基于文献计量的近20多年来土地利用对土壤有机碳影响研究进展与热点

土壤有机碳是陆地碳库的重要组成部分,土地利用/覆被变化及土地管理通过影响土壤有机碳储量、组分、时空分布,进而影响全球碳循环和全球气候变化,是当前的研究热点。土地利用变化对土壤有机碳影响的研究已有很多,但基于文献计量视角的分析报道较少。以Web of Science数据库和CNKI数据库为数据源,通过文献计量学方法和Citespace软件平台,分析了1991~2014年土地利用变化与管理对土壤有机碳影响的研究进展及热点。研究表明:森林、草地、农田等土地利用类型及土地利用变化与管理对土壤有机碳的影响是研究的重点;森林、草地生态系统主要通过土地利用变化(林地转化为次生林、草地、耕地;草地过渡放牧或转化为耕地)影响土壤有机碳变化;农田主要通过土地管理(退耕还林还草、耕作方式、施肥等)来影响土壤有机碳变化;土壤有机碳变化研究选取的指标越来越具体化,模型多样化,但土壤有机碳模型研究还未成体系,土壤有机碳变化趋势预测是未来研究的重点。     

川西亚高山云杉人工林恢复过程中土壤有机碳矿化研究

研究了川西亚高山云杉(Picea asperata Mast.)人工林不同阶段(22、47、65年)及原始林表层(0～30cm)土壤有机碳的矿化,并用两室模型对实验数据进行了回归。结果表明,不同恢复阶段云杉人工林各层土壤(0～10、10～20、20～30cm)有机碳64天累积释放的CO2-C显著大于原始林。两室模型模拟土壤有机碳矿化过程得出土壤活性有机碳(AC)含量及其占总有机碳含量的比例均大于原始林,表明原始林转化为云杉人工林后,土壤有机碳稳定性降低。此外,本文分析了凋落物、微生物、土壤理化性质等因素对云杉人工林土壤有机碳矿化的可能影响。     

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。     

吉林西部盐碱地区稻田土壤有机碳矿化特征

以吉林西部盐碱地区(前郭灌区)土壤为研究对象,选取不同盐碱程度的4块水田(P1、P2、P3和P4),采用野外实地调研采样与室内模拟试验相结合的方法,分别在培养期的第1,4,7,10,14,21,28,35,70天测定土壤CO_2气体的排放通量,结合土壤基本理化性质,分析盐碱稻田矿化模拟培养过程中CO_2通量的动态变化,研究土壤盐碱化程度对有机碳矿化过程的影响。结果表明:P1、P2、P3为弱碱化土,P4为强碱化土;各样地土壤有机碳(SOC)含量差异显著,并存在表层富集现象,与碱化度(ESP)呈显著负相关关系(r=-0.945);SOC矿化量累积过程与培养时间符合一级动力学模型C_t=C_0(1-e^-kt),各样地土壤在矿化培养初期CO_2释放量较大,释放强度降低较快,矿化速率随时间延长呈缓慢平稳下降,在培养期结束时降至最低。SOC矿化过程受多种因子共同作用,ESP是该过程的主要影响因子。土壤的盐碱化抑制了土壤碳循环的速度,相对于碳源过程而言,对碳汇的影响更大。伴随SOC含量增加,SOC矿化反应强度和矿化反应的完全程度加强,矿化反应累积量增加,反之,随ESP程度增加而减弱。     

土壤有机碳激发效应研究进展

土壤有机C激发效应是加入外源物后土壤有机C周转短期的强烈变化。综合多年的研究结果表明:外源物的加入可能加速土壤有机C的矿化,产生正激发效应;也可能减缓土壤有机C的矿化,产生负激发效应。激发效应的产生受输入外源物的数量和质量、土壤本身的性质等因素影响,其产生机理还需进一步研究。本文综合这些年来利用同位素(13C和14C)示踪技术进行的土壤有机C研究,比较系统地阐述了土壤有机C激发效应产生的驱动因子、机理及其定量化,并提出了有待研究的内容。     

基于文献计量分析的土壤固碳研究进展

为了解国内外土壤固碳的相关研究前沿与进展,本文基于Web of Science核心数据库与CNKI数据库,利用文献计量分析方法对领域内的研究现状、研究热点和前沿趋势进行了分析.研究结果表明:关于土壤固碳研究的发文量整体呈上升趋势,且近几年增幅较大.美国的发文量及发文期刊的影响力均较高.从国际合作水平来看,中美两国的合作...     

作物残体与其生物炭配施对土壤有机碳及其自身矿化率的提升

【目的】本研究通过探讨小麦和玉米残体与其生物炭配施对土壤各组分有机碳及其自身有机碳矿化的影响,揭示其在土壤固碳和培肥方面的效应,为农田有机物资源合理利用提供理论支撑。【方法】采用室内恒温培养试验,共设置小麦或玉米残体(根茬、秸秆)和秸秆制成的生物炭单施(WS、WR、WB、MS、MR、MB),配施(WS+WB、WR+WB、MS+MB、MR+MB)以及对照(CK)构成的11个处理,培养期间测定土壤CO2释放量,培养结束后测定土壤总有机碳(TOC)、可溶性有机碳(DOC)、微生物量碳(MBC)、颗粒有机碳(POC)以及粗细颗粒有机碳含量(CPOC、FPOC)。【结果】添加玉米有机物料对土壤TOC、MBC、POC、CPOC和FPOC含量的增加作用普遍高于添加小麦有机物料。添加小麦或玉米秸秆对土壤TOC、POC、CPOC、FPOC含量的增加作用均高于添加根茬。单独添加生物炭,作物残体与生物炭配施和单独添加作物残体处理分别在培养的第4、8、21 d有机碳矿化速率最大,为有机碳矿化快速期,之后矿化速率减缓并逐渐趋于稳定。单独添加作物残体其有机碳累积矿化率最大,达到30%~46%;与对照相比,添加有机物料的各处理均显著增加了土壤TOC含量,其中添加生物炭处理土壤TOC含量增幅最大;单独添加小麦和玉米生物炭处理,土壤TOC含量分别显著增加34.4%和36.5%,但其有机碳累积矿化率仅为3%左右,土壤FPOC含量及敏感性指数在单独添加生物炭处理最高;小麦和玉米残体与其生物炭配施处理,土壤MBC和CPOC含量分别显著增加80.2%~199.2%,且其有机碳累积矿化率为12%~19%,介于生物炭和残体单施之间,土壤CPOC含量及敏感性指数均表现为配施处理最高。【结论】单独添加作物残体能够较好地补充土壤养分,但CO2释放量显著高于单施生物炭及配施处理;单独添加生物炭其有机碳累积矿化率较低,短期内对土壤养分的补充作用较小。作物残体与其生物炭配施可以较好地克服各自单独施用的弊端,尤其是玉米秸秆与其生物炭配施,在保证作物养分供应的同时能增加土壤碳库储量,对土壤肥力提升效果更好。     

基于文献计量的土壤有机碳与土壤微生物多样性研究前沿态势分析

为了系统了解国际上土壤有机碳与微生物多样性的研究进展,基于Web of Science数据源,利用Web of Science数据库分析工具和Thomson Data Analysis(TDA)、社会网络分析与可视化工具Netdraw和Ucinet,从论文年度变化趋势、全球研究实力国家、机构分布和力量比较、基金资助机构和主题分布、机构合作和研究内容等方面,对1992~2015年的相关论文,尤其是近10年来土壤有机碳及其影响因素的相关文章进行计量分析。结果表明:(1)论文数量呈逐年增长态势,土壤有机碳与土壤微生物多样性研究主要集中在欧美发达国家(地区);美国和德国综合影响力最高,英国、瑞典、瑞士、荷兰论文篇均被引较高,以中国科学院为代表的中国机构在该领域研究增长较快,研究论文最多,但论文整体质量有待提高。(2)中国国家自然基金资助机构产出论文最多;美国国家科学基金会资助论文篇均被引最高,其次是德国研究基金会,中国科学院科学基金名列第3,各国在共同资助的研究主题基础上,各有其特色主题;美国的一些研究机构是全球该领域研究合作交流的中心,其次是德国和中国中科院。(3)土壤有机质、土壤有机碳、凋落物分解、氮、磷、微生物生物量、土壤性质、气候变化、碳固定是该领域10年来的热点研究主题。未来应加强国际合作研究,关注土壤重金属、凋落物分解和微生物呼吸等相关主题,以提高我国研究水平,将相关研究成果及时应用于解决相应的实际问题。     

塔里木盆地北缘绿洲不同土地利用方式下土壤有机碳含量及其碳矿化特征

[目的]探讨土地利用方式对土壤有机碳含量及碳矿化的影响,为塔里木盆地北缘绿洲土壤生态系统的保护和恢复建设提供理论依据。[方法]基于野外采样和室内培养试验,分析土壤有机碳含量的基本特征,利用回归分析法拟合出土壤有机碳矿化动态变化过程。[结果]矿化累积释放的CO2含量大小依次为:果园棉田人工林弃耕地荒草地盐碱地沙地。不同土地利用方式土壤有机碳矿化反应趋势相同,1~6d为快速分解阶段,日均矿化量高但反应时间短,6~28d为缓慢分解阶段,动态变化与前者相反。有机碳矿化率大小依次为:沙地荒草地盐碱地弃耕地人工林棉田果园,沙地最高,达(10.36±0.24)%,表明沙地土壤有机碳稳定性最差,而果园具有较强的固定有机碳能力。[结论]土地利用方式对土壤有机碳矿化及其固碳能力均有显著影响。     

尕海湿地植被退化过程中土壤有机碳矿化特征

为了揭示植被退化对湿地土壤碳矿化过程的影响,以甘南尕海4种不同植被退化梯度的湿地(未退化(UD)、轻度退化(LD)、中度退化(MD)及重度退化(HD))为研究对象,采用室内恒温培养和碱液吸收法研究不同土层土壤有机碳(SOC)矿化速率和累积矿化量,结合一级动力学方程,分析土壤半矿化分解时间(T1/2)、有机碳矿化潜势(C0)等参数对植被退化的响应。结果表明:(1)不同植被退化梯度湿地SOC矿化速率在培养期内呈现出基本一致的变化趋势,表现为,培养初期(0~4天)矿化速率快速下降,且数值较高,培养中后期缓慢下降(4~41天)并趋于平稳;各培养温度下,不同植被退化梯度湿地土壤在各土层有机碳矿化速率大小均为UD>LD>MD>HD。(2)在整个培养期间,各植被退化梯度湿地土壤有机碳矿化速率均随土层加深而降低,表层0-10 cm的矿化速率(1.14~16.23 mg/(g·d))均显著高于10-20 cm(1.05~2.85mg/(g·d))和20-40 cm土层(0.94~1.26 mg/(g·d))。(3)4种植被退化梯度湿地在不同温度下的土壤有机碳累积矿化量均值排序为5°C(34.54 mg/g)<15°C(46.67 mg/g)<25°C(58.28 mg/g)<35°C(86.46 mg/g)。(4)一级动力学方程的C0值随植被退化程度增加呈递减趋势,而C0/SOC随着温度的升高而降低。因此,植被退化能显著降低高寒湿地土壤有机碳矿化速率,而气候变暖能够显著增加湿地土壤有机碳矿化量。     

Positive and negative carbon mineralization priming effects among a variety of biochar-amended soils

Pyrogenic carbon (biochar) amendment is increasingly discussed as a method to increase soil fertility while sequestering atmospheric carbon (C). However, both increased and decreased C mineralization has been observed following biochar additions to soils. In an effort to better understand the interaction of pyrogenic C and soil organic matter (OM), a range of Florida soils were incubated with a range of laboratory-produced biochars and CO₂ evolution was measured over more than one year. More C was released from biochar-amended than from non-amended soils and cumulative mineralized C generally increased with decreasing biomass combustion temperature and from hardwood to grass biochars, similar to the pattern of biochar lability previously determined from separate incubations of biochar alone.The interactive effects of biochar addition to soil on CO₂ evolution (priming) were evaluated by comparing the additive CO₂ release expected from separate incubations of soil and biochar with that actually measured from corresponding biochar and soil mixtures. Priming direction (positive or negative for C mineralization stimulation or suppression, respectively) and magnitude varied with soil and biochar type, ranging from −52 to 89% at the end of 1 year. In general, C mineralization was greater than expected (positive priming) for soils combined with biochars produced at low temperatures (250 and 400 °C) and from grasses, particularly during the early incubation stage (first 90 d) and in soils of lower organic C content. It contrast, C mineralization was generally less than expected (negative priming) for soils combined with biochars produced at high temperatures (525 and 650 °C) and from hard woods, particularly during the later incubation stage (250-500 d). Measurements of the stable isotopic signature of respired CO₂ indicated that, for grass biochars at least, it was predominantly pyrogenic C mineralization that was stimulated during early incubation and soil C mineralization that was suppressed during later incubation stages. It is hypothesized that the presence of soil OM stimulated the co-mineralization of the more labile components of biochar over the short term. The data strongly suggests, however, that over the long term, biochar-soil interaction will enhance soil C storage via the processes of OM sorption to biochar and physical protection.     

Biochar reduces the rhizosphere priming effect on soil organic carbon

Biochar has the potential to store carbon (C) in soils on a millennial time scale and hence it is proposed as a tool to aid in the mitigation of climate change. However, the presence of biochar in soil can induce either a positive or negative priming effect on native soil C, or the converse, which may either reduce or enhance the C storage potential of biochar. Thus far, priming effects between soil and biochar have been predominately assessed in the exclusion of plants. Therefore, this study set out with the aim to assess the priming effect of plants, i.e., rhizosphere priming effect (RPE) in the presence and absence of biochar and within different soil types. Three soils (Arenosol, Cambisol and Ferralsol) were used in full factorial combination with or without soybean plants and with or without 2% blue mallee biochar that was produced at 500 °C by slow pyrolysis. Plants were labelled with an isotopically depleted δ¹³C signature to that of the soil and biochar to allow the separation of plant-derived CO₂–C from the total CO₂–C. Carbon dioxide was trapped three times over a period of 13 days. Subsequent titration of the CO₂ trap samples followed by IRMS analysis was used to quantify the CO₂–C captured and its source. Biochar was found to have no effect on plant or microbial biomass. Plant treatments had significantly higher overall respiration rates than those without plants. Plants induced a negative priming in the Arenosol which was similar in the absence and presence of biochar. In the Cambisol, biochar induced a significant negative RPE in comparison to the positive RPE in the control. The RPE in the Ferralsol was positive and substantially decreased in the presence of biochar. Our results suggest that blue mallee biochar amendments may partially offset the positive RPE, or reduce it further where it is already negative.     

The priming potential of biochar products in relation to labile carbon contents and soil organic matter status

Recognition of biochar as a potential tool for long-term carbon sequestration with additional agronomic benefits is growing. However, the functionality of biochar in soil and the response of soils to biochar inputs are poorly understood. It has been suggested, for example, that biochar additions to soils could prime for the loss of native organic carbon, undermining its sequestration potential. This work examines the priming potential of biochar in the context of its own labile fraction and procedures for their assessment. A systematic set of biochar samples produced from C4 plant biomass under a range of pyrolysis process conditions were incubated in a C3 soil at three discrete levels of organic matter status (a result of contrasting long-term land management on a single site). The biochar samples were characterised for labile carbon content ex-situ and then added to each soil. Priming potential was determined by a comparison of CO₂ flux rates and its isotopic analysis for attribution of source. The results conclusively showed that while carbon mineralisation was often higher in biochar amended soil, this was due to rapid utilisation of a small labile component of biochar and that biochar did not prime for the loss of native organic soil organic matter. Furthermore, in some cases negative priming occurred, with lower carbon mineralisation in biochar amended soil, probably as a result of the stabilisation of labile soil carbon.     

绿肥压青对粉垄稻田土壤微生物量碳和有机碳累积矿化量的影响

绿肥压青还田是调控现代集约化稻田土壤逆境的重要手段,为评估绿肥压青下粉垄耕作对稻田土壤微生物量碳和土壤有机碳累积矿化量的影响,设置早稻粉垄耕作与常规耕作2种耕作模式,不施肥和同等肥力条件下施化肥、单倍绿肥配施化肥和双倍绿肥配施化肥4种施肥处理,晚稻免耕常规施用化肥,开展双季稻周年大田应用试验。结果表明:单倍绿肥压青下,粉垄耕作能提高稻田土壤微生物量碳含量,可达常规耕作的2倍,能有效增加微生物对土壤碳素的利用率。增加绿肥压青量会提高粉垄耕作稻田土壤有机碳累积矿化量和矿化潜力,与施用化肥相比,单倍绿肥压青下早晚稻分别增加1.6%～32.8%和0.6%～16.6%,双倍绿肥压青下分别增加58.6%～70.9%和29.6%～38.4%。粉垄单倍绿肥压青会降低免耕晚稻齐穗期、收获期土壤呼吸强度,较常规耕作分别降低33.4%和38.7%,较粉垄耕作其他处理降低8.5%～31.4%。单倍绿肥压青下粉垄稻田土壤代谢商较常规耕作累积降低65.5%,与常耕相比,粉垄双倍绿肥压青和粉垄单一化肥的土壤代谢商分别累积增加20.3%和159.2%,粉垄双倍绿肥压青可有效缓解土壤代谢商的提升。微生物量碳含量与有机碳矿化激发效应呈负相关,绿肥压青还田下相关系数达0.44;累积矿化量和代谢商呈极显著正相关,粉垄耕作下相关系数达0.59。可见,绿肥粉垄耦合的模式可作为一种增加稻田土壤微生物量碳含量、减少部分生育时期土壤呼吸强度,增强土壤碳库稳定性及碳固持的重要调控技术措施。     

长期施肥对栗褐土有机碳矿化的影响

【目的】 土壤有机碳矿化是土壤中重要的生物化学过程,与土壤养分的释放、土壤质量的保持以及温室气体的形成密切相关。本文以 25 年长期定位施肥试验为依托,对栗褐土土壤有机碳矿化速率、有机碳累积矿化量的动态变化进行研究,为科学管理土壤肥力、增加栗褐土碳汇、减少温室气体排放提供依据。 【方法】 田间试验开始于 1988,共设置 8 个施肥处理:不施肥 (CK);单施氮肥 (N);氮磷肥合施 (NP);单施低量有机肥(M₁);低量有机肥与氮肥合施 (M₁N);低量有机肥与氮磷肥合施(M₁NP);高量有机肥与氮肥合施 (M₂N);高量有机肥与氮磷肥合施 (M₂NP)。于 2013 年玉米播种前,采集耕层 (0—20 cm) 土壤样品,采用室内培养方法,对土壤碳矿化释放 CO₂ 的数量和速率进行测定,并利用一级动力学方程计算出土壤有机碳库潜在矿化势和周转速率。 【结果】 各肥料处理不同程度地提高了栗褐土总有机碳含量,以高量有机肥与化肥配施作用最为显著。与 CK 相比,M₂N、M₂NP 处理土壤总有机碳含量增加了 121.1%、166.8%。不同处理土壤样品培养有机碳矿化速率均在第一天达到峰值,随后急剧下降。5 d 后,下降趋缓,不同处理 CO₂ 产生速率趋于一致。培养期间,各处理矿化速率变化符合对数函数关系。长期施用不同肥料均可以提高栗褐土有机碳的矿化速率,其大小顺序为:有机肥与化肥配施 > 单施有机肥 > 单施化肥 > 对照。培养 57 d 后,各处理土壤有机碳累积矿化量为 555.0～980.3 mg/kg,以 M₂NP、M₁N 的累积量较高,为对照的 1.77 倍、1.73 倍。长期施肥栗褐土有机碳矿化率呈下降趋势,以处理 M₂NP 下降最明显,与对照相比,降低了 6.3 个百分点。施肥处理土壤的潜在矿化势均高于对照,M₁N、M₂NP 最高,为 923.7 mg/kg 和 926.4 mg/kg,较对照增加了 74.0% 和 74.5%。不同施肥处理均可明显提升土壤有机碳的周转速率,减少周转时间,其中处理 M₁NP、M₂NP 效果最为明显。 【结论】 长期施用化肥、有机肥及有机无机肥配施可有效促进栗褐土有机碳的积累,提高有机碳的矿化速率和周转速率,降低有机碳的矿化率 (累积矿化量占有机碳总量的比率),加强了土壤的固碳能力,以 M₂NP 处理的效果更佳。      

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。     

添加生物质炭对红壤水稻土有机碳矿化和微生物生物量的影响

通过室内培育试验,研究了添加生物质炭对江西红壤水稻土有机碳矿化和微生物生物量碳、氮含量的影响。结果表明:红壤有机碳矿化速率在培育第2天达最大值后迅速降低,培养7天后下降缓慢并趋于平稳;添加生物质炭降低了土壤有机碳的矿化速率和累积矿化量,培养结束时,不加生物质炭的对照处理中有机碳的累积矿化量分别比添加0.5%和1.0%生物质炭的处理高10.0%和10.8%。此外,生物质炭的加入显著提高了土壤微生物生物量,添加0.5%生物质炭处理的土壤微生物生物量碳、氮含量分别比对照高111.5%～250.6%和11.6%～97.6%,添加1.0%生物质炭处理的土壤微生物生物量碳、氮含量分别比对照高58.9%～243.6%和55.9%～110.4%。相同处理中,干旱的水分条件下(40%田间持水量)微生物生物量要高于湿润的水分条件(70%田间持水量)。同时,添加0.5%和1.0%的生物质炭使土壤代谢熵分别降低2.4%和26.8%,微生物商减少了43.7%和31.7%。     

Soil fauna and organic amendment interactions affect soil carbon and crop performance in semi-arid West Africa

A field experiment was conducted at Kaibo in southern Burkina Faso on an Eutric Cambisol during the 2000 rainy season to assess the interaction of organic amendment quality and soil fauna, affecting soil organic carbon and sorghum (Sorghum bicolor L. Moench) performance. Plots were treated with the pesticides Dursban and Endosulfan to exclude soil fauna or left untreated. Sub-treatments consisted of surface-placed maize straw (C/N ratio = 58), Andropogon straw (C/N ratio = 153), cattle dung (C/N ratio = 40), sheep dung (C/N ratio = 17) or compost (C/N ratio = 10) and the control. Organic amendments were applied at a dose equivalent to the application of 40 kg N ha⁻¹. The presence of soil fauna increased soil total carbon by 32% and grain yield production by 50%. The interaction between high C/N ratio organic amendment, Andropogon straw (SA), and soil fauna reduced soil carbon build-up. We suggest that this is due to a priming effect of SA on soil organic matter in the presence of soil fauna. We also suggest that the interaction between soil fauna and easily decomposable organic amendment led to the smallest decrease in soil carbon build-up. It is concluded that in semi-arid West Africa, in the presence of soil fauna, soil carbon build-up is more affected by the quality of organic amendments than the quantity of carbon inputs. Sorghum grain yield production was significantly reduced in the absence of soil fauna. High C/N ratio organic amendment interacted negatively with soil fauna in its effects on crop performance. We propose that the effect of soil fauna on soil carbon build-up and crop performance can be optimised by using high quality organic matter or supplementing low-quality organic matter with inorganic nitrogen in semi-arid West Africa.     

黑碳添加对土壤有机碳矿化的影响

通过室内培养试验,向土壤中分别添加不同温度制备的黑碳,热解温度分别为350℃(T350)、600℃(T600)和850℃(T850),研究了黑碳添加对土壤有机碳矿化的影响。结果表明,不同温度条件制备的黑碳在15℃和25℃培养条件下,土壤CO2释放速率总的趋势是前期分解速率快,后期缓慢。在整个培养过程中(112天),随着培养时间的延长,土壤CO2释放速率下降趋势逐渐降低,CO2释放速率相对值的大小随着培养温度的的升高而增大。在不同温度培养条件下,添加黑碳后土壤CO2-C累计量均是T350>T600>T850,T350土壤CO2-C累计量最高分别为415.26 mg/kg和733.82 mg/kg。添加不同黑碳后,土壤有机碳矿化增加率存在极显著差异(p<0.01),表明不同温度制备的黑碳对土壤有机碳矿化的影响显著。     

温度和植物残体对紫色母岩发育的水稻土有机碳矿化的影响

培养试验研究了2种温度下紫色水稻土有机碳的矿化特征以及添加不同植物残体对其矿化的影响。结果表明, 62d的培养过程中,有机碳累积矿化量在28℃条件下为C 66.79 mg/g;40℃条件下为C 86.99 mg/g,差异达到极显著水平。用一级动力学方程对植物残体的矿化速率进行拟合表明,28℃条件下,植物残体的分解速率常数（k）为蚕豆秸秆玉米秸秆水稻秸秆,而40℃条件下则为水稻秸秆玉米秸秆蚕豆秸秆。温度状况和植物残体化学组分的差异影响了紫色水稻土中有机碳的动态变化,最终导致了碳累积矿化量的差异。