共查询到20条相似文献，搜索用时 359 毫秒
1.
植物凋落物分解对土壤有机碳稳定性影响的研究进展 总被引：1，自引：0，他引：1
凋落物是植物向土壤输入有机碳的主要途径,源于凋落物的碳一部分以CO2的形式散失到大气,另一部分以有机碳的形式输入到土壤中,在土壤微生物的作用下经过一系列的周转参与稳定有机质的形成。但土壤作为“黑箱”,凋落物向土壤有机碳转移的过程和作用机理仍不明确。结合国内外该研究领域的主要成果,简要介绍了植物凋落物分解的研究方法、土壤有机碳组分及土壤有机碳稳定性,并从植物凋落物分解对土壤有机碳及其组分、土壤呼吸和激发效应、土壤微生物群落结构及酶活性的影响以及植物-土壤-微生物相互作用过程对有机碳稳定性的影响等方面进行概述,厘清植物凋落物分解与土壤稳定有机碳形成的关系,并提出了未来该领域亟待关注的研究方向和研究内容。 相似文献
2.
外源有机碳和温度对土壤有机碳分解的影响 总被引：5，自引：0，他引：5
《土壤通报》2015,(4):916-922
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。 相似文献
3.
4.
杉木人工林凋落物添加与去除对土壤碳氮及酶活性的影响 总被引：1，自引：0，他引：1
《土壤学报》2020,(4)
为了解未来气候变化过程中森林生产力增加的背景下,凋落物增加如何影响土壤碳氮过程,在杉木人工林中通过模拟实验研究凋落物添加(一倍)与去除对土壤中碳氮、碳氮同位素(δ~(13)C、δ~(15)N)、微生物生物量碳氮(MBC、MBN)及酶活性的影响。结果表明:凋落物添加后土壤中氮获得酶(β-N-乙酰氨基葡萄糖苷酶)活性显著上升,加速对土壤中有机质的分解获取氮素;凋落物添加与去除处理对土壤碳的影响较小,土壤有机碳(SOC)与可溶性有机碳(DOC)均未发生显著变化;土壤中δ~(13)C丰度与凋落物处理之间未呈现出相关规律性,而δ~(15)N丰度在凋落物添加处理后显著上升。这些结果说明,凋落物处理对杉木林土壤中氮的影响较为敏感,对土壤碳的影响较小。因此,未来气候变化导致森林生产力提高、凋落物输入增加,可能会导致土壤中氮素的损失,迫使土壤微生物分泌更多的氮获得酶同植物竞争土壤氮,最终可能会造成土壤碳氮循环的不平衡,对整个生态系统造成严重影响。 相似文献
5.
植被恢复对土壤团聚体分布及有机碳、全氮含量的影响 总被引：16，自引：0，他引：16
植被是影响土壤有机碳含量和土壤结构的重要因素,植被通过凋落物影响有机碳输入的数量和质量,同时有改善土壤结构特别是水稳性团聚体的数量。探讨黄土高原侵蚀地区植被恢复后对土壤有机碳、氮及其团聚体平均重量直径的影响,研究结果显示：土壤有机碳、全氮含量与水稳性团聚体平均重量直径的变化趋势相同,平均重量直径与有机C含量之间有二次多项式关系。植被类型是影响土壤碳、氮含量的关键因素,植被恢复增加土壤养分含量,改善土壤结构和土壤环境。 相似文献
6.
凋落物输入改变对慈竹林土壤有机碳的影响 总被引：2，自引：0，他引：2
通过野外试验,研究了凋落物输入改变对慈竹林土壤有机碳的影响。设置10%,50%和70%这3种去除凋落物量和分别添加15%,25%的绵竹、杉木凋落物处理及对照。结果发现,去除凋落后慈竹林土壤有机碳含量明显减少(p<0.05),而且去除量越大,有机碳含量减少越大。添加外源凋落物显著提高了慈竹林土壤有机碳含量(p<0.05),其中,15%的添加比例比25%更有利于土壤有机碳的积累,添加绵竹凋落物对土壤有机碳增加的效应高于添加杉木凋落物。研究表明,选择适合的树种和恰当的混交比例以及加强对凋落物层的保护,对维持慈竹林土壤有机碳具有重要的意义。 相似文献
7.
氮磷输入对湿地生态系统碳蓄积的影响 总被引：2，自引：0，他引：2
湿地生态系统在全球碳循环中有着举足轻重的作用。由于湿地垦殖、农业化施用等人类活动和全球变暖、大气氮沉降的增多等自然因素的综合作用,大量氮磷营养物质进入湿地,这必将对湿地生态系统碳蓄积产生影响。本文综述了外源氮磷输入对湿地土壤碳库、植被碳库和枯落物分解的影响以及湿地生态系统碳循环的模型研究,并对以后发展趋势进行了预测。 相似文献
8.
我国湿地碳循环的研究进展 总被引：4，自引：1，他引：3
湿地生态系统的碳循环正成为全球变化与陆地生态系统碳循环研究中的一大热点,在稳定全球气候变化中占有重要地位,其重要性主要表现在湿地土壤是陆地重要的有机碳库,土壤碳密度高,能够相对长期地储存碳,是多种温室气体的源和汇。目前湿地碳循环的研究主要集中在碳循环的影响因素方面,对我国湿地土壤有机碳储存的变化及其空间分布规律的特点研究较少。本文通过文献综述,研究我国不同气候区湿地土壤有机碳的储存变化及空间分布规律,对于了解湿地土壤有机碳的储存特点及其与陆地生态系统碳循环的关系,评价和保护湿地生态系统都具有重要的科学意义。 相似文献
9.
凋落物和根系输入对亚热带米槠天然林土壤有机碳组分的影响 总被引：3，自引：2，他引：1
植物残体添加和去除试验(the detritus input and removal treatments, DIRT)作为一种研究碳输入来源变化对土壤质地与质量影响的试验设计,对研究土壤养分来源以及主要影响机制具有关键作用。选择福建省三明森林生态系统与全球变化研究站的米槠常绿阔叶天然林,设置对照(CT)、去除凋落物(NL)、去除根系(NR)、去除凋落物+去除根系(NI)、添加双倍凋落物(DL)5种处理,于2018年12月对各处理不同土层(0-10,10-20 cm)土壤进行取样,研究其土壤有机碳组分及其影响因子。结果表明:(1)在0-10 cm土层中,DL中NH_4~+-N与TN含量明显高于其他处理。NR处理的NH_4~+-N与DON含量显著大于NL与NI处理。在10-20 cm土层中,DL处理在NH_4~+-N、NO_3~--N、DON以及TN含量显著大于其他处理。NI处理的NH_4~+-N含量显著低于其他处理。(2)DL处理有机碳含量显著高于NL处理,但DL处理土壤有机碳含量与CT处理无明显差异(P0.05),其余各处理间差异均不显著。(3)含有凋落物的处理土壤活性碳组分含量显著高于去除凋落物处理,活性碳组分含量顺序为DLCTNRNLNI。去除凋落物处理(NL)土壤惰性碳组分含量显著高于去除根系处理(NL、NI)。(4)凋落物和根系的输入对0-10 cm土层土壤β-葡萄糖苷酶以及纤维素水解酶活性具有显著影响,呈现与土壤活性碳组分相同的变化趋势。冗余分析表明,土壤有机碳组分的变化主要是受控于β-葡萄糖苷酶。pH以及土壤含水率也是影响土壤有机碳及其组分的关键因子。凋落物的输入有利于提高土壤养分有效性以及土壤质地,加快碳循环;植物根系则对土壤中有机碳的稳定性具有关键作用。 相似文献
10.
退化红壤马尾松恢复林地土壤微生物生物量变化及其控制因素研究 总被引：2，自引：0，他引：2
退化土壤植被恢复后土壤质量在凋落物参与下提高,但恢复土壤理化性质与土壤微生物生物量间的相互作用尚不清楚。本研究目标是调查退化红壤马尾松恢复林地凋落物清除对土壤理化性质和微生物生物量的影响,分析影响土壤微生物生物量的控制因素。研究结果表明,与侵蚀裸地相比,无论凋落物清除与否,马尾松恢复林地的土壤孔隙度、水稳性团聚体比例、土壤有机碳、全氮、土壤微生物生物量均有较大提高;其提高幅度受土层深度和坡位影响,主要表现为表层土壤大于亚表层土壤,坡顶和坡底土壤大于坡中土壤。与凋落物保留林地相比,凋落物清除林地土壤各项指标提高幅度降低。通径分析的结果表明,影响微生物生物量最重要的因素是土壤有机碳含量,其次为土壤孔隙度;凋落物则是通过孔隙度和有机碳来间接影响土壤微生物生物量。本研究说明土壤物理结构恢复对土壤生物学性质的恢复有重要意义。 相似文献
11.
Yiting He Yong Wang Yi Jiang Guoping Yin Shunping Cao Xiongsheng Liu Renjie Wang Zijian Wu Fengfan Chen 《Soil Use and Management》2023,39(1):92-103
Leaf litter decomposition transfers elements from litter to soils that are essential for regulating nutrient cycles in plantation ecosystems, especially carbon and nitrogen. However, soil carbon and nitrogen dynamics in response to tree litter management remains insufficiently researched. We conducted a one-year field experiment at a fast-growing sweetgum tree plantation to evaluate the effects of leaf litter management on soil available nutrients, respiration rate and nitrogen mineralization rate. Three leaf litter treatments were applied, which were: (1) natural input (control); (2) double input and (3) non-input. It was found that the double input treatment increased soil inorganic nitrogen and microbial biomass nitrogen, but had little effect on microbial biomass carbon, dissolved organic carbon or dissolved organic nitrogen compared with natural input. The non-input treatment caused dissolved organic carbon to decrease compared with natural input. The respiration rate increased in the double input treatment, with a positive priming effect observed. Soil net ammonification, nitrification and mineralization rates also increased in the double input treatment in specific seasons. Meanwhile, positive linear relationships between respiration rate and all nitrogen transformation rates were observed for all treatments. Soil temperature was found to be an important prediction factor for predicting the respiration rate and mineralization as seasonal variations, but not for litter-induced fluctuations. Soil water content and mineral nitrogen were the primary drivers of litter-induced change to the respiration rate, whereas mineral nitrogen and microbial biomass were primary drivers of mineralization change. These results suggest that changes in soil nitrogen mineralization rate are strongly associated with the soil respiratory process, resulting in a potentially strong plant–soil feedback mechanism. 相似文献
12.
Climate and litter quality have been identified as major drivers of litter decomposition, but our knowledge of how soil characteristics (e.g. microbial community and chemical properties) determine carbon (C) and nitrogen (N) availability derived from the decomposition of litter of different qualities is still scarce. We conducted a microcosm experiment to evaluate how soils with contrasting microbial communities and soil properties (denoted Soils A and B hereafter, where Soil B has higher bacterial and fungal abundance, fungal:bacterial ratio, and organic C than Soil A) determine the availability of soil C (carbohydrates, proteins, amino acids and phenols) and N (dissolved organic and inorganic N, microbial biomass N and available N) during the decomposition of litter of contrasting quality (C:N ratios ranging from 20 to 102). We also evaluated the relative importance of soil characteristics and litter quality as drivers of C and N inputs to the soil during this process. Overall, higher soil C and N availability after litter decomposition was found in Soil B than in Soil A. Soil characteristics had a higher positive effect on soil C and N contents than litter quality during litter decomposition. We also found that changes in N availability and organic matter quality registered after litter decomposition, linked to different soil characteristics, were able to promote dissimilarities in the potential mineralization rates. In conclusion, our study provides evidence that soil characteristics (e.g. microbial communities and chemical properties) can be more important than litter quality in determining soil C and equally important for N availability during the decomposition of leaf litter. 相似文献
13.
Yolima Carrillo Becky A. Ball Michael S. Strickland Mark A. Bradford 《Pedobiologia》2012,55(4):185-192
There is increasing awareness of the importance of ecological legacies in contemporary ecosystem processes. Decomposition is regulated by a set of interacting hierarchically organized factors. As spatial and temporal scales decrease, decomposition is largely dependent on the quality of resources and the decomposer community, but whether and how these factors manifest via historical legacy effects is not well understood. We tested whether the history of plant litter inputs had short-term legacy effects on contemporary litter and soil organic matter carbon (C) and nitrogen (N) mineralization. Using a field/laboratory microcosm approach, we exposed soils to two litters of contrasting chemistry and, after adding fresh substrates, we monitored C and N dynamics. In a parallel experiment, we manipulated the soil community to reduce litter-history impacts on its composition and size to investigate whether the soil community could be an important contributor to legacy effects We found strong short-term litter legacy effects on contemporary litter and soil N mineralization, the duration of which was dependent on the contemporary substrate for decomposition. These strong effects were not consistent with the home field advantage phenomenon, as exposure to a specific litter did not favor the decomposition of the same litter when it was applied as a contemporary substrate. Reduction of the litter-history effects on soil biota decreased the impact of litter history on N immobilization, suggesting that plant litter impacts on the soil community may be an important component of plant litter legacies on N decomposition. In contrast to N, litter legacies appeared to be much less important for C decomposition, suggesting that legacy effects might uncouple contemporary C and N dynamics. 相似文献
14.
Increasing plant species richness generally enhances plant biomass production, which may enhance accumulation of carbon (C) in soil. However, the net change in soil C also depends on the effect of plant diversity on C loss through decomposition of organic matter. Plant diversity can affect organic matter decomposition via changes in litter species diversity and composition, and via alteration of abiotic and/or biotic attributes of the soil (soil legacy effect). Previous studies examined the two effects on decomposition rates separately, and do therefore not elucidate the relative importance of the two effects, and their potential interaction. Here we separated the effects of litter mixing and litter identity from the soil legacy effect by conducting a factorial laboratory experiment where two fresh single root litters and their mixture were mixed with soils previously cultivated with single plant species or mixtures of two or four species. We found no evidence for litter-mixing effects. In contrast, root litter-induced CO2 production was greater in soils from high diversity plots than in soils from monocultures, regardless of the type of root litter added. Soil microbial PLFA biomass and composition at the onset of the experiment was unaffected by plant species richness, whereas soil potential nitrogen (N) mineralization rate increased with plant species richness. Our results indicate that the soil legacy effect may be explained by changes in soil N availability. There was no effect of plant species richness on decomposition of a recalcitrant substrate (compost). This suggests that the soil legacy effect predominantly acted on the decomposition of labile organic matter. We thus demonstrated that plant species richness enhances root litter-induced soil respiration via a soil legacy effect but not via a litter-mixing effect. This implies that the positive impacts of species richness on soil C sequestration may be weakened by accelerated organic matter decomposition. 相似文献
15.
In nutrient-limited alpine meadows,nitrogen(N) mineralization is prior to soil microbial immobilization;therefore,increased mineral N supply would be most likely immobilized by soil microbes due to nutrient shortage in alpine soils.In addition,low temperature in alpine meadows might be one of the primary factors limiting soil organic matter decomposition and thus N mineralization.A laboratory incubation experiment was performed using an alpine meadow soil from the Tibetan Plateau.Two levels of NH4NO3(N) or glucose(C) were added,with a blank without addition of C or N as the control,before incubation at 5,15,or 25 ℃ for 28 d.CO2 efflux was measured during the 28-d incubation,and the mineral N was measured at the beginning and end of the incubation,in order to test two hypotheses:1) net N mineralization is negatively correlated with CO2 efflux for the control and 2) the external labile N or C supply will shift the negative correlation to positive.The results showed a negative correlation between CO2 efflux and net N immobilization in the control.External inorganic N supply did not change the negative correlation.The external labile C supply shifted the linear correlation from negative to positive under the low C addition level.However,under the high C level,no correlation was found.These suggested that the correlation of CO2 efflux to net N mineralization strongly depend on soil labile C and C:N ratio regardless of temperatures.Further research should focus on the effects of the types and the amount of litter components on interactions of C and N during soil organic matter decomposition. 相似文献
16.
Plant roots and their associated mycorrhizal fungi critically mediate the decomposition of soil organic carbon (C), but the general patterns of their impacts over a broad geographical range and the primary mediating factors remain unclear. Based on a synthesis of 596 paired observations from both field and greenhouse experiments, we found that living roots and/or mycorrhizal fungi increased organic C decomposition by 30.9%, but low soil nitrogen (N) availability (i.e., high soil C:N ratio) critically mitigated this promotion effect. In addition, the positive effects of living roots and/or mycorrhizal fungi on organic C decomposition were higher under herbaceous and leguminous plants than under woody and non-leguminous plants, respectively. Surprisingly, there was no significant difference between arbuscular mycorrhizal fungi and ectomycorrhizal fungi in their effects on organic C decomposition. Furthermore, roots and/or mycorrhizal fungi significantly enhanced the decomposition of leaf litter but not root litter. These findings advance our understanding of how roots and their symbiotic fungi modulate soil C dynamics in the rhizosphere or mycorrhizosphere and may help improve predictions of soil global C balance under a changing climate. 相似文献
17.
溶解性有机质在土壤固碳中的意义 总被引：4，自引：2，他引：2
随着全球变暖的加剧,土壤圈作为全球碳循环中的重要碳库受到日益关注。土壤有机碳固定对大气温室效应和气候变暖有重要影响。溶解性有机质(DOM)是土壤中最活跃的有机碳库,其含量与土壤CO2、CH4、N2O的排放显著正相关,DOM的矿化成为土壤有机碳损失的重要途径。DOM可通过与Fe、Al共沉淀、吸附于土壤矿物表面而改变其生物降解性,从而在土壤中稳定和保留下来,对土壤有机碳积累中具有重要贡献。DOM的化学组成和结构特征影响其生物降解性,同时也影响其沉淀吸附效应。其稳定机制不同,对土壤有机碳积累的贡献也存在差异。目前估算DOM对土壤有机碳的贡献尚无普遍认可的方法,具体数值因估算方法不同而存在较大差异,有效的估算方法仍有待于进一步研究。 相似文献
18.
选择半干旱(宁夏盐池)、干旱(内蒙古乌拉特后旗)荒漠草原区为研究样地,以牛枝子枯落物为研究对象,采用网孔分解袋法研究土壤动物分解功能对枯落物C、N、P、K分布的影响,结合枯落物分解过程中土壤有机碳(SOC)、全氮(TN)、全磷(TP)、全钾(TK)含量分布特征,阐明土壤动物分解作用对土壤营养元素含量分布的影响规律。结果表明：(1)共捕获土壤动物226只,隶属14科(属)。土壤动物个体数表现为盐池地区均高于乌拉特地区,而类群数差异较小,仅在乌拉特地区灌丛高于裸地。土壤动物Simpson指数、Shannon指数和Margalef指数在不同生境下均无显著差异,Pielou指数在裸地生境下表现为乌拉特地区显著高于盐池地区。(2)不同网孔分解袋中枯落物养分元素均处于不同程度的释放状态。其中枯落物C、N元素累积系数在盐池地区表现为2 mm网孔显著低于0.01 mm网孔,在乌拉特地区表现为2 mm网孔显著高于0.01 mm网孔;枯落物P、K元素累积系数分别在乌拉特地区和盐池地区表现为2 mm网孔显著高于0.01 mm网孔,且土壤动物对盐池枯落物C、N、P、K元素释放均表现为正效应;对乌拉特枯落物C、... 相似文献
19.
Feike A. Dijkstra Jack A. Morgan Ronald F. Follett 《Soil biology & biochemistry》2010,42(7):1073-1082
Plants can affect soil organic matter decomposition and mineralization through litter inputs, but also more directly through root-microbial interactions (rhizosphere effects). Depending on resource availability and plant species identity, these rhizosphere effects can be positive or negative. To date, studies of rhizosphere effects have been limited to plant species grown individually. It is unclear how belowground resources and inter-specific interactions among plants may influence rhizosphere effects on soil C decomposition and plant N uptake. In this study, we tested the simple and interactive effects of plant diversity and water availability on rhizosphere-mediated soil C decomposition and plant N uptake. The study was conducted in the greenhouse with five semi-arid grassland species (monocultures and mixtures of all five species) and two water levels (15 and 20% gravimetric soil moisture content). We hypothesized that microbial decomposition and N release would be less in the low compared to high water treatment and less in mixtures compared to monocultures. Rhizosphere effects on soil C decomposition were both positive and negative among the five species when grown in monoculture, although negative effects prevailed by the end of the experiment. When grown in mixture, rhizosphere effects reduced soil C decomposition and plant N uptake compared to monocultures, but only at the low-water level. Our results suggest that when water availability is low, plant species complementarity and selection effects on water and N use can decrease soil C decomposition through rhizosphere effects. Although complementarity and selection effects can increase plant N uptake efficiency, plant N uptake in the mixtures was still lower than expected, most likely because rhizosphere effects reduced N supply in the mixtures more than in the monocultures. Our results indicate that rhizosphere effects on C and N cycling depend on water availability and inter-specific plant interactions. Negative rhizosphere effects on soil C decomposition and N supply in mixtures relative to monocultures of the component species could ultimately increase soil C storage and possibly influence how plant communities in semi-arid grasslands respond to global climate change. 相似文献
20.
Phenol oxidase, peroxidase and organic matter dynamics of soil 总被引：2，自引：0，他引：2
Robert L. Sinsabaugh 《Soil biology & biochemistry》2010,42(3):391-404
Extracellular enzymes mediate the degradation, transformation and mineralization of soil organic matter. The activity of cellulases, phosphatases and other hydrolases has received extensive study and in many cases stoichiometric relationships and responses to disturbances are well established. In contrast, phenol oxidase and peroxidase activities, which are often uncorrelated with hydrolase activities, have been measured in only a small subset of soil enzyme studies. These enzymes are expressed for a variety of purposes including ontogeny, defense and the acquisition of carbon and nitrogen. Through excretion or lysis, these enzymes enter the environment where their aggegrate activity mediates key ecosystem functions of lignin degradation, humification, carbon mineralization and dissolved organic carbon export. Phenol oxidases and peroxidases are less stable in the environment than extracellular hydrolases, especially when associated with organic particles. Activities are also affected, positively and negatively, by interaction with mineral surfaces. High spatiotemporal variation obscures their relationships with environmental variables and ecological process. Across ecosystems, phenol oxidase and peroxidase activities generally increase with soil pH, a finding not predicted from the pH optima of purified enzymes. Activities associated with plant litter and particulate organic matter often correlate with decomposition rates and potential activities generally increase with the lignin and secondary compound content of the material. At the ecosystem scale, nitrogen amendment alters the expression of phenol oxidase and peroxidase enzymes more broadly than culture studies imply and these responses correlate with positive and negative changes in litter decomposition rates and soil organic matter content. At the global scale, N amendment of basidiomycete-dominated soils of temperate and boreal forest ecoystems often leads to losses of oxidative enzyme activity, while activities in grassland soils dominated by glomeromycota and ascomycetes show little net response. Land use that leads to loss of soil organic matter tends to increase oxidative activities. Across ecosystems, soil organic matter content is not correlated with mean potential phenol oxidase and peroxidase activities. A multiple regression model that includes soil pH, mean annual temperature, mean annual precipitation and potential phenol oxidase activity accounts for 37% of the variation in soil organic matter (SOM) content across ecosystems (n = 63); a similar model for peroxidase activity describes 32% of SOM variance (n = 43). Analysis of residual variation suggest that suites of interacting factors create both positive and negative feedbacks on soil organic matter storage. Soils with high oxygen availability, pH and mineral activity tend to be substrate limited: high in situ oxidative activities limit soil organic matter accumulation. Soils with opposing characteristics are activity limited: low in situ oxidative activities promote soil organic matter storage. 相似文献