Activated persulfate by DBD plasma and activated carbon for the degradation of acid orange Ⅱ

In this study, the effect of activated peroxydisulfate(PDS) by dielectric barrier discharge(DBD) plasma and activated carbon(HGAC) on the removal of acid orange Ⅱ(AOⅡ) was investigated. The effects of applied voltage, PDS dosage, HGAC dosage, initial pH value, and inorganic anions on the removal rate of AOⅡ were discussed. The main free radicals degrading azo dyes during the experiment were also studied. Experimental results show that the removal rate of AOⅡ in DBD/HGAC/PDS synergistic system is much higher than that in the single system. With the applied voltage of 16 kV, HGAC dosage of 1 g l-1, PDS and AOⅡ molar ratio of 200:1, initial pH value of 5.4 and concentration of AOⅡ solution of 20 mg l-1, the removal rate of AOⅡ reached 97.6% in DBD/HGAC/PDS process after 28 min of reaction.Acidic and neutral conditions are beneficial for AOⅡ removal. Sulfate and hydroxyl radicals play an important role in the removal of AOⅡ. Inorganic anions are not conducive to the removal of AOⅡ.

Degradation of Acid Orange Ⅱ Using Negative Pulsed Discharge Plasma from a Nozzle-cylinder Electrode Coated with TiO2

Many sub-products of pulsed discharge,such as ultraviolet light,strong electric fields,shock waves and active species,are effective in treating wastewater.To improve the efficiency of the discharge plasma technology in removing pollutants,adding TiO2 photo-catalyst to pulsed discharges could help.A negative-pulsed-discharge system,which has nozzle discharge electrodes with or without TiO2 coating,is used to degrade azo dye Acid Orange Ⅱ,and the effects of several key conditions(maximum pulse voltage,pulse repetition frequency,initial mass concentration of Acid Orange Ⅱ initial solution pH,treatment duration,the phase of discharge,and the existence of TiO2) on the degradation are experimentally investigated.The degradation of Acid Orange Ⅱ increases with maximum pulse voltage,pulse repetition frequency,and treatment duration,and it is larger when putting the discharge electrode on the solution surface than in air or inside the solution,i.e.the discharge in gas phase is more effective than that in gas-liquid phase or liquid phase.The degradation decreases as the initial mass concentration of the solution increases.It also relates to pH and is higher at acidic conditions than at neutral or alkaline conditions.Compared to treatments without TiO2,the ones using the nozzle discharge electrode with TiO2 coated increase the degradation of Acid Orange Ⅱ by 5 %.It is concluded that the proposed system with TiO2 added in can remove Acid Orange Ⅱ from wastewater effectively.

Rapid decolorization of Acid Orange Ⅱ aqueous solution by amorphous zero-valent iron

Some problems including low treatment capacity,agglomeration and clogging phenomena,and short working life,limit the application of pre-treatment methods involving zero-valent iron （ZVI）.In this article,ZVI was frozen in an amorphous state through a melt-spinning technique,and the decolorization effect of amorphous ZVI on Acid Orange II solution was investigated under varied conditions of experimental variables such as reaction temperature,ribbon dosage,and initial pH.Batch experiments suggested that the decolorization rate was enhanced with the increase of reaction temperature and ribbon dosage,but decreased with increasing initial solution pH.Kinetic analyses indicated that the decolorization process followed a first order exponential kinetic model,and the surface-normalized decolorization rate could reach 2.09 L/（m^2 ·min） at room temperature,which was about ten times larger than any previously reported under similar conditions.Recycling experiments also proved that the ribbons could be reused at least four times without obvious decay of decolorization rate and efficiency.This study suggests a tremendous application potential for amorphous ZVI in remediation of groundwater or wastewater contaminated with azo dyes.

Understanding changes in volatile compounds and fatty acids of Jincheng orange peel oil at different growth stages using GC-MS

Jincheng orange(Citrus sinensis Osbeck)is widely grown in Chongqing,China,and is commonly consumed because of its characteristic aroma contributed by the presence of diverse volatile compounds.The changes in aroma during the development and maturation of fruit are indicators for ripening and harvest time.However,the influence of growth stages on the volatile compounds in Jincheng orange remains unclear.In addition,volatiles originate from fatty acids,most of which are the precursors of volatile substances.On this basis,gas chromatography-mass spectrometry(GC-MS)was performed to elaborate the changes in volatile constituents and fatty acids as precursors.This study tested proximately 60 volatiles and 8 fatty acids at 9 growth and development stages(AF1-AF9).Of those compounds,more than 92.00%of total volatiles and 87.50%of fatty acids were terpenoid and saturated fatty acids,respectively.As shown in the PCA plot,the AF5,AF6,and AF9 stages were confirmed as completely segregated and appeared different.In addition,most of the volatiles and fatty acids first increased at the beginning of the development stage,then decreased from the AF6 development stage,and finally increased at the AF9 maturity stage.Moreover,the highest contents of terpenoid,alcohols,aldehydes,ketones,and saturated fatty acids in Jincheng orange peel oil were d-limonene,linalool,octanal,cyclohexanone,and stearic acid during development stages,respectively.Our results found that the growth stages significantly affected the volatile constituents and precursors in Jincheng orange peel oil.

含铁柱撑膨润土光催化降解Orange Ⅱ

制备了两种含铁柱撑膨润土(FeAlBent和FeBent),用XRD、BET、TEM对它们进行了性能表征。以偶氮染料OrangeⅡ为目标降解物,考察了它们作为复相Fenton催化剂的光催化性能,以及溶液的pH、H2O2浓度、催化剂用量对OrangeⅡ降解的影响,并与相应的均相Fenton反应进行了比较。结果表明FeAlBent和FeBent具有很高的比表面积(分别为194.2和114.6m2/g),用FeAlBent或FeBent作光催化剂的复相光助Fenton反应的催化性能明显优于相应的均相光助Fenton反应。此外复合铁铝柱撑膨润土(FeAlBent)比单一的铁柱撑膨润土(FeBent)在反应过程中具有更低的铁离子溶出量,它们还具有分离简单、重复使用性好等特点。

Formation of the Inclusion Complex of Orange Ⅱ with β-Cyclodextrin and Its Photostability

Inclusion complex of Orange II with β-Cyclodextrin (β-CD) and the anti-photolysis effect under UV-light were investigated. The molar ratio of inclusion complex of β-Cyclodextrin and Orange Ⅱ is 1∶1. The formation constant K=1.236×10 3 L/mol was determined by the UV and Fluorescence spectra respectively, which was quite in accordance with the calculation with a modified Benesi-Hildbrand equation. The inclusion complex was characterized by the IR spectra and the molar ratio of inclusion complex is 1∶1 too. The formation constant K=1.266×10 3 L/mol was determined by 1 H NMR analysis and was nearly the same by UV and fluorescence spectra. The photocatalytic decolorization rate of Orange Ⅱ solutions containing β-CD and TiO_ 2 was smaller by 51.9% than that of the Orange Ⅱ solutions only containing TiO_ 2 , while in the case of direct photolysis of Orange Ⅱ solutions, β-CD can lower the photolysis rate by 48.1% under UV-light. This result indicates β-CD can inhibit the photolysis and photocatalytic decolorization of Orange Ⅱ under UV-light. The β-CD inclusion complex was found to be persistent to UV-light photolysis.

Photocatalytic Degradation of Organic Dye Methyl Orange with Phosphotungstic Acid

Silicotungstic acid and phosphotungstic acid were prepared and characterized by Fourier Transform Infrared Spectroscopy (FTIR) and X-ray diffraction (XRD). The results showed that the prepared catalysts possess classical Keggin structure. The factors on the degradation of methyl orange, such as the kind of catalyst, the amount of catalyst, the original concentration of dye and illumination time were investigated under metal halide lamp. The degradation of methyl orange is up to 93.6% with phosphotungstic acid at the best reaction conditions at 8.89 g/L concentration of phosphotungstic acid, 5.56 mg/L concentration of methyl orange and 80 min illumination time.

Regeneration of Acid Orange 7 Exhausted Granular Activated Carbon Using Pulsed Discharge Plasmas

In this paper, a pulsed discharge plasma （PDP） system with a multi-needle-to-plate electrodes geometry was set up to investigate the regeneration of acid orange 7 （AO7） exhausted granular activated carbon （GAC）. Regeneration of GAC was studied under different conditions of peak pulse discharge voltage and water pH, as well as the modification effect of GAC by the pulse discharge process, to figure out the regeneration efficiency and the change of the GAC structure by the PDP treatment. The obtained results showed that there was an appropriate peak pulse voltage and an optimal initial pH value of the solution for GAC regeneration. Analyses of scanning electron microscope （SEM）, Boehm titration, Brunauer-Emmett-Teller （BET）, Horvath-Kawazoe （HK）, and X-ray Diffraction （XRD） showed that there were more mesopore and macropore in the regenerated GAC and the structure turned smoother with the increase of discharge voltage; the amount of acidic functional groups on the GAC surface increased while the amount of basic functional groups decreased after the regeneration process. From the result of the XRD analysis, there were no new substances produced on the GAC after PDP treatment.

超高效液相色谱-串联质谱法测定禽用饲料中苏丹红、罗丹明B和酸性橙Ⅱ等6种染色剂含量

本研究基于超高效液相色谱-串联质谱(UPLC-MS/MS)结合QuEChERS快速净化方法,旨在建立禽用饲料中苏丹红等6种化工染料的定量分析方法。样品用乙腈提取,C_(18)+PSA净化材料净化,净化液经Hypersil GOLD C_(18)反向色谱柱分离,在电喷雾离子源(ESI)正、负离子双扫描模式下多反应监测(MRM),以标准曲线外标法定量。结果表明:6种化合物线性关系良好;相关系数(R^(2))>0.999,4种苏丹红和酸性橙Ⅱ检出限(LOD)为0.5μg/kg,定量限(LOQ)为1.0μg/kg,罗丹明B LOD为0.05μg/kg,LOQ为0.1μg/kg。添加回收率为90%~110%,相对标准偏差<10%。本研究方法具有快速、灵敏等优势,可实现禽用饲料中6种化工染料的准确定量分析,为禽用饲料的质量安全提供技术参考。

羟基磷灰石复合腐植酸及其对Mn(Ⅱ)的去除

以硝酸钙和磷酸氢铵为原料,采用化学沉淀法成功合成羟基磷灰石(HAP),并将其与腐植酸(HA)复合,制备出复合吸附剂HAP-HA。通过傅里叶变换红外光谱(FT-IR)、比表面积及孔径分析、差热-热重分析(TGDSC)及扫描电镜(SEM)等方法对样品进行表征。结果表明:腐植酸成功负载到羟基磷灰石上;HAP-HA孔径主要分布在3~5 nm,比表面积较大,且具有较好的稳定性;HAP-HA表面粗糙不平、孔隙较多,这增大了比表面积,为重金属离子提供了大量的活性位点。以Mn(Ⅱ)为目标污染物,将Mn(Ⅱ)的去除率作为指标,通过吸附实验考察吸附剂HAP-HA对污染物的吸附性能。结果表明:在常温、pH为8.0、投加量为0.15 g、吸附时间为150 min的条件下,吸附剂HAP-HA对Mn(Ⅱ)的去除率最高,可稳定达到99.0%以上;该吸附过程符合Freundlich等温吸附模型。同时,对吸附后的吸附剂进行脱附及再生吸附实验,以NaOH溶液作为洗脱剂可取得较好的脱附效果,脱附效率可达78.1%,再生循环吸附6次后HAP-HA仍具有良好的吸附性能。

氮掺杂多孔污泥炭活化过二硫酸盐降解橙黄Ⅱ

以市政污泥为碳源、碳酸氢钾为活化剂、尿素为氮源,制备了氮掺杂多孔污泥生物炭(NKBC),并采用N2吸附-脱附实验、SEM、XRD、XPS对其比表面积、表面特征进行了系列表征与分析,结果表明,NKBC具有较大的比表面积,由于N负载于NKBC孔道内,其表面褶皱、缺陷较多,活化位点较多。将NKBC用于活化过二硫酸盐(PDS)降解橙黄Ⅱ,考察NKBC/PDS体系降解橙黄Ⅱ的性能,结果表明,在加入PDS 20 min后,NKBC/PDS体系对橙黄Ⅱ的降解率高达99.7%;该体系可在较宽pH范围(3~11)及常见阴离子存在条件下发挥作用。自由基猝灭实验和EPR光谱结果表明,NKBC/PDS体系降解橙黄Ⅱ的主要活性物种有·OH、SO_(4)^(·-)和^(1)O_(2),且以^(1)O_(2)为主。该研究所构建的NKBC/PDS体系可应用于染料废水的处理,实现“以废治废”的目标。

Synthesis of the Prospective Anticancer Molecule Perillic Acid from Orange Essential Oil by the Yeast <i>Yarrowia lipolytica</i>

The bioconversion of the hydrophobic and volatile limonene to perillic acid, a potential anticancer agent, by the yeast Yarrowia lipolytica was studied in two steps. Firstly, experimental design was used for process optimization using high-purity limonene as substrate and secondly orange essential oil containing 89.1% limonene was used as substrate under the previously optimized conditions. Limonene concentration and pH were identified by fractional factorial design as significant factors and were optimized by central composite design. Under optimized process conditions (0.16% (v/v) limonene;pH 6.9), the 24 h biotransformation process resulted in the accumulation of 0.368 g·L-1 of perillic acid corresponding to a molar yield of 23.1%. A subsequent substrate addition under the same reaction conditions doubled perillic acid concentration to 0.793 g·L-1 and a molar yield of 24.2%. The use of orange essential oil under the optimized reaction conditions increased both perillic acid accumulation and yield to 0.872 g·L-1 and 29.7%, respectively. The robustness of Y. lipolytica allowed the efficient biotransformation of a crude by-product of the citrus industry into a valuable fine chemical.

基于4-羟基间苯二甲酸和含氮杂环配体的Zn(Ⅱ)配合物的合成、晶体结构与荧光性质研究

在水热法条件下,4-羟基间苯二甲酸(H 2HPHA)和锌离子分别与1,2二(吡啶-4-基)乙烯(dpee)及4,4′-联吡啶(4,4′-bpy)反应得到了2个三维的配位聚合物[Zn(HPHA)(dpee)·(DMA)2]n(配合物1)和[Zn(HPHA)2(4,4′-bpy)2·DMA]n(配合物2)。用X射线单晶衍射测定了配合物的晶体结构,结果显示:配合物1属于单斜晶系,C2空间群,每个不对称单元由一个锌离子,一个4-羟基间苯二甲酸配体及一个1,2-二(吡啶-4-基)乙烯组成;配合物2属于单斜晶系,P12/c1空间群,每个不对称单元由两个锌离子,两个4-羟基间苯二甲酸配体及两个4,4′-联吡啶配体组成。荧光光谱分析结果表明:配合物1的最强激发峰和发射峰在分别在251和397 nm,配合物2的最强激发峰和发射峰分别在415和513 nm。热重分析表明两个配合物在室温下稳定。

铝镁混悬液(Ⅱ)在酸相关性疾病中的应用

目的探究铝镁混悬液(Ⅱ)在酸相关性疾病中的应用现状分析。方法选取2022年4月—2023年4月本院收治的酸相关性疾病患者202例临床资料开展回顾性分析。分析患者基本人口学特征、生命体征、既往史、主要临床症状及诊断、疗效结果分析、治疗期间不良反应发生情况,为优化诊疗方案寻求循证医学支持。结果抗酸药记录表1填写者202例,其中铝镁混悬液(Ⅱ)为抗酸药物使用最常见药物。使用铝镁混悬液(Ⅱ)治疗的130例患者中男性76例,女性54例;年龄阶段以23~55岁居多;收缩压平均值106~120mmHg居多;舒张压平均值66~80mmHg居多;体重平均值51~70kg居多;心率平均值76~90次/分居多;既往疾病史中发生率最高的为高血压;个人史中发生率最高为饮酒史;既往治疗用药最常见为奥美拉唑。常出现的几种症状发生率依次为反酸、烧心、腹痛、嗳气、黑便;而临床诊断统计中显示主要为慢性胃炎。铝镁混悬液(Ⅱ)治疗130例患者的总体疗效有效率为95.89%。药物不良反应者1例,具体为大便黏稠和胃肠道不适。结论铝镁混悬液(Ⅱ)在酸相关性疾病中临床应用较为普遍,使用群体较为广泛,临床治疗疗效较好,且安全性较好。

NTA强化Fe(Ⅱ)/PMS体系降解橙黄G的效能与机制

针对二价铁/过一硫酸盐(Fe(Ⅱ)/PMS)体系存在近中性pH条件下氧化效能低的问题,采用氨基三乙酸(NTA)强化Fe(Ⅱ)/PMS体系降解橙黄G(OG),研究NTA/Fe(Ⅱ)/PMS体系中OG降解的效能和机制,考察NTA,Fe(Ⅱ),PMS等反应物浓度和溶液pH值对OG降解效能的影响.实验结果表明:当pH=6.5时,NTA可显著强化Fe(Ⅱ)/PMS体系的氧化效能,OG的去除率从11.7%提高到92.5%,NTA的加入提高了溶液中有效活化剂的浓度,促进PMS分解生成活性物质;NTA/Fe(Ⅱ)/PMS体系中主导的活性物质为Fe(Ⅳ)和SO_(4)^(-)·,二者对体系氧化效能的贡献分别为72.0%和28.0%;增加NTA,Fe(Ⅱ)和PMS的浓度有助于OG的降解,但当三者浓度分别超过1.5,1.5,2.0 mmol·L^(-1)时,出现抑制现象;引入NTA既提高了Fe(Ⅱ)/PMS体系在近中性pH条件下的氧化能力,又拓宽了该体系的pH应用范围.

Photo-induced transformations of Hg(Ⅱ) species in the presence of Nitzschia hantzschiana,ferric ion,and humic acid

Effects of algae Nitzschia hantzschiana, Fe（Ⅲ） ions, humic acid, and pH on the photochemical reduction of Hg（Ⅱ） using the irradiation of metal halide lamps （λ〉 365 nm, 250 W） were investigated. The photoreduction rate of Hg（Ⅱ） was found to increase with increasing concentrations of algae, Fe（Ⅲ） ions, and humic acid. Alteration of pH value affected the photoreduction of Hg（Ⅱ） in aqueous solution with or without algae. The photoreduction rate of Hg（Ⅱ） decreased with increasing initial Hg（Ⅱ） concentration in aqueous solution in the presence of algae. The photochemical kinetics of initial Hg（Ⅱ） and algae concentrations on the photoreduction of Hg（Ⅱ） were studied at pH 7.0. The study on the total Hg mass balance in terms of photochemical process revealed that more than 42% of Hg（Ⅱ） from the algal suspension was reduced to volatile metallic Hg under the conditions investigated.

Adsorption of Cu(Ⅱ) on humic acids derived from different organic materials

The adsorption of Cu（Ⅱ） from aqueous solution onto humic acid （HA） which was isolated from cattle manure （CHA）, peat （PHA）, and leaf litter （LHA） as a function of contact time, pH, ion strength, and initial concentration was studied using the batch method. X-ray absorption spectroscopy （XAS） was used to examine the coordination environment of the Cu（ll） adsorbed by HA at a molecular level. Moreover, the chemical compositions of the isolated HA were characterized by elemental analysis and solid-state 13C nuclear magnetic resonance spectroscopy （NMR）. The kinetic data showed that the adsorption equilibrium can be achieved within 8 h. The adsorption kinetics followed the pseudo-second-order equation. The adsorption isotherms could be well fitted by the Langmuir model, and the maximum adsorption capacities of Cu（ll） on CHA, PHA, and LHA were 229.4,210.4, and 197.7 mg g-1, respectively. The adsorption of Cu（Ⅱ） on HA increased with the increase in pH from 2 to 7, and maintained a high level at pH〉7. The adsorption of Cu（Ⅱ） was also strongly influenced by the low ionic strength of 0.01 to 0.2 mol L-1 NaNO3, but was weakly influenced by high ionic strength of 0.4 to 1 mol L-1 NaNO3. The Cu（Ⅱ） adsorption on HA may be mainly attributed to ion exchange and surface complexation. XAS results revealed that the binding site and oxidation state of Cu adsorbed on HA surface did not change at the initial Cu（Ⅱ） concentrations of 15 to 40 mg L 1. For all the Cu（Ⅱ） adsorption samples, each Cu atom was surrounded by 40/N atoms at a bond distance of 1.95 A in the first coordination shell. The presence of the higher Cu coordination shells proved that Cu（Ⅱ） was adsorbed via an inner-sphere covalent bond onto the HA surface. Among the three HA samples, the adsorption capacity and affinity of CHA for Cu（Ⅱ） was the greatest, followed by that of PHA and LHA. All the three HA samples exhibited similar types of elemental and functional groups, but different contents of elemental and functional groups. CHA contained larger proportions of methoxyl C, phenolic C and carbonyl C, and smaller proportions of alkyl C and carbohydrate C than PHA and LHA. The structural differences of the three HA samples are responsible for their distinct adsorption capacity and affinity toward Cu（Ⅱ）. These results are important to achieve better understanding of the behavior of Cu（Ⅱ） in soil and water bodies in the presence of organic materials.

Synthesis, Crystal Structure and Fluorescent Property of a New One-dimensional Cadmium(Ⅱ) Coordination Polymer Based on 3,4-Thiophenedicarboxylic Acid and 1,10-Phenanthroline

A new cadmium（Ⅱ） polymer [Cd（tdc）（Phen）]n 1 （H2tdc = thiophene-3,4-dicar-boxylic acid, Phen = 1,10-phenanthroline） was synthesized under hydrothermal conditions. The compound crystallizes in the triclinic system, space group P , with a = 7.3150（10）, b = 10.3598（14）, c = 10.8784（15） , α = 82.2740（10）, β = 72.9730（10）, γ = 80.236（2）°, V = 773.68（18） 3, Z = 2, Mr = 462.74, Dc = 1.986 Mg/m3, μ = 1.58 mm-1, F（000） = 456, the final R = 0.0218 and wR = 0.0465 for 3361 observed reflections with Ⅰ 〉 2σ（Ⅰ）. The compound presents a one-dimensional （1-D） double-stranded structure and exhibits fluorescent emission at room temperature. Furthermore, infrared spectroscopy, elemental analyses, thermogravimetric analysis and powder X-ray diffraction properties of the compound are also investigated.

Hydrothermal Synthesis and Crystal Structure of a New One-dimensional Nickel(Ⅱ) Complex with 2-Pyridinecarboxyic Acid and 4,4′-Bipyridine Ligands

A new metal-organic coordination polymer [Ni[（2-pya）2（4,4′-bipy）]n·6nH2O （2-pya = 2-pyridinecarboxylic acid, 4,4′-bipy = 4,4′-pyridine） 1 has been hydrothermally synthesized and structurally characterized by elemental analysis, IR spectrum, TG and single-crystal X-ray diffraction. The complex crystallizes in tetragonal, space group I4 1/α with a = b = 22.5642（19）, c = 10.7118（18） A, V = 5453.8（11） A^3, C22H28N4NiO10, Mr= 567.19, Dc = 1.382 g/cm^3, μ（MoKα） = 0.769 mm^-1, F（000） =2368, Z = 8, the final R = 0.0572 and wR = 0.1254 for 1401 observed reflections （I 〉 2σ（I））. It exhibits a one-dimensional chain-like structure by mixed ligands of 2-pyridinedicarboxylic acid and 4,4′-pyridine.