矿化,但毛竹林土壤有机碳激发效应对不同类型养分输入的响应及其机制尚不明确。【方法】选用尿素和磷酸二氢钠作为外源养分,通过80 d的培养试验,研究氮素、磷素及两者联合添加对毛竹林土壤有机碳矿化及其激发效应、微生物功能以及土壤理化性质的影响。【结果】氮素、磷素及两者联合添加均显著提高了土壤原有有机碳矿化累积CO2排放量（增幅分别为91.3%、19.2%和94.9%）,产生显著的正激发效应,其中氮素及其与磷素联合添加诱导的正激发效应强度显著大于磷素添加处理。上述三种养分添加处理均显著提高了土壤pH、活性有机碳库（微生物量碳、可溶性有机碳和烷氧碳组分）、碳降解酶（?-葡萄糖苷酶和蔗糖酶）活性以及cbhI和GH48功能基因丰度,但抑制了多酚氧化酶和RubisCO酶活性;另外,土壤无机氮含量（NH4+-N和NO3--N）在氮和氮磷添加下增加却在磷添加下降低。相关性分析表明,累积激发效应与土壤pH、活性有机碳库、无机氮含量、碳降解酶活性以及cbhI和GH48功能基因丰度呈显著正相关,而与多酚氧化酶和RubisCO酶活性显著负相关。【结论】氮磷养分添加可能是通过影响土壤pH、活性碳氮含量,并提升微生物的活性和功能,从而显著提高土壤原有有机碳的矿化速率。     

外加碳、氮对黄绵土有机质矿化与激发效应的影响

应用14C标记的葡萄糖和麦秸,15N标记的(NH4)2SO4和Ca(NO3)2对生黄绵土、菜园黄绵土土壤有机质的矿化与激发效应进行了研究。结果表明,外加有机质,特别是外加易分解的葡萄糖,和外加氮源,特别是外加(NH4)2SO4,对两种黄绵土土壤的有机质矿化与激发效应都有明显的促进作用,土壤有机质的矿化是高肥力菜园黄绵土高于低肥力生黄绵土,而有机质矿化的激发效应却是低肥力生黄绵土高于高肥力菜园黄绵土。外加有机质与外加N同时施入土壤时,外加N对外加有机质的矿化与激发效应同样有明显的促进作用,并发现外加有机质与外加N在促进土壤有机质矿化与激发效应过程中表现出正交互作用。激发效应对土壤肥力的更新和培养有积极作用。     

Evidence that stable C is as vulnerable to priming effect as is more labile C in soil

A significant fraction of soil organic carbon, named stable organic carbon (C) pool, has residence times longer than centuries and its vulnerability to land use or climatic changes is virtually unknown. Long-term bare fallows offer a unique opportunity to isolate the stable organic pool of soils and study its properties. We investigated the vulnerability of the stable organic C pool to fresh organic matter inputs by comparing the mineralization in a long-term bare fallow soil with that of an adjacent arable soil, containing stable C as well as more labile C. For this, we amended or not the soil samples with two different ¹³C-labelled fresh organic matter (straw or cellulose). In all cases we found a positive priming effect (i.e. an increased mineralization of soil organic carbon) when fresh organic matter was added. By comparing the results obtained on both soils, we estimated that half of the “primed” C in the arable soil due to straw addition as fresh organic matter, originated from the stable C pool. Our results suggest that under such conditions, which frequently occur, the stable pool of soil organic matter may largely contribute to soil extra-CO₂ emissions due to priming effect. Consequently, the C storage potential of this pool may be modified by changes in land use and/or biomass production that might change the priming of the mineralization of the stable pool of soil organic carbon.     

Negative priming effect on mineralization in a soil free of vegetation for 80 years

The priming effect (PE) is a complex process corresponding to a modification of mineralization rates of soil organic matter (SOM) following inputs of fresh organic matter (FOM). The priming effect can be either positive or negative (i.e. an acceleration or retardation of SOM decomposition) and is controlled by several factors such as microbial community composition, SOM chemical structure and nutrient availability. The first objective of our experiment was to study negative or positive PE of stabilized SOM. The second was to identify the role of FOM decomposers in the PE of stabilized SOM. We incubated, for 39 days, a fallow soil free of vegetation for 80 years amended with ¹³C‐cellulose and inoculated with a FOM‐decomposing community. The soil contained stabilized SOM. The PE of the stable organic matter was always negative and tended to be more negative when the FOM‐decomposing community was added. This suggests that for this particular soil, SOM mineralization was not limited by energy. Moreover, as the inoculation of a FOM‐decomposing community led to a more negative PE, we assume that the FOM‐decomposing community facilitated the access of FOM to the indigenous bare soil community.     

The priming effect of organic matter: a question of microbial competition?

It is generally accepted that the low quality of soil carbon limits the amount of energy available for soil microorganisms, and in turn the rate of soil carbon mineralization. The priming effect, i.e. the increase in soil organic matter (SOM) decomposition rate after fresh organic matter input to soil, is often supposed to result from a global increase in microbial activity due to the higher availability of energy released from the decomposition of fresh organic matter. Work to date, however, suggests that supply of available energy induces no effect on SOM mineralization. The mechanisms of the priming effect are much more complex than commonly believed. The objective of this review was to build a conceptual model of the priming effect based on the contradictory results available in the literature adopting the concept of nutritional competition. After fresh organic matter input to soils, many specialized microorganisms grow quickly and only decompose the fresh organic matter. We postulated that the priming effect results from the competition for energy and nutrient acquisition between the microorganisms specialized in the decomposition of fresh organic matter and those feeding on polymerised SOM.     

Model organic compounds differ in priming effects on alkalinity release in soils through carbon and nitrogen mineralisation

The influence of organic matter and its cycling on soil pH change is still unclear. This study investigated the effect of organic compounds on carbon and nitrogen dynamics and their relationship with pH changes in two soils differing in initial soil pH (Podosol of pH 4.5 and Tenosol of pH 6.2). Seven organic compounds representing common compounds in decomposing plant residues or root exudates were added to the soils and incubated for 60 d. The largest cumulative soil respiration occurred when glucose, malic acid and citric acid were added. In addition, the Tenosol had the greater respiration compared to the Podosol. The addition of organic acids (acetic, malic, citric, ferulic and benzoic acid) instantly decreased soil pH due to the dissociation of H⁺ from the acids. The pH of both soils was then restored over time, which was positively correlated with decomposition % of these compounds. The pH of the Tenosol amended with all the organic acids and of the Podosol with malic acid exceeded that of the control, and net alkalization occurred, with the degree of alkalization being greater with malic and citric acid. Adding organic acids to the Tenosol generally increased NH₄ concentrations but decreased NO₃ concentrations. The addition of glucose decreased pH in Podosol but slightly increased it in the Tenosol. The addition of glucosamine hydrochloride decreased pH due to significant nitrification. The results suggest that the addition of organic acids stimulates microbial NO₃ uptake, and ammonification and decomposition of indigenous soil organic matter, resulting in a priming effect on alkalinity release, and that the degree of the priming effect is influenced by the type of organic acid and initial soil pH.     

Nitrogen and phosphorus constrain labile and stable carbon turnover in lowland tropical forest soils

Tropical forests contain a large stock of soil carbon, but the factors that constrain its mineralization remain poorly understood. Microorganisms, when stimulated by the presence of new inputs of labile organic carbon, can mineralize (‘prime’) soil organic matter to acquire nutrients. We used stable carbon isotopes to assess how nutrient demand and soil properties constrain mineralization of added labile (sucrose) carbon and pre-existing (primed) soil carbon in tropical forest soils. In a series of lowland tropical forest soils from Panama, we found that the mineralization of fresh labile carbon was accelerated foremost by phosphorus addition, whereas the mineralization of pre-existing soil carbon was constrained foremost by nitrogen addition. However, there was variation in the relative importance of these nutrients in different soils and the largest effects on the acceleration of sucrose metabolism and constraint of priming occurred following the addition of nitrogen and phosphorus together. The respiration responses due to sucrose or primed soil carbon mineralization were reduced at pH below 4.8 and above 6.0. We conclude that in these tropical forest soils, phosphorus availability is more important in promoting microbial mineralization of sucrose carbon, whereas nitrogen availability is more important in constraining the priming of pre-existing soil organic carbon. This response likely arises because nitrogen is more closely coupled to organic matter cycling, whereas phosphorus is abundant in both organic and inorganic forms. These results suggest that the greatest impact of priming on soil carbon stocks will occur in moderately acidic tropical forest soils of low nitrogen availability. Given long-term changes in both atmospheric carbon dioxide and nitrogen deposition, the impact of priming effects on soil carbon in tropical forest soils may be partially constrained by the abundance of nitrogen.     

溶解性有机质对紫色土中锌形态分布的影响

溶解性有机质(Dissolved Organic Matter)作为有机质中生物活性和物理化学反应活性较为活跃的重要组成部分,对土壤中锌的形态分布有着重要影响,本文采用室内培养的方法,在相同的温度和湿度条件下,分析了两种不同来源的DOM在不同浓度梯度下对紫色土外源锌形态分布的影响,得出以下结论:(1)紫色土在添加DOM后,显著地促进了外源锌各形态之间的相互转化分布,酸性紫色土中DOM促进了外源锌由EX-Zn向其它形态转化,这对于减少土壤锌污染的植物毒性有一定的作用。石灰性紫色土中主要促进RES-Zn向其它形态转化,提高了锌对植物的有效性;(2)两种DOM对酸性紫色土的影响优于石灰性紫色土,影响效果DOM2>DOM1;(3)酸性紫色土形态间的相关关系程度显著,石灰性紫色土形态间的相关关系程度不显著。