甘薯淀粉接枝共聚高吸水树脂的合成及在种子包衣上的应用研究

以甘薯淀粉为原料,高锰酸钾为引发剂合成高吸水树脂,并研究高吸水树脂作为种子包衣剂对种子发芽率的影响.通过正交试验,探讨了引发剂浓度、催化剂浓度等因素及皂化条件对高吸水树脂吸水率的影响.研究结果表明,接枝共聚的最佳条件是:淀粉1 g,丙烯酰胺7.5 g,糊化水100 mL,催化剂1.54×10-2 mol/L,引发剂1.5×10-3 mol/L.最佳皂化条件为:氢氧化钠用量26 mL/(g单体),100℃水浴,皂化3 h.用制备的高吸水树脂做玉米种子包衣剂,初步试验结果表明可有效提高种子发芽率.     

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。     

Occurrence of Polycyclic Musks in Sewage Sludge and their Behaviour in Soils and Plants. Part 1: Behaviour of Polycyclic Musks in Sewage Sludge of Different Treatment Plants in Summer and Winter (5 pp)

Background, Aim and Scope   Part 1: Behaviour of Polycyclic Musks in Sewage Sludge of Different Treatment Plants in Summer and Winter Part 2: Investigation of Polycyclic Musks in Soils and Plants -  Preamble. In Part 1 of the study, screening tests were performed to investigate the occurrence of PCMs in sewage sludges. For a preliminary risk assessment, further information is needed about their behaviour in the terrestrial environment. Hence, Part 2 examined the adsorption of PCMs to soil, their dissipation and leaching in soil and their uptake by plants. Background, Aim and Scope   Polycyclic Musks (PCMs) enter the environment via the waste water system. Because of their persistence, they can accumulate in different matrices like sewage sludge or biota. By the use of sewage sludge as a fertilizer, PCMs are transferred to agricultural soils. Therefore, in Part 1 of the study, screening tests were performed to investigate the occurrence of PCMs in sewage sludge. For a preliminary risk assessment, further information is needed about their behaviour in the terrestrial environment. Hence, Part 2 of the study examined the adsorption of PCMs to soil, their dissipation and leaching in soil, and their uptake by plants. Materials and Methods: In the screening study, samples of activated sewage sludge were taken both in summer and in winter at 21 treatment plants. In order to get an overview of the contamination situation, sampling covered different types of treatment plants (in rural, urban, industrial areas). Analytical methods for the determination of HHCB, AHTN, ADBI, ATTN, AHDI and ATII in the sludge samples were developed and applied. Results: The analytical screening of PCMs showed their presence in activated and dried sewage sludge samples. HHCB and AHTN represented about 95% of the PCMs investigated. Their concentrations in the activated sludge samples varied between 2.9 and 10.4 mg/kg dry mass (dm) and 1.1 to 4.2 mg/kg dm, respectively. Although different types of sewage treatment plants were investigated, similar PCM levels were found, showing the widespread input of these compounds into domestic waste water. Discussion: PCM concentrations in activated sludge varied widely. The variation drops substantially when concentrations are related to the varying dry mass. In dehydrated sludge, PCM concentrations were up to 24 mg/kg dm for HHCB and up to 6.9 mg/kg dm for AHTN. These high values are comparable to those obtained in other investigations analysing PCMs. If the degradation of organic mass during anaerobic decomposition is included in the evaluation, the figures obtained are comparable to those for activated sludge. Elimination in sewage sludge was higher in summer than in winter. Therefore, the contamination of the sludges in winter reached higher levels compared to the summer. Conclusions: The results show that PCMs are widespread contaminants in sewage sludge. Recommendations and Perspectives: PCM should be considered in a risk assessment as potential contaminants of sewage sludge destined for agricultural use. Due to the high PCM levels in sewage sludge, further investigations into the degradation and elimination behaviour in sewage sludge have to be carried out, including that involving PCM metabolites such as lactone derivatives.     

pH对砖红壤和黄棕壤Cu~(2+)吸附与解吸的影响

对砖红壤和黄棕壤在不同浓度、不同pH下吸附和解吸Cu2+进行了测定。结果表明, 2种土壤Cu2+吸附量均随平衡液中Cu2+浓度增加而增大,两者关系较好地符合Langmuir吸附方程。Cu2+吸附量随pH升高而增加,Cu2+分配系数的对数与pH呈极显著的线性正相关,吸附一个Cu2+所释放H+的平均数砖红壤(1. 19)大于黄棕壤(1. 01)。可解吸Cu2+的数量随pH升高和吸附Cu2+的数量增加而增加,在pH4~6下,黄棕壤吸附Cu2+及可解吸Cu2+的比例(平均为10. 5% )大于砖红壤(平均为3. 1% )。由此认为, 2种土壤吸附Cu2+虽以专性吸附为主,但砖红壤的表面吸附点位较少,专性吸附点位的比例较高,对Cu2+的亲和性或专性吸附性大于黄棕壤。     

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.     

热固性树脂包膜控释肥料肥效期的快速预测方法

采用静水溶出率的方法,在25℃、40℃、60℃7、0℃、80℃和100℃条件下,探讨了控释肥料中养分累积释放率与温度的变化规律,以期建立控释肥料肥效期或养分释放期的快速预测方法。结果表明,从低温到高温的各种温度处理下,Scotts公司的Osmocote热固性树脂包膜控释肥料养分累积释放曲线都呈二次曲线,相关指数R2均大于0.996。温度与包膜控释肥料肥效期间呈极显著的负相关,并符合一元二次方程,相关指数R2大于0.993。在高温下培养3或8.h建立的预测预报回归方程,可以快速而准确地预测预报包膜控释肥料在常温下(25℃)的肥效期,预测值与实测值只相差2.4.d;而习惯上的微分溶出率法却相差29～42.d。表明用高温下的肥效期预测预报回归法可以在数小时内准确、迅速地预测控释肥料的肥效期。同时该方法可作为控释肥料在线生产质量控制和市场上控释肥料质量检验的候选方法。     

几种有机酸对恒电荷和可变电荷土壤吸附Cu2+的影响

以恒电荷土壤(黄褐土和黄棕壤)和可变电荷土壤(红壤和砖红壤)为供试材料,研究了乙酸、草酸、酒石酸和柠檬酸对土壤吸附重金属铜离子(Cu2 )的影响。结果表明,在相同酒石酸浓度下,土壤对酒石酸的吸附量依次为黄棕壤(2 1 8mmolkg-1) >红壤(15 4mmolkg-1) >砖红壤(9 5mmolkg-1) ,土壤吸附有机酸后负电荷量增加,相同条件下增幅为砖红壤>红壤>黄棕壤;无有机酸配体时,供试土壤对Cu2 的吸附量为黄褐土>黄棕壤>砖红壤>红壤;加入有机酸时,随有机酸浓度增高,土壤对Cu2 的吸附一般表现为“峰”形曲线,峰所对应的有机酸浓度因有机酸类型而异,且随土壤可变电荷性质增强而增高;土壤吸附有机酸后对Cu2 的次级吸附不同于有机酸与铜共存时的竞争吸附,且因土壤性质表现迥异。这些结果意味着在存在有机酸配体的根际环境中,恒电荷土壤与可变电荷土壤对Cu2 的吸附明显不同,并将影响重金属离子在根际的转化与有效性     

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。     

有潜在性的大孔吸附树脂模拟植物根系分泌有机酸吸附的方法

为探索一种根系分泌物富集的方法,用静态吸附法,通过研究HPD-400型大孔吸附树脂对水溶液中柠檬酸、苹果酸和酒石酸的吸附行为,模拟大孔吸附树脂对根系分泌物收集液中主要有机酸吸附的结果表明,相同条件下,HPD-400型大孔吸附树脂对3种有机酸的吸附强度依次为柠檬酸>苹果酸>酒石酸;它对各有机酸的吸附能力随各有机酸浓度的升高而增加,随温度的降低而增加;对各有机酸的吸附均符合Freundlich等温吸附方程,且表现为优惠吸附。试验表明,用HPD-400型大孔吸附树脂可作为根系分泌物的富集材料。     

吸附天然气技术及其应用

阐述了吸附天然气(ANG)的工作原理及其吸附技术、影响吸附剂吸脱附量的因素和解决热效应与气质组分问题的处理措施,并与压缩天然气(CNG)参数进行了比较.研究认为,吸附天然气技术日趋成熟,已经具备了工业化应用的基础条件.提出了加快研究开发ANG技术的建议.