The Role Played by Acetyl Group Distribution Patterns in Substituted Starch Toward Enzymatic De-acetylation and Chain Fragmentation

The nature and distribution of the acetylated groups were evaluated by ¹³C-NMR and ¹H-NMR. The starch substrate with a DS of 1.5 comprises only two patterns: -(14)-d-glucopyranose and 2,3,6-tri-O-acetyl--(14)-d-glucopyranose. The starch with a DS of 3.0 also comprises two patterns: 2,3,4,6-tetra-O-acetyl--(14)-d-glucopyranose and 2,3,6-tri-O-acetyl--(14)-d-glucopyranose; whereas starch (DS = 1.9) contains 4 patterns: 2,3,6-tri-O-acetyl--(14)-d-glucopyranose, 2,3,4,6-tetra-O-acetyl--(14)-d-glucopyranose terminal, 2,6-di-O-acetyl--(14)-d-glucopyranose, and 3,6-di-O-acetyl--(14)-d-glucopyranose. Using esterase from Viscozyme, it has been possible to hydrolyze up to 7% of the DS 3.0 starch. An -amylase (Fungamyl 800) was then added to these acetylesterases. With a 2.4 FAU/mL fraction of -amylase and 2.4 U/mL from the Viscozyme's acetylesterase, 28% of the acetylated end groups were hydrolyzed for the starch substrates with DS 3.0. Moreover, a synergic action between -amylase and acetylesterase was noticed, allowing fragmentation of 32% for DS 1.5, 30% for DS 1.9, and 11% for DS 3.0.     

Research of Toxic Mechanism on Anaerobic Digestion by Lead

The paper analyzes the influence of lead toxicity by anaerobic granule sludge inhibition and recovering experiments. The result shows that there are different inhibition types at different lead contents. Higher lead content leads to more inhibition granular sludge, and at the same time, the time of gas recovery is different. Lower lead content per microorganism results in sooner sludge recovery. Microorganisms have a good ability to resist lead toxicity.     

Effect of six kinds of scale inhibitors on calcium carbonate precipitation in high salinity wastewater at high temperatures

Precipitation of calcium carbonate(Ca CO3) scale on heat transfer surfaces is a serious and expensive problem widely occurring in numerous industrial processes. In this study, we compared the scale inhibition effect of six kinds of commercial scale inhibitors and screened out the best one(scale inhibitor SQ-1211) to investigate its scale inhibition performance in highly saline conditions at high temperature through static scale inhibition tests. The influences of scale inhibitor dosage, temperature, heating time and p H on the inhibition efficiency of the optimal scale inhibitor were investigated. The morphologies and crystal structures of the precipitates were characterized by Scanning Electron Microscopy and X-ray Diffraction analysis. Results showed that the scale inhibition efficiency of the optimal scale inhibitor decreased with the increase of the reaction temperature. When the concentration of Ca2+was 1600 mg/L, the scale inhibition rate could reach 90.7% at 80°C at p H 8. The optimal scale inhibitor could effectively retard scaling at high temperature. In the presence of the optimal scale inhibitor, the main crystal structure of Ca CO3 changed from calcite to aragonite.     

Experimental and theoretical research on the inhibition performance of ethanol gasoline/air explosion by C6F12O

The safety issue of ethanol gasoline and the methods to control or weaken its explosion have attracted attention. To clarify the effect of C₆F₁₂O (perfluoro(2-methyl-3-pentanone)) on the explosion of ethanol gasoline-air mixtures and intrinsic mechanism, the explosion overpressure and flame propagation behavior under different equivalence ratios (φ = 0.6–0.8) and C₆F₁₂O concentrations (χ_inh = 0–4.0%) were experimentally obtained. The detailed inhibitor reaction process was also obtained by CHEMKIN based on a new assembly kinetic mechanism. The results show that the effects of C₆F₁₂O on the explosion characteristics of ethanol gasoline varied with χ_inh and φ. For rich flames, C₆F₁₂O is more effective than and heptafluoropropane (C₃HF₇) and nitrogen (N₂) in suppressing explosions; for lean and equivalence ratio flames, the addition of C₆F₁₂O may result in more severe explosions. The decrease in chemical reactivity is mainly because the mole fractions of OH and H radicals and the proportion of paths H radicals involved decrease after adding C₆F₁₂O, and R1500: CF₃COF + H = CF₃CO + HF, R965: CF₂:O + H = CF:O + HF, R863: CF₃ + H = CF₂ + HF are main suppressing reactions.     

溶解性有机物对冰相中蒽和芘光降解的影响

以Suwannee River Fulvic Acid Standard II(SRFA)、Upper Mississippi River NOM(UMRN)、Elliott Soil Humic Acid Standard IV(ESHA)和Leonardite Humic Acid Standard(LHA) 4种溶解性有机物(Dissolved Organic Matter, DOM)为研究对象,利用125 W高压汞灯作为模拟光源进行室内模拟光解实验,考察了DOM对冰相中蒽和芘光降解的影响.其中,SRFA和UMRN是水源DOM,ESHA和LHA是陆源DOM.结果表明,蒽和芘在冰相中均可以发生直接光降解.4种DOM对冰相中蒽和芘光降解的影响行为并不相同,水源DOM对冰相中蒽和芘光降解的影响程度小于陆源DOM.DOM对冰相中蒽和芘光降解的抑制以光屏蔽效应为主.4种DOM对冰相中蒽和芘光降解均产生淬灭效应,但淬灭程度相异,DOM对蒽激发态的淬灭程度高于其对芘激发态的淬灭程度.与DOM共存条件下,冰相中芘的表观光解速率常数与DOM的SUVA值具有显著正相关性(p0.01).     

一株Acinetobacter johnsonii的部分反硝化特性及动力学研究

从实验室A²/O小试设备中分离纯化出一株具有高亚硝酸盐氮（NO₂^--N）积累率的反硝化菌株ZY04,经过16SrDNA鉴定和基因比对后,初步鉴定为Acinetobacter johnsonii.使用Logistic模型可以很理想地拟合菌株ZY04的生长特性曲线,得到生长方程常数a=0.6588,b=24.08,k=0.2413.在维持初始基质中硝酸盐氮（NO₃^--N）浓度为100mg/L的条件下,改变碳源乙酸钠的浓度,使碳氮比（TOC/TN）为3.5,4.5,5.5,6.5,研究菌株ZY04部分反硝化性能,发现该菌株在不同碳氮比条件下均能够保持95%以上的NO₃^--N降解率,在碳氮比为3.5和4.5时,17h后NO₂^--N积累率达到70%以上;在碳氮比为5.5和6.5时,NO₂^--N积累率在更快的11h后达到85%以上,碳氮比为5.5时达到最高NO₂^--N积累率91%.使用Aiba,Edwards和Andrews模型对菌株的基质抑制动力学进行拟合,结果表明,3种模型均可以很好的拟合NO₃^--N和乙酸钠对菌株的单基质抑制动力学,在双基质抑制的9种组合中,有6种模型成功拟合了NO₃^--N和乙酸钠对菌株的双基质抑制动力学,得到了相关半饱和参数和基质抑制参数,相关系数（R²）可以达到98%.     

Acute and chronic toxicity of nickel to nitrifiers at different temperatures

This study investigated the acute nickel toxicity on nitrification of low ammonia synthetic wastewater at 10, 23, and 35°C. The nickel inhibition half-velocity constants(K_(I,Ni)) for ammonia oxidizing bacteria(AOB) and nitrite oxidizing bacteria(NOB) based on Ni/MLSS ratio at 10, 23, and 35°C were 5.4 and 5.6 mg Ni/g MLSS, 4.6 and 3.5 mg Ni/g MLSS, and 9.1 and 2.7 mg Ni/g MLSS, respectively. In addition, chronic toxicity of nickel to nitrification of low ammonia synthetic wastewater was investigated at 10°C in two sequencing batch reactors(SBRs). Long-term SBRs operation and short-term batch tests were comparable with respect to the extent of inhibition and corresponding Ni/MLSS ratio. The μ_(max), b, and K_o of AOB were 0.16 day~(-1), 0.098 day~(-1) and 2.08 mg O_2/L after long-term acclimatization to nickel of 1 mg/L at 10°C, high dissolved oxygen(DO)(7 mg/L) and long solids retention time(SRT) of 63–70 days. Acute nickel toxicity of nitrifying bacteria was completely reversible.     

荣成天鹅湖水体有机磷的生物有效性和时空分布

磷是滨海湿地生产力的关键限制因素之一,有机磷的矿化分解是湿地活性磷的重要补充途径。本文以滨海荣成天鹅湖湿地为研究对象,通过采集不同季节、不同点位的表层水样,利用酶水解技术研究了天鹅湖水体有机磷的生物有效性及其时空变化规律。研究表明:(1)天鹅湖已经出现轻度富营养化。有机磷是天鹅湖水体总磷(TP)重要组成部分,其中溶解态有机磷(DOP)的含量为0.039～0.123 mg/L,占水体TP的29%～74%,颗粒态有机磷(POP)的含量为0.011～0.073mg/L,占水体TP的11%～25%。(2)在有机磷中,24%～31%的DOP和41%～82%的POP是潜在的生物可利用磷。(3)天鹅湖DOP遵循春夏高而秋冬含量低的特点。有机磷空间分布非均一性,DOP主要分布在湖中区和入河口区。POP集中分布在北部入河口和湖心区及其北部沙滩区域。另外,通过相关性分析表明,有机磷与水环境因子关系密切,DOP和溶解态酶水解有机磷(DEHP)的含量可以指示水体富营养化程度。总之,水体有机磷循环供磷可能是造成水体富营养化的重要原因。因此,在富营养化的防治过程中应该采取有效措施防治有机磷的矿化。     

Insecticidal and growth-reducing activity of foliar extracts from Meliaceae

Summary Thirty-one species in twenty genera of the plant family Meliaceae were assayed for the production of growth-inhibiting phytochemicals, using the generalist herbivorePeridroma saucia. Most species were inhibitory when methanolic extracts were incorporated into artificial diets at concentrations at or below those occurring naturally. In general members of the subfamily Melioideae were more inhibitory than members of the Swietenioideae. Extracts of deciduous species with short leaf lifetimes were significantly more inhibitory than those of evergreen species with longer leaf lifetimes. In a smaller sample of species, evergreen species showed a trend towards having tougher leaves than deciduous species. These results support the resource availability hypothesis of Coleyet al. (1985), and suggest that life history attributes may be of some value in selecting plants for phytochemical prospecting.     

农药杀螟硫磷酶促降解的研究

从长期受农药杀螟硫磷污染的土壤中分离到一株高效降解菌株,研究了其最适产酶条件:培养温度为30℃,培养液起始pH为7.0,培养时间为30 h.从该降解菌中提取的粗酶液在pH 7.5和30℃时显示最大的降解活性,其米氏常数Km为2.92×10-4mol/L,最大降解速率为2 422.79 nmolm in-1mg-1.图7参15