硫酸盐对锌和镉在可变电荷土壤上吸附的影响

SO4^2- and Zn^2 or Cd^2 were added to three variable charge soils in different sequences.In one sequence sulfate was added first ,and in the other,Zn^2 or Cd^2 first.The addition of sulfate to the system invariably caused an increase in adsorption of the heavy metal added,with the effect more remarkable whn the soil reacted with the sulfate prior to the metal.the shift in pH50 for both Zn and Cd adsorption was aslo comparatively larger in the first sequence of reactions .It was suggested that the increase in negative charge density and the resultant negative potential of the soil were the primary cause of the pronounced effect of sulfate on adsorption of Zn or Cd,and the formaiton of the ternary surface complex-S-SO4-M might also play a role in the effect.     

黄土性土壤在连续液流条件下吸附、解吸磷酸根的动力学研究

采用连续液流法研究了黄土性土壤吸附,解吸磷酸根的动力学性质。结果表明：（１）供试土壤对磷酸根的吸附,解吸扫速率可分为快,中,慢三种反应类型;（２）描述吸附,解吸反应的最优模型均为Ｅｌｏｖｉｃｈ方程,最差模型分别为一级反应方程及双常数方程,拟合差的模型对反应速率变化“敏感”,可用于反应类型划分和机理研究;（３）粘粒含量及代换量对吸附速率有著影响,游离铁对吸附速率,ＣａＣＯ３对较低温度下的吸附及较高温     

The effect of soil flooding on the transformation of Fe oxides and the adsorption/desorption behavior of phosphate

As repeatedly reported, soil flooding improves the availability of P to rice. This is in contrast with an increased P sorption in paddy soils. The effects of soil flooding on the transformation of Fe oxides and the adsorption/desorption of P of two paddy soils of Zhejiang Province in Southeast‐China were studied in anaerobic incubation experiments (submerging with water in N₂ atmosphere). Soil flooding significantly increased oxalate‐extractable Fe (Fe_ox), mainly at the expense of dithionite‐soluble Fe (Fe_DCB), as well as oxalate‐extractable P (P_ox), but decreased the ratio of P_ox/Fe_ox. Flooding largely increased both, P adsorption and the maximum P adsorption capacity. The majority of newly sorbed P in the soils was P_ox, but also more newly retained P was found to be not extractable by oxalate. Flooding also changed the characteristics of P desorption in the soils. Due to a decrease of the saturation index of the P sorption capacity, P adsorbed by flooded soils was much less desorbable than that from non‐flooded soils. There are obviously significant differences in the nature of both, the Fe_ox and P_ox fractions under non‐flooded and flooded conditions. The degree of the changes in Fe_ox, P_ox, P adsorption and P desorption by flooding depended on the contents of amorphous and total Fe oxides in non‐flooded soils. Our results confirm that the adsorption and desorption behavior of P in paddy soils is largely controlled by the transformation of the Fe oxides. The reasons of the often‐reported improved P availability to rice induced by flooding, in spite of the unfavorable effect on P desorbability, are discussed.     

不同液土比和温度条件下塿土铵离子吸附

Effects of NH₄⁺ concentration, solution/soil ratio and temperature on NH₄⁺ adsorption were studied in a Eum-Orthic Anthrosol. The slopes of the soil NH₄⁺ adsorption isotherms and the fitted n, the coefficient for the adsorption intensity, and k, the coefficient related to adsorption capacity, of the Freundlich equation increased with increasing solution/soil ratio (SSR) and with decreasing temperature (T). For the range of experimental conditions, the value of ∂q/∂c, the rate of change of the amount of NH₄⁺ adsorbed in the soil solid phase (q) with respect to the equilibrium concentration of NH₄⁺ in soil solution (c), was 0.840, indicating that q increased with increasing c. From 2 to 45 ℃, ∂q/∂SSR, the rate of change of q with respect to SSR, decreased from 2.598 to 1.996, showing that q increased with increasing SSR, while its increasing rate decreased with temperature. From SSR 1:1 to 20:1, ∂q/∂T, the rate of change of q with respect to T, decreased from -0.095 to -0.361, indicating that q decreased with increasing temperature, and at the same time the negative effect of temperature became larger as SSR increased. Thus under the experimental conditions the order of importance in determining the amount of NH₄⁺ adsorbed in the soil solid phase was ∂q/∂SSR > ∂q/∂c > |∂q/∂T|, indicating that the greatest effect on the amount of NH₄⁺ adsorbed was with the solution/soil ratio; the equilibrium concentration of NH₄⁺ had a lesser effect; and temperature had the least effect.     

有机肥非水溶性分解产物对 铜 、镉吸附及解吸的影响

研究了稻草、紫云英和猪粪淹水培养的非水溶性分解产物、两种土壤( 红壤、潮土) 与这 3 种有机肥共同淹水培养后的非水溶性产物( 水溶性物质被除去) 对铜、镉的沉淀、吸附及解吸作 用的影响。 结果表明, 当铜初始浓度为 10-4mol/ L, pH <6 时有机残渣促进铜的沉淀;当 pH >6 时则抑制了铜的沉淀。 当铜初始浓度降为 10-5mol/ L 时, 有机残渣对铜沉淀的促进作用加强。 3 种有机残渣均促进镉的沉淀, 但促进程度比铜低。 与有机肥共同培养的红壤, 在相同的 pH 条 件下, 提高对铜、镉的吸附;在不调节 pH 条件下, 由于有机肥料有提高 pH 的作用, 进一步提高 对铜 、镉的吸附。 与有机肥共同培养的潮土, 在相同的 pH 条件下, 对铜、镉吸附的影响很小;在 不调节 pH 时, 提高了潮土对铜的吸附, 但对镉吸附的影响则较复杂。 上述结果表明, 有机肥的 非水溶性分解产物主要通过提高体系的 pH 值、与铜、镉形成不溶性的络合物而影响铜、镉的吸 附。 与有机物料共同培养的红壤所吸附的铜、镉的解吸率均不同程度降低。     

亚洲棉EST-SNP的挖掘及其在陆地棉中的验证

【目的】随着不同棉种序列数据库的逐步完善以及高通量测序技术的发展,棉花单核苷酸多态性(Single nucleotide polymorphism,SNP)标记开发可利用的公共数据资源逐步增加。【方法】本研究基于陆地棉祖先基因组的现代种亚洲棉表达序列标签(Expressed sequence tag,EST)数据库,利用CAP3对亚洲棉EST数据库进行拼接。拼接获得7 187个重叠群(Contig),再利用Quality SNP软件进行SNP位点分析。【结果】在807条含有4条以上EST序列的Contig中查找到2 690个SNP位点。通过筛选次要等位基因频率大于30%的位点,获得953个可靠度较高的候选SNP,通过电子筛选,最终获得可用于陆地棉分析的SNP 149个,利用位点特异性聚合酶链式反应以及酶切扩增多态序列验证了EST-SNP的准确性。【结论】本研究证实基于亚洲棉EST数据库挖掘用于陆地棉研究的EST-SNP切实可行,并有望将EST-SNP用于陆地棉遗传图谱构建、重要性状的基因定位以及分子标记辅助育种。     

单片机控制电子喷油泵试验台的研究

现有的6PSD30—1型电子控制喷油泵试验台,其电气控制部分电路采用大量分立电子元件,且元件大多老化、损坏,处于闲置状态。现对其进行技术改造,以8031单片机为核心,对喷油泵试验台的喷油计数和主轴转速进行控制。改造后的试验台,省去由大量分立元件组成的单元环节,减少焊接点,大大提高了工作可靠性、检测精度和效率,使用、维护和修理方便。     

设施土壤中连续施用生物炭对土壤磷形态及吸附与释放特性的影响

针对设施土壤中长期大量施用有机肥可能造成的土壤磷素过度积累及易流失等问题,本研究拟通过施用生物炭增加土壤中磷的吸附,从而减少磷流失。此外,目前关于在设施土壤中连续施用生物炭对土壤磷素形态和有效性的影响作用尚不清楚。为此,在辣椒大棚中通过长期定位试验,研究连续4茬施用生物炭对土壤有效磷、不同形态磷、磷吸附及释放的影响。结果表明：在每公顷施用15 t猪粪稻草有机肥基础上施用生物炭可显著增加土壤有机碳含量和土壤pH,并显著改变了土壤磷各组分含量,显著增加了NaHCO₃ P_i、NaHCO₃ P_o、Fe/Al-P_i和Ca-P_i含量,且显著降低了Ca-P_o含量。此外,连续4茬施用生物炭还增加了土壤对磷的吸附,从而降低土壤磷的释放。本研究结果说明,在设施土壤中长期大量施用有机肥下结合施用生物炭在保持土壤有效磷供应下可提高土壤磷的吸附,从而降低土壤磷素的流失风险。     

pH值对重金属Pb~(2+)吸附特性的影响

以砂壤土为研究对象,采用1次平衡法,研究了pH值对重金属Pb2+吸附特性的影响,在此基础上对等温吸附进行模拟分析。结果表明,土壤对Pb2+吸附的pH值影响敏感阈值范围为pH7。所引入的平衡质量体积比与吸附量之间的模型ln(S)=K1×CK2能较好地模拟不同pH值条件下的等温吸附规律。其次为Freundilich模型,Henry模型较适用于低pH值条件下的模拟分析。     

氟离子、磷酸根和铬酸根在可变电荷土壤表面吸附过程中羟基释放动力学

用恒pH自动电位滴定装置研究了氟离子(F-)、磷酸根(H2PO4-)和铬酸根(CrO42-)在3种可变电荷土壤表面吸附过程中羟基(-OH)释放的动力学。研究结果表明,3种阴离子在可变电荷土壤表面吸附时-OH释放量的大小顺序为:F->>H2PO4->CrO42-,这与土壤对3种阴离子吸附量的大小顺序一致。pH对不同阴离子体系中-OH释放的影响不同,在F-体系中,pH5.0时-OH释放量最高,其次为pH6.0时,pH4.0时-OH释放量最小;CrO42-体系中-OH释放量随pH的增加而减小;pH对H2PO4-体系中-OH释放的影响较小。Elovich方程(Y=a kln(t))能够很好拟合2～60min之间的动力学数据,说明-OH释放的速率随时间增加而减小。比较速率常数k的大小可以发现,虽然F-体系中3种可变电荷土壤在前2min释放的-OH量有很大差异,但在2～60min内,-OH释放速率差别不大。在H2PO4-和CrO42-体系中,-OH释放速率的大小顺序是:昆明砖红壤>徐闻砖红壤>江西红壤,与土壤铁、铝氧化物含量一致。