VDF/CTFE共聚物原子转移自由基反应法氢化制备VDF/TrFE/CTFE三元共聚物的研究

报道了一种用于偏氟乙烯-三氟氯乙烯共聚物(VDF/CTFE共聚物)制备偏氟乙烯/三氟乙烯/三氟氯乙烯共聚物(VDF/TrFE/CTFE共聚物)的新方法,该方法以CuCl与2′,2-Bpy的配合物为催化剂,N-甲基吡咯烷酮(NMP)为溶剂,异丙苯(丙酮、2,6-二叔丁基-4-甲基苯酚)为链转移剂,通过原子转移法在VDF/CTFE共聚物上产生自由基,进而利用自由基链转移反应将VDF/CTFE共聚物上部分Cl原子用H原子取代以制备VDF/TrFE/CTFE三元共聚物.对该体系的反应机理及其影响因素进行研究发现,随着实验温度的升高(80～140℃),反应时间的延长,氢化量增加,产物中TrFE含量增加;反应温度越高,初始反应速度越快,完全氢化时间越短;催化剂与氢化量的比例基本为1:1,通过控制催化剂的量可以定量控制氢化率;新的反应体系不会对产物的分子量产生大的影响.     

取代基效应与乙烯-α-烯烃共聚物的序列结构——5.乙烯-乙烯醇共聚物

本文应用取代基效应(SCS)方法研究了乙烯-乙烯醇(EVA)共聚物,得到了羟基(-OH)在两种不同溶剂中的SCS参数:在苯酚+重水(80/20W/W)中参数为S_1=42.77±0.08ppm,S_2=7.155±0.06ppm,S_3(s)=-4.08±0.02ppm,S_3(t)=-3.09±0.02ppm,S_4=0.48±0.03ppm,S_5=0.26±0.05ppm,在以邻二氯苯为溶剂时参数为S_1=44.97±0.61ppm,S_2=7.40±0.00ppm,S_3(s)=-4.51±0.17ppm,S_3(t)=-3.13±0.00ppm,S_4=0.63±0.04ppm,S_5=0.36±0.00ppm,同时利用所得到的SCS参数对该共聚物的~(13)C NMR谱进行了归属。     

POSS基杂化含氟丙烯酸酯共聚物涂膜的表面相分离与疏水性研究王鹏金云皮丕辉文秀芳徐守萍程江

采用自由基溶液聚合法成功合成了多面体低聚倍半硅氧烷(POSS)基杂化含氟丙烯酸酯共聚物,并采用核磁共振仪(NMR)和凝胶渗透色谱仪(GPC)表征了共聚物,其中POSS和含氟单体分步加入到反应中.首先将共聚物溶解到三氟三氯乙烷(F113)和乙酸乙酯的混合溶剂中配制成溶液,然后通过直接在玻璃片上滴落共聚物溶液制备了共聚物涂膜.采用扫描电子显微镜(SEM)、X-射线光电子能谱(XPS)、原子力显微镜(AFM)和接触角测量仪考察了F113和乙酸乙酯的配比对共聚物涂膜表面形貌、表面元素组成、表面粗糙度以及表面疏水性的影响.实验数据表明POSS在表面能够聚集成纳米颗粒并能极大增强涂膜表面粗糙度和疏水性.共聚物表面同时存在POSS聚集与有机相微相分离两类相分离行为,并形成了复合粗糙结构.虽然POSS和含氟段竞争迁移到表面,但是随着混合溶剂中F113的增多,涂膜表面含氟量越来越多,同时POSS在表面的聚集体越来越少,表面平均粗糙度越来越小,最终涂膜的疏水性越来越强,这说明F113有助于提升氟的趋表迁移能力,使涂膜表面含氟链段占据较多的表面空间,从而抑制了POSS在表面聚集分布.当使用纯F113作为溶剂时,共聚物涂膜的表面氟含量为45.25%,平均粗糙度为93.4 nm,此时静态水接触角最大为135.0?,表现出优异的疏水性.     

POSS基杂化含氟丙烯酸酯共聚物涂膜的表面相分离与疏水性研究

采用自由基溶液聚合法成功合成了多面体低聚倍半硅氧烷(POSS)基杂化含氟丙烯酸酯共聚物,并采用核磁共振仪(NMR)和凝胶渗透色谱仪(GPC)表征了共聚物,其中POSS和含氟单体分步加入到反应中.首先将共聚物溶解到三氟三氯乙烷(F113)和乙酸乙酯的混合溶剂中配制成溶液,然后通过直接在玻璃片上滴落共聚物溶液制备了共聚物涂膜.采用扫描电子显微镜(SEM)、X-射线光电子能谱(XPS)、原子力显微镜(AFM)和接触角测量仪考察了F113和乙酸乙酯的配比对共聚物涂膜表面形貌、表面元素组成、表面粗糙度以及表面疏水性的影响.实验数据表明POSS在表面能够聚集成纳米颗粒并能极大增强涂膜表面粗糙度和疏水性.共聚物表面同时存在POSS聚集与有机相微相分离两类相分离行为,并形成了复合粗糙结构.虽然POSS和含氟段竞争迁移到表面,但是随着混合溶剂中F113的增多,涂膜表面含氟量越来越多,同时POSS在表面的聚集体越来越少,表面平均粗糙度越来越小,最终涂膜的疏水性越来越强,这说明F113有助于提升氟的趋表迁移能力,使涂膜表面含氟链段占据较多的表面空间,从而抑制了POSS在表面聚集分布.当使用纯F113作为溶剂时,共聚物涂膜的表面氟含量为45.25%,平均粗糙度为93.4 nm,此时静态水接触角最大为135.0?,表现出优异的疏水性.     

合l，4—萘基结构的聚芳醚酮的合成与表征

以无水A1Cl3为催化剂，N-甲基毗咯烷酮为助剂，ClCH2CH2Cl为溶剂，将一种含萘环的新芳醚单体——4，4’-二(α-萘氧基)二苯酮(DNBP)分别与对苯二甲配氯、间苯二甲配氯、2，5-二氯对苯二甲配氯等芳二酰氯通过低温溶液亲电共缩聚反应合成了6种主链含1，4-萘基结构的新型聚芳醚酮醚酮酮无规共聚物。考察了溶剂体系、反应温度、反应时间、单体摩尔浓度等聚合反应条件对聚合物分子量的影响，并用对数比浓粘度(ηnl3)，IR，DSC，TG和WAXD等方法对其进行了分析表征。结果表明：它们均为非晶态聚合物，有较高的玻璃化温度和优良的耐热性，可溶于一些强权性非质子溶剂中。并以CHCl3为溶剂，甲酵和正已烷为沉降剂用浊度滴定法测定了上述6种聚合物的溶度参数(δ)。     

氢键辅助光诱导N-乙基马来酰亚胺/甲基丙烯酸甲酯序列可控共聚物的聚合

在405 nm光源辐照下，采用二硫代羰基苯甲酸异丁腈酯(CPDB)作为光引发剂和链转移剂，对N-乙基马来酰亚胺(NEM)和甲基丙烯酸甲酯(MMA)的光诱导链转移共聚行为进行了研究。通过核磁共振氢谱(¹H-NMR)和基质辅助激光解吸电离飞行时间质谱(MALDI-TOFMS)对共聚物的结构进行了表征。利用1,1,1,3,3,3-六氟-2-丙醇(HFP)溶剂与单体构筑氢键，探究了HFP的最佳添加量，并通过单体在聚合物中的累计组成(Fcum)与其在聚合过程中的瞬间组成(Finst)之间的关系，对不同聚合条件下聚合物的组成和序列结构进行了探究。结果表明：在405 nm光照下，CPDB能够成功引发NEM和MMA的共聚，且聚合行为具有活性特征；当HFP与单体的物质的量之比为1∶1时，MMA单体会优先与HFP形成氢键，使NEM和MMA反应速率相近，形成交替结构共聚物；当不以HFP为溶剂或在加热条件下进行聚合时，NEM和MMA共聚得到的共聚物均为梯度共聚物。     

PS-b-P4VP两嵌段共聚物的合成及其自组装的研究

双硫酯 (PhC(S)SCH2 Ph)作为链转移剂 ,AIBN作为引发剂 ,用可逆的加成 断裂链转移 (RAFT)活性自由基聚合方法 ,合成了PS大分子链转移剂 .然后在AIBN引发下 ,利用制得的大分子链转移剂 ,以DMF为溶剂 ,80℃下采用RAFT方法 ,合成了PS b P4VP两嵌段共聚物 ,通过核磁共振谱及动力学的研究证明了其活性聚合的特征 .结果表明聚合反应在 2 4h内转化率可达 95 % .并用透射电子显微镜 (TEM )和扫描电子显微镜(SEM)研究了PS b P4VP两嵌段共聚物在选择性溶剂硝基苯 四氢呋喃中的自组装行为 ,研究结果表明改变聚合物的浓度以及选择性溶剂 ,可观察到自组装行为的变化 .     

医用生物相容性接枝共聚物负载阿霉素和香豆素的研究

以一端连有单电子转移自由基聚合(RAFT)链转移剂的聚乙二醇(PEG)为大分子链转移剂,调控2-(4-羟基丁酰氧基)甲基丙烯酸叔丁酯(t BHBMA)的RAFT聚合,得到的PEG-b-Pt BHBMA嵌段共聚物引发丙交酯的开环聚合,制得接枝共聚物PEG-b-(Pt BA-g-PLA).通过聚乳酸末端的羟基与7-甲氧基香豆素-3-羧酸(COU)中羧基的酯化反应,得到了含有荧光标记分子的接枝共聚物PEG-b-(Pt BA-g-PLA-COU).该聚合物主链选择性水解,得到了含有荧光标记分子的两亲性接枝共聚物PEG-b-(PAA-g-PLA-COU).以PEG-b-(PAA-g-PLA-COU)为药物载体,对阿霉素(DOX)进行了负载,制得了含有荧光标记分子的聚合物载药胶束.利用紫外光谱和动态光散射测定了载药胶束的载药量和胶束尺寸.     

可逆加成-断裂链转移聚合/点击化学法制备含1,2,3-三氮唑官能团的嵌段聚合物及其静电纺丝

通过可逆加成-断裂链转移聚合(RAFT)活性自由基聚合方法制备了聚(苯乙烯-b-对氯亚甲基苯乙烯)(PS-b-PCVB)二嵌段共聚物,其中的氯亚甲基侧基经叠氮化反应后与丙炔醇进行点击(Click)反应,最终得到了含有1,2,3-三氮唑官能团的聚苯乙烯二嵌段共聚物(PS-b-PVBTM),核磁共振谱表征结果证明,PS-b-PCVB中的氯亚甲基完全转变成了1,2,3-三氮唑基团。PS-b-PVBTM在15kV电压下进行静电纺丝,制得具有相分离现象的直径在100nm左右的纤维。在90℃退火后纳米纤维表面变得光滑。红外光谱证明,在加热前后聚合物组成没有明显变化,而XPS结果显示退火后共聚物中C1s振起伴峰降低,说明形成了电子转移络合物;XPS结果还表明,退火后表面张力较低的聚苯乙烯链段在表面富集。     

四配位硅与丙烯酸甲酯共聚物的制备及其性能

以SiO_2为起始反应物,与乙二醇、氢氧化钾反应,生成高反应活性的五配位硅钾化合物,并以此为原料与等摩尔比的对苄氯苯乙烯反应制备出含双键单官能团的四配位硅单体;然后与丙烯酸甲酯在甲苯溶剂中进行溶液自由基聚合反应,得到支链含硅共聚物。对合成的四配位硅单体及其共聚物采用红外光谱、元素分析、能谱元素分析、热失重分析、差示扫描量热谱分析、凝胶渗透色谱等测试技术进行了结构表征与性能分析。结果表明．四配位硅单体在1 630 cm~(-1)附近的C=C伸缩振动吸收峰在共聚物中消失了,说明共聚反应完全;共聚物的热性能较好．在357℃开始失重;共聚物的玻璃化转变温度为23．4℃,刚好界于聚丙烯酸甲酯的T_g(8℃)和苯乙烯基四配位硅的均聚物的T_8(32．8℃)之间;共聚物的数均分子量为2．2×10~4,多分散系数为1．76。通过测定共聚物在潮湿空气中(相对湿度RH=90％)放置一年后的IR谱和分子量,结果表明与新合成物的数据基本一致,说明Si—O—C键接到支链上的共聚物结构很稳定。     

SEQUENCE STRUCTURE OF ETHYLENE-VINYL SUBSTITUTED COPOLYMER WITH ~(13)C NMR IV——CHLORINATED POLYETHYLENE

The substituent chemical shift (SCS) has been applied to the assignment of the ~(13)C NMRspectrum of chlorinated polyethylene (CPE). CPE of different chlorine contents has been em-ployed and their sequence structure discussed. The results show that characteristic of CPEwith medium chlorine content is the dichloroethane structure in molecular chain. SCS param-etets have been obtained from the ~(13)C NMR spectra. It was found that the effects of chlorinecontent and temperature on SCS are negligible, but the substituent parameter S_1 reduced by0.39 ppm when C_2Cl_4 was added to solvent ODCB.     

Carbon-13 NMR spectra of DDT,its analogues and related compounds

Carbon-13 NMR spectra of mono- and disubstituted aromatic compounds including DDT, its analogues, homologues, derivatives and certain model compounds have been studied. The Savitsky scheme of carbon chemical shifts in disubstituted benzenes is applicable to these compounds. The data obtained show that in mono- and disubstituted aromatic compounds containing two different substituents in the α- and β-positions of the side chain, the substituted ring carbon atom shifts follow the additivity rule and can be calculated from substituent increments. Mutual effects of substituents in the ring and in the side chains are analysed. The chlorine atoms in α-position to the phenyl ring give rise to an additive α-effect of about 25 ppm, as in perchloroalkanes. The influence of a β-chlorine atom in the side chain on the substituted carbon atom in the ring is, however, only 3 ppm as against the usual value of about 10 ppm for the β-effect in alkyl chains. Moreover, the first β-chlorine substituent has no noticeable influence on the substituted ring carbon chemical shift: the effect of 3 ppm is transferred to the para-carbon atom almost without attenuation. The ring substituted carbon atom signal shifts caused by the γ-effect of chlorine in the side chain are similar to those observed in aliphatic chains. The ortho-chlorine substituents shift the side chain α-carbon atom signal by 3.6-5.2 ppm to high field compared to para-chlorophenyl compounds. This is similar to the chlorine γ-effect in aliphatic chains.     

The photo-chlorination of polystyrene

Polystyrene and poly-β,β-dideuterostyrene have been photo-chlorinated in solution in carbon tetrachloride. The products have been examined by i.r., 220 MHz NMR and laser Raman spectroscopy. For chlorination at 13°, approximately equal numbers of chlorine atoms are introduced at α- and β-sites along the chain; in the later stages of reaction, there is appreciable addition of chlorine to the rings. The photo-chlorination is accompanied by degradation of the polymer; the average number of scissions per polymer molecule is better correlated with the amount of chlorine introduced into the main chain than with the total chlorine content of the polymer.     

Deterioration of polyethylene pipes exposed to water containing chlorine dioxide

Chlorine species used as disinfectants in tap water have a deteriorating effect on many materials including polyethylene. There are only very few scientific reports on the effect on polyethylene pipes of water containing chlorine dioxide. Medium-density polyethylene pipes stabilized with hindered phenol and phosphite antioxidants were pressure tested with water containing 4 ppm chlorine dioxide at 90 °C and pH = 6.8 as internal medium. The stabilizers were rapidly consumed towards the inner pipe wall; the rate of consumption was four times greater than in chlorinated water (4 ppm, pH = 6.8) at the same temperature. The depletion of stabilizer occurred far into the pipe wall. A supplementary study on a polymer analogue (squalane) containing the same stabilizer package showed that the consumption of the phenolic antioxidant was 2.5 times faster when exposed water containing chlorine dioxide than on exposure to chlorinated water. The subsequent polymer degradation was an immediate surface reaction. It was confirmed by differential scanning calorimetry, infrared spectroscopy and size exclusion chromatography that in the surface layer which came into contact with the oxidising medium, the amorphous component of the polymer was heavily oxidized leaving a highly crystalline powder with many carboxylic acid chain ends in extended and once-folded chains. Scanning electron microscopy showed that propagation of cracks through the pipe wall was assisted by polymer degradation.     

The effect of a carbon-carbon double bond on electron beam-generated plasma decomposition of trichloroethylene and 1,1,1-trichloroethane

The effect of a carbon-carbon double bond on the energy required for decomposition in an electron beam-generated plasma reactor is studied by comparing the decomposition of trichloroethylene and 1,1,1-trichloroethane. A reaction mechanism for TCE decomposition based on a chlorine radical chain reaction is presented which accounts for the formation of all of the experimentally observed reaction products. TCE decomposition is autocatalyzed by reaction products, whereas TCA decomposition is inhibited. The rate expression for the decomposition of TCE in the reactor is determined to be r=−[T](15.07[T₀]^−0.40+0.006{[T₀]−[T]}), where [T] and [T₀] are both in ppm, and r is in ppm Mrad⁻¹. The energy expense ɛ for TCE decomposition is determined as a function of inlet concentration. For 99% decomposition of 100 ppm TCE in air, ɛ=28 eV/molecule, and ɛ=2.5 eV/molecule at 3000 ppm. This is only 2.5–5% of the amount of energy required to decompose a similar amount of TCA as reported by the authors in a previous study. By comparing the energy requirements for TCE decomposition to those for TCA decomposition, the TCE reaction chain length is determined to increase from approximately 20 at 100 ppm initial TCE concentration, to 40 at 3000 ppm. This work was supported by the Contaminant Plume Containment and Remediation Focus Area, Office of Environmental Management, U.S. Department of Energy.     

Continuous Flow Determination of Residual Aqueous Ozone With Membrane Separation-Chemiluminescent Detection

Abstract

A method for the determination of ultra-trace aqueous ozone utilizing a membrane-separation process and a chemiluminescent detector is proposed. The microporous PTFE tube was used as separator to transfer aqueous ozone into a gas phase. Air bubbling was used to enhance the separation. Chemilumi nescent signals produced from the reaction of ozone with ethylene in air were linearly proportional to concentration of aqueous ozone from 8 ppb to 9.5 ppm. The relative standard deviation (n=4) was 3.5% at 0.2 ppm. The time it took from starting the sample flow until the signal to reach a stable level was 1.5 min. The interference from chromium(VI), manganese(VII), chlorine, bromine, phthalate, and sulfophthalate was completely eliminated.     

Aluminum Alkyls as Highly Active Catalytic Chain Transfer Agents

During the production of free radical initiated low‐density polyethylene (LDPE), it was discovered that the addition of low levels of alkyl aluminum compounds caused the molecular weight of the LDPE to drop precipitously. Further investigation demonstrated that aluminum‐alkyl compounds are among the most effective chain transfer agents ever utilized. It was also shown that polymer chains, which transfer to Al alkyl species, contain almost exclusively vinyl terminated end groups. A catalytic chain transfer mechanism is proposed in which chain transfer occurs from a growing polymer chain to an aluminum center followed by beta hydride elimination to produce a vinyl terminated polymer chain and a new aluminum hydride bond. This new aluminum hydride bond can then undergo further chain transfer reactions. This is the first time such a catalytic chain transfer mechanism has been reported. As little as 10–20 mol ppm aluminum alkyl species decreased the degree of polymerization by a factor of 2 resulting in chain transfer constant (C_s) values as high as 1000–2000. Density functional theory (DFT) study elucidated the catalytic cycle of triethylaluminum (TEA). It is discovered that, depending on the reaction conditions, TEA can serve as a conventional as well as catalytic chain transfer agent.     

Polybutene-1 pipes exposed to pressurized chlorinated water: Lifetime and antioxidant consumption

Pipes of isotactic polybutene-1 were pressure-tested in chlorinated water at a controlled pH (6.5 ± 0.1), and the lifetime was assessed as a function of temperature (95-115 °C) and chlorine content (≤3 ppm). These data were compared with data from pressure testing in hot water (0 ppm chlorine). The lifetime shortening in chlorinated water was significant even at relatively low chlorine contents, 0.5 ppm. A further increase in chlorine content led only to a moderate shortening of the lifetime. The temperature dependence of the lifetime data obeyed the Arrhenius law. The activation energy obtained for failure data in chlorinated water was ∼140 kJ mol⁻¹, which was greater than the value of 108 kJ mol⁻¹ earlier reported for failure data from hot-water pressure testing. A 0.5-mm thick layer of material at the inner wall in the fractured pipes showed depletion of the antioxidant system and the inner wall displayed a large number of surface cracks, confirming that there was a pronounced chemical degradation of the inner wall material. The decrease in the antioxidant concentration was independent of the chlorine concentration in the range 0.5-1.5 ppm. The time to reach depletion of the antioxidant system could be predicted by linear extrapolation in an oxidation induction time (log scale)-exposure time (linear scale) diagram.     

Relationship among iodine, bromine and chlorine concentrations in cow's milk in Japan

In order to know the relationship among some elements in biological materials, iodine, bromine and chlorine concentrations in cow's milk samples in Japan were determined by the thermal neutron activation analysis using a low power research reactor and a Van de Graaff accelerator. The iodine contents in cow's milk samples ranged from 0.041 to 0.316 ppm with an average of 0.096 ppm. The bromine and chlorine in these samples ranged from 2.3 to 11.1 ppm and from 475 to 1650 ppm, respectively. The average concentration of the bromine was calculated to be 5.6 ppm and that of the chlorine was 853 ppm. The relationship among iodine, bromine and chlorine concentrations in cow's milk samples in Japan was studied with a regression analysis. It was suggested that the correlation has a power function as follows; Y = K(Z)-A where, Y is elemental concentration in ppm, Z is atomic weight [corrected] of element, A (= 7.4) is exponent and K (= 14.7) is a constant.     

New approaches to the study of labile structures in poly(vinyl chloride) by phenolysis

Three samples of PVC having different tacticities were treated with phenol in cyclohexanone at 60° until there was no more reaction (96 hr). The incorporation of phenate into the chain was observed by u.v.-visible spectroscopy. The phenolysis extent was shown to be lower as the syndiotactic content of the polymer increased. On the other hand, the modified polymers showed enhanced thermal stability relative to the starting materials particularly for the more isotactic sample. The observed behaviour of either the starting materials in phenolysis or the treated polymers in thermal degradation appears to be very similar to that observed previously in the reaction with sodium thiophenate. On the basis of this similarity, it might be concluded that the phenolysis occurs with chlorine atoms at isotactic placements. That effect would confirm the thermal lability of some normal chlorine atoms as indicated by other results.