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1.
碳氮添加对雨养农田土壤全氮、有机碳及其组分的影响 总被引：2，自引：1，他引：1
为探明碳氮添加4年后,土壤全氮、有机碳及其组分(可溶性有机碳、微生物量碳、轻组和重组有机碳)的变化特征,依托布设于甘肃省定西市安定区李家堡镇的不同碳源配施氮素田间定位试验,涉及秸秆、生物质炭、氮素3个因素,秸秆设置为不施、施用秸秆2水平;生物质炭为不施和施用生物质炭2个水平;氮素设置为不施氮、施纯氮50 kg/hm^2、施纯氮100 kg/hm^2 3个水平,共9个处理。结果表明:不同处理下土壤全氮、有机碳及其组分的含量均随土层的加深而降低。添加生物质炭对土壤全氮、有机碳及其组分均具有不同程度的提升效应。添加秸秆对土壤全氮、有机碳和可溶性有机碳、微生物量碳、轻组有机碳均具有显著提升效应,仅在0-5 cm土层对重组有机碳有显著提高。添加氮素可显著提升土壤全氮、有机碳和可溶性有机碳、微生物量碳、轻组有机碳含量。较其他处理,添加生物质炭对土壤全氮、有机碳和重组有机碳的提升效应最高,添加秸秆对可溶性有机碳、微生物量碳、轻组有机碳的提升效果最优。从提升土壤质量的角度出发,推荐秸秆配施氮素模式,该模式下土壤碳素有效性高、易于被微生物利用,有利于作物生长。从提高土壤固碳角度考虑,推荐生物质炭配施氮素模式,该模式有利于碳的封存。 相似文献
2.
生物质炭对土壤有机质活性的影响 总被引：35，自引：4，他引：31
为了解施用生物质炭对土壤碳组分的潜在影响,通过室内2年盆栽培养试验研究施用不同用量生物质炭对土壤有机碳积累、有机碳稳定性、微生物量碳和水溶性有机碳的影响,并与施用等碳量的小麦秸秆、酸洗生物质炭(去除生物质炭中的速效养分)及同时施用小麦秸秆与生物质炭的处理进行比较。结果表明,施用生物质炭可显著提高土壤有机碳的积累,增加土壤有机碳的氧化稳定性,降低土壤水溶性有机碳。施用生物质可在短时间内增加微生物量碳,但随着培养时间的增加,其微生物量碳逐渐下降,最终明显低于对照土壤(不施有机物料的处理)。土壤水溶性有机碳的下降可能与生物质炭对其吸附固定有关,而短时间内激发微生物量碳增加可能与施入生物质炭增加了土壤有效养分、改善土壤微生物生长环境有关。研究结果认为,长期单一施用生物质炭可能会引起土壤有机质生物活性的下降,但生物质炭与一般生物质有机肥配合施用可减免这些负影响。 相似文献
3.
玉米秸秆和污泥共热解制备的生物质炭及其对盐碱土壤理化性质的影响 总被引：5，自引：2，他引：3
[目的]研究不同温度制备的玉米秸秆和污泥基生物质炭不同施加量对盐碱土壤基本理化性质的影响,为盐碱土改良及土壤污染物质的生态修复等方面的研究提供科学依据。[方法]以质量比5∶2的玉米秸秆和剩余活性污泥为原料,分别在300,350,400,450,500℃共5个不同温度条件下热解制备生物质炭,通过扫描电镜、元素分析和红外光谱对其性质及结构进行分析,并通过培养试验研究其对盐碱土壤基本理化性质的影响。[结果]随着热解温度的升高,生物质炭微观结构越发达,比表面积越大,表面官能团的种类和数量也产生了显著性变化;同时随着热解温度逐渐升高,生物质炭C含量不断增加,而O,H和N含量却逐渐降低;添加玉米秸秆和污泥共热解制备的生物质炭能够显著增加盐碱土壤中有机碳含量,而土壤中总氮、总磷、有效磷、速效钾含量变化幅度较小;水溶性盐含量降低明显;加入生物质炭后大幅度提高了土壤阳离子交换能力,添加量越大,阳离子交换量越大;但生物质炭对土壤pH值影响不大。[结论]玉米秸秆和污泥基生物质炭提高了土壤养分含量和肥力指标,降低了土壤盐碱性。玉米秸秆和污泥基生物质炭可用于盐碱土壤的改良。 相似文献
4.
为探明添加不同碳源及不同量氮肥4年后对土壤物理性质、产量的影响,依托布设于甘肃省定西市安定区李家堡镇的不同碳源田间定位试验,设置2种碳源(生物质炭15t/hm^2,秸秆4.5t/hm^2),3个氮肥施用量(0,50,100kg/hm^2),共计9个处理。研究了生物质炭、秸秆配施氮肥对试区土壤容重、总孔隙度、土壤饱和导水率、土壤团聚体稳定性、产量的影响。结果表明:较之无碳添加处理,添加生物质炭或秸秆均可改善土壤物理性质,但生物质炭效果最好。秸秆输入对0-5cm土层土壤容重的降低和总孔隙度、水稳性团聚体稳定性的提升具有显著效应,对土壤饱和导水率和0-30cm各土层机械稳定性团聚体稳定性的提升具有显著效应,而生物质炭对0-30cm各土层的土壤物理指标的改善均具有显著效应。氮素添加对土壤物理指标影响较小。生物质炭、秸秆、氮素均可促进作物增产,总体而言,生物质炭增产效果优于秸秆,尤其是生物质炭15t/hm^2+施纯氮100kg/hm^2处理。因此,添加生物质炭更有利于该区土壤物理性质的改善和产量的增加。 相似文献
5.
以宁夏贺兰山东路风沙土为研究对象,分析秸秆、生物质炭等碳量添加下土壤有机碳及活性碳组分的变化,为确定该地区最佳施肥措施提供科学理论依据。结果表明:添加生物质炭和秸秆均显著增加了土壤有机碳含量,与对照相比土壤有机碳含量分别增加了7.7%、7.5%。添加生物质炭有利于土壤易氧化有机碳、颗粒有机碳的积累,二者含量分别比对照增加49.6%、17.5%;而添加秸秆更有利于土壤微生物生物量碳、可溶性有机碳的积累,其含量分别比对照分别增加25.8%、59.9%。秸秆与生物质炭添加均显著增加了土壤速效氮、容重和黏粒含量,且以添加生物质炭增加作用更为明显,显著降低了土壤全盐、砂粒含量。土壤有机碳、可溶性有机碳、颗粒有机碳、易氧化有机碳与速效氮含量极显著正相关,与全盐、砂粒含量极显著负相关;土壤可溶性有机碳、颗粒有机碳、易氧化有机碳与容重极显著负相关;而土壤微生物生物量碳与理化性质之间无显著相关性。综上,在风沙土中添加生物质炭更有利于土壤活性碳库提升和理化性质改善,且以年添加量7 t/hm2以上为宜。 相似文献
6.
以水稻秸秆为原料,分析了不同热解温度下所制备的生物质炭的性质,并采用批处理法,分析了生物质炭添加量和不同热解温度制备的生物质炭对土壤磷吸附特性的影响。结果表明:随着热解温度的升高,生物质炭的碳化程度、比表面积和磷含量增加。添加生物质炭显著减少了土壤对磷的吸附量,而且随着生物质炭热解温度的增加,土壤对磷的吸附量显著增加。Langmuir方程和Freundlich方程都能够较好地拟合添加生物质炭土壤的磷等温吸附曲线。准一级动力学方程和准二级动力学方程可较好地描述添加生物质炭土壤的磷吸附动力学行为。通过以上研究结果可知,水稻秸秆生物质炭可以减少土壤对磷的吸附并增加土壤有效磷的含量,因此在土壤磷肥肥效改良方面具有一定的应用潜力。 相似文献
7.
生物质炭结构性质及其对土壤有效养分和腐殖质组成的影响 总被引：1，自引：0，他引：1
生物质炭是具有高度热稳定性和较强吸附特性的含碳物质,不同来源生物质炭的结构性质可能存在着很大的差异。为此对2种自制的不同来源生物质炭和1种商业黑炭进行了结构表征,并研究了添加生物质炭对土壤有效养分和腐殖质组成的影响。结果表明,不同来源的生物质炭在结构上有明显区别：秸秆生物质炭的芳构化程度和热稳定性最低,脂族性最强;商业黑炭缩合程度和热稳定性最高,脂族性最弱;松枝生物质炭介于二者之间。向土壤中添加秸秆生物质炭和松枝生物质炭培养45d后,土壤有机碳含量、胡敏酸和富里酸含量、有效养分含量都有不同程度的增加,同时胡敏酸的色调系数ΔlgK降低,对土壤有机碳的长期保存有积极意义。 相似文献
8.
生物质炭添加对重金属污染稻田土壤理化性状及微生物量的影响 总被引：2，自引：1，他引：1
分析了生物质炭添加对红壤性水稻土理化性状、重金属含量及微生物生物量的影响。通过田间小区长期定位试验,一次性施入不同量生物质炭(0,10,20,30,40t/hm2),于2017年9月采集各处理表层土样(0—15cm),研究土壤理化性状、重金属含量及微生物生物量的变化。结果表明:生物质炭添加对土壤理化性状、重金属含量及微生物生物量均有显著影响。与对照相比,供试土壤的pH、EC和有机质含量随生物质炭添加量的增加而增大,增幅分别为5.11%~18.43%,37.62%~104.31%和1.72%~22.41%,而有效磷和铵态氮含量随生物质炭添加量的增加呈先增大后减小趋势,分别在生物质炭添加量为10t/hm2和30t/hm2时达到最大值。随生物质炭添加量的增加,土壤有效态Cd和有效态Pb含量均呈降低趋势,而土壤有效态As含量呈先增加后减少的趋势,三者均在生物质炭添加量为40t/hm2时达到最小值。土壤微生物生物量碳、氮和微生物商随生物质炭添加量的增加均呈先升高后降低的趋势,均在生物质炭添加量为20t/hm2时达到最大值。相关分析表明,生物质炭添加量分别与土壤有效态Cd和Pb含量之间呈极显著负相关(P0.01);通径分析表明,生物质炭主要是通过直接作用影响土壤有效态Cd含量,而土壤pH、EC、有机质、微生物生物量碳、氮和有效磷主要是通过间接作用影响土壤有效态Cd含量。因此,添加适量生物质炭不仅可以改善土壤重金属污染现状和土壤理化性状,提高土壤养分含量,还可以改良土壤生物学性质,增加土壤微生物量。研究结果可为提高稻田土壤肥力和改善土壤重金属污染状况提供科学依据。 相似文献
9.
油菜秸秆生物质炭对紫色土有机碳矿化和累积效应的影响 总被引：1，自引：0，他引：1
《水土保持学报》2015,(6)
采用室内模拟培养试验,以油菜秸秆为对比,分析油菜秸秆生物质炭的施用对紫色土有机碳矿化的影响。在培养试验中,设置0.25%,0.5%和1%3个不同秸秆/土壤质量比的油菜秸秆还田培养处理,依次标记为J_1,J_2和J_3;同时,设置3个不同油菜秸秆生物质炭添加量的培养处理,其生物质炭添加量分别为J_1,J_2和J_3处理中添加的等量油菜秸秆在600℃下制成的生物质炭量,依次标记为S_1,S_2和S_3,所有处理置于25℃下避光培养56d。在培养期内,各处理中土壤有机碳(SOC)矿化速率随时间的变化符合乘幂函数。添加生物质炭处理的SOC累积矿化量、矿化强度和易分解有机碳占总有机碳含量的比例(Ca/CSOC)显著低于与其对应的油菜秸秆处理(P0.05),表明油菜秸秆经过热解制成生物质炭后可显著提高其在土壤中的稳定性。各添加生物质炭处理的SOC累积矿化量、矿化强度、Ca/CSOC和难分解有机碳占总有机碳含量的比例(Cs/CSOC)与对照(无外源碳添加)之间无显著性差异,添加生物质炭几乎不影响紫色土有机碳的分解。另外,S_1处理中外源碳的表观残留率显著高于其它培养处理,而S_2和S_3处理中外源碳的表观残留率则显著低于与其对应的油菜秸秆处理(J_2和J_3)(P0.05)。这表明在低量油菜秸秆还田时,将其制成生物质炭还田比直接还田更利于紫色土有机碳的积累。 相似文献
10.
秸秆与生物质炭施用对土壤温室气体排放的影响差异 总被引：1，自引：4，他引：1
采用室内培养试验,向土壤中添加小麦秸秆和不同量生物质炭,同时比较探究秸秆与生物质炭施用对土壤温室气体排放及微生物活性的影响差异。试验共设5个处理:土壤(S)、土壤+1%小麦秸秆(WT)、土壤+1%生物质炭(BC1)、土壤+2%生物质炭(BC2)和土壤+4%生物质炭(BC4)。在培养期内,施秸秆处理土壤CO2排放量比对照处理S显著增加约12.60%~2005.63%,而施生物质炭处理降低约51.49%~97.93%。施秸秆处理的温室气体增温潜势(GWP)是对照处理S的1.12~19.24倍,而施生物质炭处理,即处理BC1、BC2和BC4的GWP分别降低了0.27%~64.06%,15.78%~94.01%和29.43%~92.28%。小麦秸秆施用会明显增加土壤温室气体排放,增加温室效应;而添加生物质炭对土壤CO2、N2O排放表现出一定的抑制作用,并明显减弱温室气体增温潜势,即生物质炭能明显减弱温室效应。添加小麦秸秆促进土壤微生物生物量碳的增加,提高FDA水解酶、脲酶、过氧化氢酶、磷酸酶活性;生物质炭施用一段时间后对土壤过氧化氢酶活性表现为显著激活作用。 相似文献
11.
Short-term biochar-induced increase in soil CO2 release is both biotically and abiotically mediated 总被引：2，自引：0，他引：2
The application of biochar to soil has been shown to cause an apparent increase in soil respiration. In this study we investigated the mechanistic basis of this response. We hypothesized that increased CO2 efflux could occur by: (1) Biochar-induced changes in soil physical properties (bulk density, porosity, moisture content); (2) The biological breakdown of organic carbon (C) released from the biochar; (3) The abiotic release of inorganic C contained in the biochar; (4) A biochar-induced stimulation of decomposition of native soil organic matter (SOM) which could occur both biotically or abiotically; (5) The intrinsic biological activity of the biochar results in the liberation of CO2. Our results show that most of the extra CO2 produced after biochar addition to soil came from the equal breakdown of organic C and the release of inorganic C contained in the biochar. Using long-term 14C-labelled SOM, we show that biochar repressed native SOM breakdown, counteracting the release of CO2 from the biochar. A range of mechanisms to describe this negative priming response is presented. Although biochar-induced significant changes in the physical characteristics of the soil, overall this made no contribution to changes in soil respiration. Similarly, the evidence from our study suggests that changes in soluble polyphenols do not help explain the respiration response. In summary, biochar induced a net release of CO2 from the soil; however, this C loss was very small relative to the amount of C stored within the biochar itself (ca. 0.1%). This short-term C release should therefore not compromise its ability to contribute to long-term C sequestration in soil environments. 相似文献
12.
Recent studies have shown both increased (positive priming) and decreased (negative priming) mineralisation of native soil organic carbon (SOC) with biochar addition. However, there is only limited understanding of biochar priming effects and its C mineralisation in contrasting soils at different temperatures, particularly over a longer period. To address this knowledge gap, two wood biochars (450 and 550 °C; δ13C −36.4‰) were incubated in four soils (Inceptisol, Entisol, Oxisol and Vertisol; δ13C −17.3 to −28.2‰) at 20, 40 and 60 °C in the laboratory. The proportions of biochar- and soil-derived CO2–C were quantified using a two-pool C-isotopic model.Both biochars caused mainly positive priming of native SOC (up to +47 mg CO2–C g−1 SOC) in the Inceptisol and negative priming (up to −22 mg CO2–C g−1 SOC) in the other soils, which increased with increasing temperature from 20 to 40 °C. In general, positive or no priming occurred during the first few months, which remained positive in the Inceptisol, but shifted to negative priming with time in the other soils. The 550 °C biochar (cf. 450 °C) caused smaller positive priming in the Inceptisol or greater negative priming in the Entisol, Oxisol and Vertisol at 20 and 40 °C. At 60 °C, biochar caused positive priming of native SOC only in the first 6 months in the Inceptisol. Whereas, in the other soils, the native SOC mineralisation was increased (Entisol and Oxisol) and decreased (Vertisol) only after 6 months, relative to the control. At 20 °C, the mean residence time (MRT) of 450 °C and 550 °C biochars in the four soils ranged from 341 to 454 and 732−1061 years, respectively. At 40 and 60 °C, the MRT of both 450 °C biochar (25−134 years) and 550 °C biochar (93−451 years) decreased substantially across the four soils. Our results show that biochar causes positive priming in the clay-poor soil (Inceptisol) and negative priming in the clay-rich soils, particularly with biochar ageing at a higher incubation temperature (e.g. 40 °C) and for a high-temperature (550 °C) biochar. Furthermore, the 550 °C wood biochar has been shown to persist in soil over a century or more even at elevated temperatures (40 or 60 °C). 相似文献
13.
外源铅胁迫对不同土壤上水稻生长及铅形态的影响 总被引：1，自引：0，他引：1
采用温室水稻盆栽试验研究2种土壤上水稻铅的生物有效性及土壤铅形态的变化。结果表明:铅对2种土壤水稻干物重和籽粒重量的影响表现为,随铅处理浓度升高,水稻干物重和籽粒重量明显下降。黄红壤上种植的水稻干物重和籽粒重量高于青紫泥。不同铅处理下水稻各器官铅含量表现为根>茎>叶>壳>籽粒。2种土壤上NH4OAc提取的有效态铅含量与外源铅的量呈显著正相关。随外源土壤铅含量增加土壤pH显著下降。随土壤铅含量增加土壤铅的生物有效性增强,水稻对铅的吸收明显增加,水稻可食部的铅含量升高。采用连续提取法分析了土壤铅的形态,结果表明,青紫泥铁锰氧化态和有机态的铅含量高于黄红壤,水溶态、交换态和碳酸盐态含量低于黄红壤。铅在黄红壤上的移动性较青紫泥高。 相似文献
14.
Biochar was prepared using a low temperature pyrolysis method from nine plant materials including non‐leguminous straw from canola, wheat, corn, rice and rice hull and leguminous straw from soybean, peanut, faba bean and mung bean. Soil pH increased during incubation of the soil with all nine biochar samples added at 10 g/kg. The biochar from legume materials resulted in greater increases in soil pH than from non‐legume materials. The addition of biochar also increased exchangeable base cations, effective cation exchange capacity, and base saturation, whereas soil exchangeable Al and exchangeable acidity decreased as expected. The liming effects of the biochar samples on soil acidity correlated with alkalinity with a close linear correlation between soil pH and biochar alkalinity (R2 = 0.95). Therefore, biochar alkalinity is a key factor in controlling the liming effect on acid soils. The incorporation of biochar from crop residues, especially from leguminous plants, can both correct soil acidity and improve soil fertility. 相似文献
15.
Paddy fields are one of the largest anthropogenic sources of global CH4 emission. A decrease in paddy CH4 emission can contribute significantly towards the control of global warming. Recent studies have demonstrated that the application of biochar in paddy soils has such a capability, but its underlying mechanism has yet to be elucidated. In this investigation, we studied CH4 emission, methanogenic archaeal, as well as methanotrophic proteobacterial communities, from microcosms derived from two paddy soils, Inceptisol and Ultisol. Both soils were amended with biochar at different pyrolysis temperatures (300 °C, 400 °C and 500 °C) at field condition. The soil CH4 flux was monitored across whole rice season in 2010; the functional guilds communities were analyzed by PCR–DGGE and real-time quantitative PCR (qPCR). It is found that paddy CH4 emissions significantly decreased under biochar amendments, which, interestingly, didn't result from the inhibition of methanogenic archaeal growth. qPCR further revealed that biochar amendments (1) increased methanotrophic proteobacterial abundances significantly, and (2) decreased the ratios of methanogenic to methanotrophic abundances greatly. These results shed insight on the underlying mechanism of how biochar decreases paddy CH4 emission. This knowledge can be applied to develop a more effective greenhouse gas mitigation process for paddy fields. 相似文献
16.
秸秆及其生物炭对土壤碳库管理指数及有机碳矿化的影响 总被引：6，自引：0，他引：6
以河南省粮食主产区壤质潮土和砂土为研究对象,通过盆栽试验和室内恒温培养试验,研究了生物炭与不同腐殖化程度的传统有机物料(秸秆和腐熟鸡粪)单施及配施对壤质潮土和砂土有机碳储量、活性及碳库管理指数的影响,并进一步比较了小麦秸秆直接还田和制炭还田对土壤有机碳矿化的影响,以及生物炭对土壤原有有机碳矿化的调控作用。结果表明:相同添加量下,生物炭对土壤有机碳含量的提升效果优于秸秆和腐熟鸡粪,在壤质潮土和砂土上分别较对照提升了63.15%和115.62%。另外,生物炭显著增加了土壤稳态碳含量和土壤碳库指数(CPI),但降低了土壤碳素有效率(SC)和碳库活度指数(AI),对土壤易氧化有机碳(POXC)和碳库管理指数(CMPI)无显著影响,添加秸秆显著增加了2种土壤POXC含量、基础呼吸和CPMI。进一步通过室内恒温培养试验发现,秸秆可在培养前期(0～37天)大幅度提升2种类型土壤有机碳矿化速率和累积矿化量,秸秆制炭还田对土壤有机碳矿化无显著影响。此外生物炭对土壤原有有机碳矿化的调控作用受其施用量、外源活性有机碳输入和土壤类型的影响,高量生物炭(2%)对非秸秆还田土壤有机碳矿化表现出较强的负激发效应,而低量生物炭(0.55%)对秸秆还田土壤有机碳矿化表现出较明显的负激发效应。因此,从"固碳减排"角度考虑,秸秆制炭还田是更合理的利用方式,且应根据土壤施肥管理措施和土壤类型考虑生物炭的施用量,添加质量比为2%的生物炭可显著抑制土壤原有有机碳矿化,降低CO_2排放,但应避开秸秆快速腐解期施用。 相似文献
17.
L. Wang C. R. Butterly Y. Wang H. M. S. K. Herath Y. G. Xi X. J. Xiao 《Soil Use and Management》2014,30(1):119-128
Strongly acidic soil (e.g. pH < 5.0) is detrimental to tea productivity and quality. Wheat, rice and peanut biochar produced at low temperature (max 300 °C) and differing in alkalinity content were incorporated into Xuan‐cheng (Ultisol; initial pHsoil/water = 1/2.5 4.12) and Ying‐tan soil (Ultisol; initial pH soil/water = 1/2.5 4.75) at 10 and 20 g/kg (w/w) to quantify their liming effect and evaluate their effectiveness for acidity amelioration of tea garden soils. After a 65‐day incubation at 25 °C, biochar application significantly (P < 0.05) increased soil pH and exchangeable cations and reduced Al saturation of both tea soils. Association of H+ ions with biochar and decarboxylation processes was likely to be the main factor neutralizing soil acidity. Further, biochar application reduced acidity production from the N cycle. Significant (P < 0.05) increases in exchangeable cations and reductions in exchangeable acidity and Al saturation were observed as the rate of biochar increased, but there were no further effects on soil pH. The lack of change in soil pH at the higher biochar rate may be due to the displacement of exchangeable acidity and the high buffering capacity of biochar, thereby retarding a further liming effect. Hence, a significant linear correlation between reduced exchangeable acidity and alkalinity balance was found in biochar‐amended soils (P < 0.05). Low‐temperature biochar of crop residues is suggested as a potential amendment to ameliorate acidic tea garden soils. 相似文献
18.
为探讨生物质炭对红壤性水稻土中镉(Cd)元素吸附解吸特性的影响,采用一次平衡法研究添加生物质炭后Cd2+在红壤性水稻土中的吸附动力学、等温吸附和解吸过程。结果表明:施用CK(0t/hm^2)、A10(10t/hm^2)、A20(20t/hm^2)、A30(30t/hm^2)和A40(40t/hm^2)生物质炭后,红壤性水稻土对Cd2+的吸附过程是以化学吸附为主、非均匀的多表面吸附。施用CK(0t/hm^2)、A10(10t/h2)、A20(20t/hm^2)、A30(30t/hm^2)和A40(40t/hm^2)生物质炭处理的最大吸附量和最大解吸量分别为2933~3346mg/kg和171~192mg/kg。添加生物质炭可以提高红壤性水稻土对Cd2+的吸附固持能力,同时增强土壤对外源Cd2+的缓冲能力。生物质炭添加量对红壤性水稻土的吸附解吸能力的改良效果具体表现为:A30>A40>A20>A10。高剂量的生物质炭处理使土壤吸附点位饱和,生物质炭吸附能力相对降低。因此,添加30t/hm^2生物质炭是一种有效预防和治理红壤性水稻土镉污染的措施。 相似文献
19.
S. Bek 《Biology and Fertility of Soils》1994,17(1):21-26
Soil was amended with 14C-labelled unripe straw only (C:N ratio ca. 20), with 14C-labelled unripe straw plus unlabelled ripe straw (C:N ratio ca. 100) or with 14C-labelled unripe straw plus glucose. Half the samples with 14C-labelled straw and half the samples with 14C-labelled plus unlabelled straw were cropped with rape plants. A decreased rate of mineralization of the 14C-labelled straw was found in the planted soil compared with the unplanted soil. The reduction was most profound in the soil amended with both labelled and unlabelled straw, indicating that at least part of the reduction was due to competition between plants and microorganisms for mineral N. No other explanations for the decrease in mineralization in the presence of plants were found. The soil amended with glucose which simulated the effect of root exudates showed an increased rate of mineralization. Therefore, the reduction in the presence of plants was probably not due to microbial use of the rhizodeposition in favour of the labelled straw. Only a minor part of the reduction was apparently due to uptake of labelled C by the plant, as only small amounts were found in the roots and shoots at harvest. The difference in 14C mineralization between treatments was not reflected in the number of bacteria in the soil at harvest. The number of bacteria, which was determined by plate counts and direct microscopy, was the same in all the soils, rhizosphere soils as well as bulk soils. 相似文献
20.
J. M. Novak K. A. Spokas K. B. Cantrell K. S. Ro D. W. Watts B. Glaz W. J. Busscher P. G. Hunt 《Soil Use and Management》2014,30(2):175-181
Biochar and hydrochars (HC) are emerging soil fertility amendments; however, their ability to improve fertility levels in soils possessing vastly different pedogenic characteristics has not been well investigated. In this study, several plant and manure biochars and two blended HC applied at 3.84 g/kg (ca.10 t/ha) were incubated in pots containing a highly fertile‐Mollisol (Waukegan series; Sandy‐skeletal, mixed, superactive, mesic Typic Hapludoll) and an infertile Entisol (Margate series; Siliceous, hyperthermic, Mollic Psammaquent). During the 124–125 day laboratory incubations, pots were leached four times with deionized H2O with the leachates analysed for the concentrations of dissolved phosphorus (DP) and potassium (DK). After the incubations, both soils were analysed for fertility characteristics (i.e. pH, cation‐exchange capacity (CEC), and extractable P and K). In both soils after biochar additions, there were mixed pH and CEC responses. Both the Mollisol and Entisol treated with swine solid biochar had greater plant extractable P and K contents, which was reflective of the elevated P and K contents in the swine solid biochar. However, most biochars and HC additions to the Mollisol and Entisol had minimal impact on soil fertility characteristics indicating a low direct fertilization potential. These nutrient contents could be altered through feedstock blending to target a particular fertilizer requirement. 相似文献