生物炭对不同酸化水平稻田土壤性质和重金属Cu、Cd有效性影响

针对南方稻田土壤酸化严重,导致养分流失有毒重金属活化,严重影响稻米质量安全的重大现实问题。以水稻秸秆和谷壳等农业废弃物为原料制备生物炭(分别记为RSC和RHC),研究不同原料生物炭对酸化土壤改良及其对重金属有效性的影响。设置3个生物炭用量(0,20,50 g/kg,分别记为CK、C1、C2),4种土壤酸化水平(pH 4.01,4.25,4.33,4.58,分别记为L1、L2、L3、L4),生物炭与重金属污染土壤共同培养60天后测定土壤pH、全氮、有机质、有效磷、速效钾和有效态Cu、Cd含量。结果表明:RSC对酸化土壤pH的改良效果明显优于RHC,且施炭量越高提高幅度越大,RSC的C2处理使4种酸度水平的土壤pH分别提高了0.68,0.97,1.29,1.71个单位。2种生物炭均能提高土壤的全氮、有效磷、速效钾和有机质含量,其中各施炭处理有机质显著提高,尤以速效钾的增幅最为显著,RSC对4种养分的提高均优于RHC。RHC对土壤有效态Cu含量无显著影响;RSC的C2较C1处理更能降低土壤中有效态Cu含量,使4种酸度水平的土壤分别降低了13.62%,6.57%,4.36%,7.88%。RHC处理的L3、L4土壤中有效态Cd含量显著降低,最大分别降低了13.79%,19.23%。RSC使4种酸度土壤有效态Cd含量最大分别降低了20.00%,25.81%,20.69%,19.23%。相关分析表明,土壤pH与有效态重金属含量呈显著负相关关系。水稻秸秆炭用于改良酸化土壤、降低重金属Cu和Cd有效性的效果更佳,且降低污染土壤中Cd的有效性较Cu好;生物炭对酸化程度越低的土壤pH和有效磷含量的提高以及有效态Cd含量的降低效果较好,而有效态Cu含量的降低效果则在酸化程度越高的土壤中表现更佳;土壤pH是生物炭调控重金属Cu、Cd有效性的主要影响因素。     

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

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。     

生物炭对铜矿区排土场污染土壤理化性质和重金属形态的影响

为了探讨在重金属胁迫下,不同用量(0,1%,2%,4%)生物炭对土壤pH、有机碳、全氮、全磷以及重金属形态的影响,以铜矿区排土场污染土壤为研究对象,开展室内盆钵试验。结果表明：与对照K相比,在不同剂量生物炭处理下,土壤pH、有机碳、全N和全P增幅分别为3.5%～23.0%,5.6%～13.2%,2.9%～6.8%和3.4%～9.5%,酸溶态Cd, Pb, Cu和Zn含量降幅分别为65.5%～71.2%,49.9%～71.5%,34.6%～50.6%和45.3%～52.1%,可还原态Cd, Pb, Cu和Zn含量降幅分别为71.5%～74.3%,44.4%～63.6%,38.5%～57.8%和29.1～39.1%,可氧化态Cd含量降幅为15.6%～36.9%,可氧化态Pb, Cu和Zn含量增幅分别为16.9%～20.5%、3.9%～26.0%和18.8%～55.9%,残渣态Cd, Pb, Cu和Zn含量增幅分别为42.4%～44.2%,11.0%～23.5%,15.0%～37.9%和20.0%～41.9%。添加生物炭可以提高土壤pH,增加土壤有机碳和全氮含量,对土壤全磷含量也略有增加,但...     

施用生物炭对红壤性水稻土重金属钝化与土壤肥力的影响

通过田间小区试验,分析了不同用量的生物炭处理下(0,10,20,30,40 t/hm^2)0-17,17-29 cm土层土壤的理化性质、重金属钝化及酶活性的影响。采用IFI(土壤肥力综合质量指数)评价了土壤肥力状况。结果表明:施用生物炭可以改善红壤的理化性状,降低土壤容重,提高土壤的孔隙度、饱和含水量、pH、CEC、有机质、有效磷、铵态氮和全氮及DOC含量;同时提高土壤脲酶、过氧化氢酶和蔗糖酶活性。土壤有效态Cd和Pb含量均随生物炭施用量的增加而减少;而有效态As含量则随生物炭施用量的增加呈先增后减的趋势,三者均在生物炭施用量为40 t/hm^2时为最小值。利用IFI对土壤肥力综合质量进行评价可知,在不同生物炭用量条件下土壤肥力综合质量指数依次为A30>A40>A20>A10>CK,相应的土壤肥力综合质量指数分别为0.64,0.62,0.57,0.47,0.44。评价结果表明在生物炭施用量为30 t/hm^2时,红壤的肥力改良效果最佳。因此,采用适量的生物炭可修复重金属对红壤性水稻土的污染,并改善土壤肥力状况。     

冻融-化学淋洗法协同修复重金属Cd和Pb污染黏性土

针对质地黏重、低渗透性黏性土的淋洗效率低下,该文提出冻融协同化学淋洗的修复方案,并以某冶炼厂受Cd、Pb污染场地黏性土为研究对象,选用乙二胺四乙酸二钠(ethylene diaminetetraacetic acid disodium salt,EDTA)为淋洗剂,进行了冻融-淋洗土柱的实证试验。结果表明,土体的反复冻融(冻胀-吸水、融沉-排水)破坏土体颗粒原有结构,有助于淋洗液与污染物充分接触,淋洗效果明显,经7次冻融后,Cd、Pb去除率分别达到77.24%、37.78%。采用改进的BCR(European Communities Bureau of Reference)连续提取法分析了土柱中Cd、Pb的赋存特征,经7次冻融后,土壤中弱酸提取态、可还原态、残渣态结合的Cd质量分数较淋洗前分别降低了41.46%、63.02%、26.33%,而土壤中可还原态和残渣态结合的Pb质量分数分别降低了32.32%、67.36%。冻融协同化学淋洗修复技术的淋洗剂用量远小于传统淋洗法,为今后利用寒区冻融交替现象,大规模对季冻区重金属污染土壤的异位修复提供了新的思路。     

广东省酸性硫酸盐水稻土作物产量的主要限制因子分析

【目的】酸性硫酸盐水稻土(ASPS,简称反酸田)因强酸严重限制水稻生长,其产量远低于全国平均水平,是我国南方典型中低产田。为了进一步提高反酸田的水稻产量,需要对反酸田土壤的主要限制因子进行分析,以更好地对症下药,有效合理地改良土壤。本研究调查了不同产量水平下酸性硫酸盐水稻田的理化性状,探讨限制水稻生长的关键土壤化学因子,为反酸田的改良提供理论依据。【方法】 根据前期调查结果,选择3种产量水平(4500、 3000、 1500 kg/hm2)的代表性反酸田为研究对象,并以因强酸而撂荒的水稻田作为对照,于2013年6月28日在不同采样点各采集8个耕作层土壤样品,测定其有机质, 酸度, 氮、 磷、 钾养分以及微量元素含量等化学性状指标,比较不同田块间各种化学性状的差异,并通过相关分析、 主成分分析探讨影响反酸田水稻生长的关键土壤化学因子。【结果】反酸田的酸度水平极高,其pH值在3.0~4.0之间,水溶性酸、 交换性酸和吸持性酸含量分别达到0.6~5.6、 2.7~6.3和1.3~14.1 cmol/kg; 不同调查田块的酸度水平差异显著,高产田块的各种形态酸含量均显著低于低产田块,尤以水溶性酸和吸持性酸的差异更明显。随产量水平的降低,反酸田的有效磷、 速效钾含量显著降低,而水溶性硫、 交换性硫、 交换性锰、 交换性铝含量显著提高,交换性钙、 交换性锌、 交换性铜含量差异不显著,反映出缺磷、 缺钾、 硫酸盐含量过高、 铝毒、 锰毒显著限制了反酸田的水稻产量。相关分析表明,土壤有效磷、 速效钾与各种形态酸含量和硫酸盐含量显著负相关,而交换性钙、 锰、 铜、 锌、 铝与各种形态酸含量和硫酸盐含量显著正相关,表明反酸田水稻产量的主要限制化学因子受土壤酸含量及硫酸盐含量的水平影响。主成分分析表明,水溶性硫、 交换性硫、 交换性铝、 交换性酸、 交换性锰、 水溶性酸、 吸持性酸、 pH值、 有效磷、 速效钾等组成一个相对均质的变量群组,概括了64.99%的不同产量水平下反酸田理化性状的总变异度,为影响反酸田产量的主要土壤化学因子。其中水溶性硫、 交换性硫、 交换性铝、 交换性酸、 交换性锰、 水溶性酸、 吸持性酸为影响反酸田产量水平的负效应变量,而pH值、 有效磷、 速效钾为影响反酸田产量水平的正效应变量。【结论】硫酸根含量过高、 铝毒、 锰毒、 酸毒、 缺磷、 缺钾是限制反酸田产量的主要土壤化学因子。酸、 硫酸盐是反酸田的发育产物,是影响广东省反酸田水稻生长的原生及根本性障碍因素,而铝毒、 锰毒、 缺磷、 缺钾等是因土壤中酸、 硫酸盐含量较高时引起的次生障碍因素。因此,在反酸田的改良过程中需以减缓黄铁矿氧化、 促进黄钾铁矾水解,降低耕层土壤酸、 硫酸盐含量为主要目标。     

菌渣生物炭对镉污染土壤性质及小白菜吸收镉的影响

为探讨以菌渣为原料制备的生物炭修复重金属镉污染土壤的可行性。采用盆栽试验,以香菇菌渣生物炭(SC)和平菇菌渣生物炭(PC)为研究对象,设置0.5%,1%,2%的生物炭施用量(w/w,%),研究其对镉污染土壤理化性质、土壤各形态镉分布、小白菜生长及镉吸收的影响。结果表明:施用SC和PC均能显著提高土壤pH和有机质(SOM)含量。与对照相比,2%的生物炭处理,土壤pH分别提高1.05和1.10个单位,SOM含量分别提高80.6%和61.2%。施用SC和PC使土壤可交换态镉降低,而提高残渣态镉含量。相关分析表明,土壤可交换态镉与pH、SOM和蔗糖酶呈显著负相关。与对照相比,2%处理下SC和PC显著降低小白菜镉含量,分别降低57.5%和54.1%;1%用量下小白菜产量分别提高53.4%和41.6%,表明高投加量菌渣生物炭对小白菜生长有不利影响。总体看来,SC和PC均有利于改善土壤性质,减轻镉对植物的毒害,促进小白菜生长。     

The application of biochar on soil acidity and other physico‐chemical properties of soils in southern Ethiopia

The aim of this research was to investigate the effect of biochar amendment on soil acidity and other physico‐chemical properties of soil in Southern Ethiopia using a field experiment of three treatments: (1) biochar made of corn cobs, (2) biochar made of chopped Lantana camara stem, and (3) biochar made of Eucalyptus globulus feedstock and a control, in which neither of the biochar was used. Each treatment had three levels of 6, 12 and 18 t ha⁻¹. The experiment was setup with RCBD in a factorial arrangement with three replications. In this regard, a total of 36 plots (each 2 × 2 m size) were applied with three replications to the depth of 0–15cm. From these 36 plots, composite soil samples were collected to the depth of 0–30 cm and analyzed for bulk density, total porosity, pH, soil organic carbon, total nitrogen, available phosphorus, potassium, and exchangeable acidity using standard procedures before and after biochar application. Two‐way ANOVA was also used to analyze the impact of the biochars on soil acidity and other properties. For the treatments that had significant effects, a mean separation was made using Least Significance Difference (LSD) test. The results showed the application of biochar significantly reduced, soil bulk density and exchangeable acidity when compared with a control (p < 0.05). Moreover, the total soil porosity, soil pH, total nitrogen, soil organic carbon, available phosphorus, and potassium were significantly increased in the soil. From among applied biochar treatments, Lantana camara applied at the level of 18 t ha⁻¹ had a higher impact in changing soil physico‐chemical properties. In general, the study suggests that the soil acidity can be reduced by applying biochar as it can amend other soil physico‐chemical properties.     

利用土壤改良剂固定污染土壤中铅、镉的研究进展

Since the inception of industrial revolution, metal refining plants using pyrometallurgical processes have generated the prodigious emissions of lead (Pb) and cadmium (Cd). As the core target of such pollutants, a large number of soils are nowadays contaminated over widespread areas, posing a great threat to public health worldwide. Unlike organic pollutants, Pb and Cd do not undergo chemical or microbial breakdown and stay likely in site for longer duration after their release. Immobilization is an in-situ remediation technique that uses cost-effective soil amendments to reduce Pb and Cd availability in the contaminated soils. The Pb and Cd contamination in the soil environment is reviewed with focus on source enrichment, speciation and associated health risks, and immobilization options using various soil amendments. Commonly applied and emerging cost-effective soil amendments for Pb and Cd immobilization include phosphate compounds, liming, animal manure, biosolids, metal oxides, and biochar. These immobilizing agents could reduce the transfer of metal pollutants or residues to food web (plant uptake and leaching to subsurface water) and their long-term sustainability in heavy metal fixation needs further assessment.     

土壤调理剂对土壤理化性质及甘蓝生理特性的影响

试验研究了土壤调理剂对土壤结构性质和甘蓝根系活力、光合指标的影响.结果表明,施用调理剂后,处理两次、处理一次分别使20 cm和30 cm土层的容重下降7.3%、1.9%和4.6%、1.3%,孔隙度分别提高9.3%、2.8%和5.9%、1.9%;与对照相比,处理两次后的阳离子交换量在0～27 cm、27～45 cm土层分别增加5.7%和10.9%;甘蓝的根系活力,处理与对照相比达到1%的显著差异水平;改变了Pn的光合日变化曲线,提高了甘蓝对光强的适应能力,光合能力加强.     

机械化整地方式对低洼水田土壤理化性质及水稻产量影响

低洼地是黑龙江省分布在三江平原地区的地势较低的一类耕地土壤,由于地势低、易受渍涝影响,土壤生产力低,作物产量低而不稳,提高这类土壤生产力对农业生产尤为重要。该文以低洼地典型的一类土壤沼泽土为供试土壤,采用大田对比试验的方法,开展旋耕、深松、深翻、深松鼠洞4种不同机械化整地方式对低洼水田理化性质改良效果的研究。结果表明:与常规旋耕比,深松、深翻机械整地可以使0～30cm土层土壤含水率降低10.03%～27.23%,土壤透水性提高,土壤容重增加0.05～0.18 g/cm3、增幅为6.60%～16.98%,差异显著,深松、深翻使土壤硬度提高,总孔隙降低幅度3.16%～11.92%,滞水现象得到改善,深松鼠洞机械整地效果与旋耕比差异不明显;在排水晒田后,土壤温度明显上升,平均每天增加1～2℃,深松效果好于深翻,土壤氮素供应强度增加;深松整地水稻产量连年增加,第1年增产4.21%,第2年增产10.46%,达到显著水平,深翻对水稻产量无影响,第2年有增加趋势,差异不显著,深松鼠洞整地第1年和第2年水稻产量与旋耕比无差异显著,在深松鼠洞改土技术及机械研发上要进行新的改进与探讨。     

盐化草甸土和黑土型水田土壤连续深耕改土效果

为明确深耕在不同类型水田土壤上的改土效果及对水稻产量的影响,该研究应用自主研发水田深耕犁,在黑土和盐化草甸土上开展深翻、浅翻与旋耕对比试验研究。结果表明,深耕在不同类型土壤上对水稻产量及土壤理化性质影响存在差异:1)黑土深翻区增产7.28%~8.37%,浅翻区增产6.02%~7.72%,盐化草甸土深翻区和浅翻区与旋耕相比第1年水稻产量差异不大;第2年减产9.96%~11.03%;2)翻耕促进黑土土壤养分均一化,耕作层土壤养分降低不明显,土层间养分含量差异变小,盐化草甸土深耕后造成表层养分浓度降低,0~20 cm土层浅翻区和深翻区土壤有机质与对照相比分别下降4.57和6.68 g/kg,全氮分别下降0.24和0.29 g/kg,碱解氮0~10 cm土层分别比对照降低2.31和11.52 mg/kg,pH值明显增加,0~30cm土层交换性Na+浓度增加;3)与对照相比,浅翻和深翻降低了黑土下层土固相比率、容重,提高土壤通气、透水性,10~20 cm土层土壤固相比率比对照分别降低4.23%和3.23%,土壤容重下降0.09 g/cm3和0.08 g/cm3,通气系数分别提高3.04倍和3.42倍,透水系数提高1.71倍和1.14倍;20~30 cm土层深翻区土壤固相比率降低1.86%,通气系数和饱和透水系数比对照提高0.86倍和1.87倍;盐化草甸土浅翻区和深翻区均有增加下层土固相率和容重,降低通气、透水性的趋势。盐化草甸土水田不适合深耕,黑土型水田土壤深耕可改善土壤理化性质,提高水稻产量。     

红壤稻田土壤理化及生物学性状的动态变化特征

Rice production plays a crucial role in the food supply of China and a better understanding of the changes in paddy soil fertility and the management effects is of practical importance for increasing rice productivity. In this study, field sampling in a typical red soil region of subtropical China, Jiangxi Province, was used to observe changes in the soil physical, chemical, and biological properties in a cultivation chronosequence of paddy fields. After cultivation, clay (< 0.002 mm) content in the soil, which was 39% in the original uncultivated wasteland, decreased, to 17% in the 80-year paddy field, while silt (0.02--0.002 mm) content increased. Additionally, macroporosity increased and pore shapes became more homogeneous. Soil Ph generally increased. Soil organic C and total N content of the 0-10 cm layer increased from 4.58 and 0.39 g kg-1 to 19.6 and 1.62 g kg-1, respectively in the paddy fields after 30-year cultivation and then remained stable. Soil total P content increased from 0.5 to 1.3 g kg-1 after 3 years of rice cultivation, indicating that application of phosphate fertilizer could accelerate phosphorous accumulation in the soil. Total K content in the 0--10 cm soil layer for the 80-year paddy fields decreased by 28% compared to that of the uncultivated wasteland land. Total Fe and free Fe contents declined with years of cultivation. The bacterial population increased and urease activity noticeably intensified after years of cultivation. In this chronosequence it appeared that it took 30 years to increase soil fertility to a relatively constant value that was seen after 80 years of cultivation.     

Effect of soil microorganisms on the sorption of zinc and lead compounds by goethite

The objectives of this study were (1) to determine the effect of microorganisms during in‐vitro incubation on the amount of Zn and Pb from solution retained on goethite precipitated as coatings on a sand matrix and (2) to evaluate accumulation of heavy metals in the biomass of soil microorganisms in the fresh soil samples using an extractive approach. A mixture of colonies of cultivated microorganisms extracted from a Haplic Luvisol (Russia) and an Antropi‐urbic Regosol (Germany) were used to prepare the cell and the microbial‐debris suspensions. The concentrations of Zn and Pb in the studied solutions supplied with microbial suspensions and/or goethite coated sand were 0.1 mM (130.8 and 414 mg kg^–1 of sand, respectively). Exchangeable forms of metals were determined by extraction with 10 mL of 1.0 M KNO₃. Nonexchangeable forms of Zn and Pb were recovered using 40 mL of 0.3 M NH₂OH‐HCl in 1 M HNO₃. Concentrations of Pb increased in the solutions and decreased on the surface of the Fe‐mineral due to living microorganisms. In comparison to incubation of heavy‐metal solutions with goethite only, the absolute concentrations of nonexchangeable forms of metal were reduced by microbial suspension to a greater extent than those of the exchangeable forms, whereas the relative content of both fractions decreased by a factor of almost two. Sorption of Pb by goethite was inversely correlated with the concentration of organic C in the solution. Microorganisms clearly influenced the Zn sorption by goethite at concentrations of C_org > 400 mg L^–1. The amount of Zn retained was decreased primarily due to decreasing Zn portions in the exchangeable fraction. Microbial debris prepared by autoclaving reduced the Pb sorption by goethite similar to the results for living cells. Living microorganisms accumulated more Zn than did microbial debris. The data of this paper show that a direct determination of heavy‐metal accumulation in soil microorganisms by extraction with 2.0 M KCl as well as by extraction with 1 M CH₃COONH₄ at the natural pH of the soils after chloroform fumigation of fresh soils samples with different concentrations of organic C was not possible.     

阻隔主要外源输入重金属对土壤-水稻系统中镉铅累积的影响

土壤-水稻系统中重金属输入输出调控对稻田污染防治和水稻安全生产具有重要意义。该文研究稻草移除、截断大气沉降、清洁水灌溉等调控措施对稻田土壤-水稻系统中重金属Cd和Pb的累积与运移特征的影响。结果表明,稻草移除、截断大气沉降和清洁水灌溉均能明显降低污染土壤中有效态重金属含量和水稻中重金属的累积量。与稻草还田对照处理相比,除种植早稻后的土壤有效态Pb含量外,稻草移除处理下土壤中有效态Cd、Pb含量均略有降低,且在该处理下,早稻糙米中Pb含量与晚稻糙米中Cd、Pb含量显著降低,降幅分别为3.6%、10.4%和32.4%;稻草移除+截断大气沉降处理下,土壤中有效态Cd、Pb含量均不同程度地下降,种植晚稻后的土壤有效态Pb含量显著降低,除早稻的根和糙米中Cd含量外,其余早晚稻水稻各部位Cd、Pb含量均显著降低,水稻根和茎叶Cd、Pb含量平均降幅分别为32.8%、36.8%和32.2%、24.8%,晚稻糙米Cd、Pb累积量分别显著降低66.3%和22.2%;稻草移除+清洁水灌溉处理下,种植早晚稻后的土壤有效态Cd、Pb含量平均下降幅度分别为11.7%和15.9%,早晚稻各部位Cd、Pb含量降低幅度较大,早晚稻根和茎叶Cd、Pb含量平均降幅分别为38.34%、30.35%和43.4%、13.2%,晚稻糙米中Cd、Pb累积量降幅分别为39.4%、67.2%。分析水稻地上部的Cd、Pb富集与转运系数表明,稻草移除结合截断大气沉降或清洁水灌溉等控源措施可显著降低Cd、Pb在水稻地上部位的富集系数,减少地上部位重金属的累积量。上述结果表明,采用稻草移除结合截断大气沉降或清洁水灌溉措施可进一步降低土壤中有效态Cd、Pb含量和水稻中Cd、Pb富集。因此,控制区域大气污染,净化农田灌溉水等控源措施,同时施行稻草移除等输出污染农田土壤中重金属等策略,可有效实现污染农田土壤安全利用和水稻安全生产。     

生物质炭输入减少稻田痕量温室气体排放

为揭示不同水平生物质炭输入对稻田土壤理化性质、水稻产量及温室气体排放的影响,采用自制竹炭在4种不同施用水平下(0、10、20、40 t/hm2)输入稻田土壤,开展了水稻一个生长周期的田间试验。结果表明,生物质炭输入可显著提高土壤p H值和有机碳含量(P0.05),且有机碳含量增幅与生物质炭施用水平呈正比(相关系数为0.78,P0.01)。生物质炭施用可显著降低土壤容重(P0.05),最大降幅为0.25 g/cm3,土壤容重随着生物质炭施用量的增加而降低。不同处理水稻产量无显著性差异(P0.05)。CH4累积排放量与生物质炭施用量呈负相关性(相关系数为-0.24,P0.01),投加生物质炭可显著降低稻田CH4排放通量和累积排放量(P0.05),但过量施用生物质炭(超过20 t/hm2)并不能显著降低CH4累积排放量(P0.05)。相比对照处理(不输入生物质炭),生物质炭输入后一周内可显著性降低N2O排放通量(P0.05),并在排水烤田时升高,最终稳定于9.80 mg/(m2·h)。生物质炭输入可显著性降低N2O累积排放量(P0.05),但不同水平生物质炭输入处理之间差异不显著(P0.05)。该试验条件下,生物质炭施用量为20 t/hm2时可实现稻田稳产和固碳减排目标,该研究可为太湖地区苕溪流域稻田增汇和温室气体减排提供参考。     

Changes of soil organic carbon and its fractions in relation to soil physical properties in a long-term fertilized paddy

Soil organic carbon (SOC) has an important role in improving soil quality and sustainable production. A long-term fertilization study was conducted to investigate changes in SOC and its relation to soil physical properties in a rice paddy soil. The paddy soils analyzed were subjected to different fertilization practices: continuous application of inorganic fertilizers (NPK, N–P–K = 120–34.9–66.7 kg ha⁻¹ yr⁻¹ during 1967–1972 and 150–43.7–83.3 kg ha⁻¹ yr⁻¹ from 1973 to 2007), straw based compost (Compost, 10 Mg ha⁻¹ yr⁻¹), a combination of NPK + Compost, and no fertilization (control). Soil physical properties were investigated at rice harvesting stage in the 41st year for analyzing the relationship with SOC fraction. Continuous compost application increased the total SOC concentration in plough layers and improved soil physical properties. In contrast, inorganic or no fertilization markedly decreased SOC concentration resulting to a deterioration of soil physical health. Most of the SOC was the organo-mineral fraction (<0.053 mm size), accounting for over 70% of total SOC. Macro-aggregate SOC fraction (2–0.25 mm size), which is used as an indicator of soil quality rather than total SOC, covered 8–17% of total SOC. These two SOC fractions accumulated with the same tendency as the total SOC changes. Comparatively, micro-aggregate SOC (0.25–0.053 mm size), which has high correlation with physical properties, significantly decreased with time, irrespective of the inorganic fertilizers or compost application, but the mechanism of decrease is not clear. Conclusively, compost increased total SOC content and effective SOC fraction, thereby improving soil physical properties and sustaining production.     

Biochar combined with nitrogen fertilizer affects soil properties and wheat yield in medium-low-yield farmland

Biochar combined with fertilizer as a soil amendment benefits to improving soil fertility, especially soil organic carbon and crop yield. However, the effect of biochar on the improvement of soil properties and crop yield was varied from soil properties and limited for medium–low-yield farmland in the North China. During the completely randomized field experiment, SIX treatments (biochar applied as 0, 15 and 30 t·ha^-1, under 240 and 300 kg N ha^-1 nitrogen fertilizer) were applied in wheat season and examined to reveal changes in the SOC and other properties of 0- to 10-cm and 10- to 20-cm soil layers. The results showed that two years after the application of biochar, a significant increase in the SOC was observed, ranging from 19.52% to 97.50% (p < 0.05) in the 0- to 20-cm soil layer. Wheat yield and SOC content increased with increasing amount of biochar applied under the same amount of nitrogen fertilizer. The content of soil available potassium increased significantly under 30 t·ha^-1 biochar application (p < 0.05). Both biochar and nitrogen fertilizer application could increase wheat yield, and the effect of biochar application for increasing wheat yield was better than that of nitrogen fertilizer. Wheat yield and SOC content increased with increasing nitrogen fertilizer at the same amount of biochar application. The principal component analysis results showed that biochar input, SOC, available potassium and total nitrogen were the key factors affecting wheat yield. Biochar application is a fast and effective measure to improve SOC and wheat yield in medium- and low-yield farmlands.     

Redistribution of cadmium,copper, lead,nickel, and zinc among soil fractions in a contaminated calcareous soil after application of nitrogen fertilizers

This study was conducted to evaluate the redistribution of the heavy metals Cd, Cu, Pb, Ni, and Zn among different soil fractions by N fertilizers. In a lab experiment, soil columns were leached with distilled water, KNO₃, NaNO₃, NH₄NO₃, or Ca(NO₃)₂ · 4H₂O. After leaching, soil samples were sequentially extracted for exchangeable (EXCH), carbonate (CARB), organic‐matter (OM), Mn oxide (MNO), Fe oxide (FEO), and residual (RES) fractions. Distilled water significantly increased the concentrations of Cd and Ni in EXCH fraction, while concentration of Cu and Zn did not change significantly. Application of KNO₃, NaNO₃, NH₄NO₃, or Ca(NO₃)₂ · 4H₂O significantly increased the concentrations of Cd and Zn in EXCH fraction, while concentration of Pb and Ni was decreased. Application of all fertilizers caused an increase of Cu in the OM fraction. Moreover, leaching with these solutions significantly increased Cd [except in Ca(NO₃)₂ · 4H₂O], Cu, and Zn concentrations in the CARB fraction, while Pb and Ni concentrations were decreased. With application of all leaching solutions, Zn in the EXCH, CARB, FEO, and MNO fractions was significantly increased, while Zn in the OM fraction did not change. The mobility index indicated that Ca(NO₃)₂ · 4H₂O increased the mobility of Cd, Cu, and Zn in the soil, whereas NaNO₃ decreased the mobility of Pb and Ni in the soil. The mobility index of Pb decreased by all leaching solutions. Thus, these results suggest that applying N fertilizers may change heavy‐metal fractions in contaminated calcareous soil and possibly enhance metal mobility and that N‐fertilization management therefore may need modification.     

生物炭对铜矿区污染土壤微生物活性及香根草富集铜、镉、铅的影响

矿区土壤易发生重金属污染,是土地资源利用和维护的一大难题。以铜矿区污染土壤为研究对象,按质量比添加0,1%,2%,4%,10% (w/w)的生物炭,进行香根草室内盆栽试验。研究添加生物炭对土壤pH和微生物活性、香根草富集与转运重金属的影响,探明重金属形态含量与生物炭、微生物活性的相关性,旨在为生物炭与香根草联合修复矿区重金属污染土壤提供理论参考。结果表明:生物炭的添加能提高土壤pH,显著提高土壤FDA水解酶、蔗糖酶和脲酶活性,显著促进土壤基础呼吸,但对土壤微生物量碳无显著影响;生物炭的添加使香根草生物量显著增大,降低土壤Cu和Pb的有效态占比,Cd的变化与此相反;添加生物炭促进香根草对Cd和Pb的富集,降低香根草对Cu的富集,减少Cu、Cd和Pb在香根草体内的转运,因此香根草可作为Cu、Cd和Pb的稳定化植物。土壤蔗糖酶活性与香根草叶片Cu、Cd和Pb含量、有效态和残渣态Cu含量呈显著正相关,土壤基础呼吸与叶片Cu、Cd和Pb含量、有效态Cu、Pb含量呈显著负相关,而与有效态Cd含量呈显著正相关。总之,生物炭可减弱矿区土壤重金属对香根草生长的毒害作用,并促进香根草对重金属的富集,两者结合可改善铜矿区污染土壤的理化性质和微生物活性,有利于重金属污染土壤修复,改善土壤质量。