关于混有二氧化钛的氧化镁在PVC门窗型材中的可用性研究 毕业论文外文资料翻译

关于混有二氧化钛的氧化镁在PVC门窗型材中的可用性研究 毕业外文资料翻译 外文资料翻译 A study on usability of magnesium oxide with titanium dioxide in PVC door and window profiles 1. Introduction Polyvinyl chloride is among the most widely used synthetic organic polymer materials. Plasticized polyvinyl chloride compositions are widely encountered as, for instance,vinyl sheet goods and as objects formed from plastisols.Polyvinyl chloride is commercially available in a variety of grades, some of which are suitable for preparing rigid,plasticizer-free compositions for extrusion . For plastics, prolonged exposure to the sun’s electromagnetic radiation in the ultraviolet (UV) region can lead to photooxdiation and degradation of physical properties, often manifested by color change and embrittlement. Similarly,the UV component of ordinary fluorescent lighting can degrade polymers and many of the additives used with them. The effective UV radiation that does reach the earth’s surface extends from about 290–400 nm. This range happens to include the highest energy component UV band, and the segment around 300 nm, which is the most distractive to plastics. Some man-made high-energy radiation sources mercury arc lamps, xenon arcs, carbon arcs, and various sun-lamps can emit radiation at wave lengths below 290 nm and these can degrade plastics even more severely than natural sun light. Hence, they are often used for accelerated testing of plastics. The energy content of UV radiation in the 290–400 nm can rupture most of the chemical bonds present in polymer structures. Not all the polymers are equally affected by UV radiation, and some have a degree of resistance, otably polymethyl methacrylates and fluorocarbons. Others, that in their pure forms could be expected to be resistant to UV, are degraded because of contaminants 1 present that act as sites for UV energy absorption. Absorption of radiation energy by polymer produces molecular excitations: if the level of absorbed energy is high enough, it can activate a chemical reaction whereby internal bonds (carbon to carbon, carbon to hydrogen, carbon to halogen, etc.) are broken so that polymer degradation results. PVC is damaged by dehydrochlorination (release of hydrogen chloride), autooxidation and echanochemical chain scission. This degradation is caused by the simultaneous sequence of these reactions. Dehydrochlorination, prevailing reaction during processing,leads to increasing discoloration. In the course of the proceeding degradation the physical properties are also changed in the direction of increasing embrittlement. PVC of ideal constitution should be thermally stable, which was concluded from investigations with model substances. Therefore, it has to be assumed that the damage, articularly the dehydrochlorinations, starts from sites of the macromolecule with labile chlorine–carbon bonds. PVC can be degraded by heat and sun lights. The release of hydrogen chloride, which is the indication of PVC degradation in prolonged exposure to the sun’s electromagnetic radiation in the UV region, is occurred according to the following reactions: Heat，，,(CH,CHCl),,,,,,CH,CH,，nHCl2nn The color of PVC-based article is changed from yellow to black according to degrees of the degradation. Once the reaction has started, polymers quickly and progressively experience changes in appearance: surface qualities, gloss, chalking, color, electrical properties, tensile strength and elongation; and can reach the end points of embrittlement and total disintegration. The degradation of polymers exposed to UV, often described as photodegradation and frequently identified as photooxidation, can follow various routes. By absorbing UV radiation directly, a polymer molecule can reach a high-energy excited state where it becomes unstable. If the excess 2 energy can be dissipated in a fashion that does not affect the molecule by making it phosphoresce or fluoresce, or by converting the energy to heat that can be carried away, or by transferring the energy to another molecule, photochemical reaction does not started and thus, polymer degradation will not happen. However, such actions occur only rarely, since most polymers cannot dispose of the excitation energy without undergoing a chemical reaction that sets off a degradative process. In theory, many pure polymers should not absorb UV radiation, and thus, not be subject to photodegradation. However, in practice the most polymers contain impurities such as carbonyl or carboxy groups or hydroperoxides that readily absorb radiation in the 290–400 nm range causing them to break down. Thus, generating sites within the polymer structure where chemical reactions can be initiated and propagated by free radicals. The active groups may be unavoidably present as a result of reactions that occur during polymerization. Similarly, metallic ions are present in most polymers as residues from polymerization catalysts, or as constituents of compounding additives such as heat stabilizers, antioxidants, colorants, fillers and others. The metal ions are highly receptive to the absorption of UV radiation, and are efficient in transferring the absorbed energy to the polymer molecules around them, thus, they act as photo-sensitizers and can promote degradation at the same time that they perform their desired functions. Another contributor to photodegradation of polymers is oxygen, which helps any free radicals that may be liberated by the UV to initiate and propagate oxidation of the polymer, hence, the term photooxidation. Polyvinyl chloride suffers from poor heat stability. Its degradation occurs by autocatalytic dehydrochlorination initiated at the labile sites in the polymer chains. This leads to severe discoloration and loss of mechanical properties. The dehydrochlorination most probably proceeds by a chain mechanism involving radical intermediates. Various defect sites in PVC are branching. Inorganic and organic thermal stabilizers are commonly added to protect 3 the polymer from heat degradation. Among the most widely used ultraviolet stabilizers is titanium dioxide pigment. Filling a polyvinyl chloride composition with this pigment substantially reduces the effective depth of penetration of ultraviolet light into the surface of an article formed from such a composition. Mohamed et al. pointed out that barbituric acid and thiobarbituric acid are nontoxic organics, thermally stable materials of high melting point. Both contain active methylene groups, and can act as H-donor through their enolic hydrogen groups, which can intervene with the radical species derived from the thermal degradation of PVC. They investigated the possibility of using barbituric acid and its thioanalogue as thermal stabilizers for rigid PVC. The effective stabilization often requires a combination of antioxidant system in which complementary overlap of different mechanistic pathways involved. This act often referred to as synergism, is the motivation for the use of admixing composition of dibutyltin maleate and trinitro and its ester homologues. The stabilization agents of dibutyltin maleate and trinitro esters could retard somewhat the photodegradation of PVC. It is hoped that the total stabilizing effect of this admixed system should be greater than the sum of the individual effects when PVC is subjected to an environment where the effects of heat and UV are combined. Turoti et al. investigated the effect of the stabilizing action of admixed mixtures of dibutyltin maleate and trinitro and its ester homologues on polyvinyl chloride exposed to natural atmosphere. In their study, the degradation and stabilization reactions were monitored by color formation, tensile strength and elongation at break, reduced viscosity as well as determination of time to embrittlement. It is observed that the stabilized PVC sample has an effective reduction in degradation reactions. Titanium dioxide is by far the most important of white inorganic pigments and possesses all-round suitability. While rutile titanium dioxide is highly reflective at visible wavelengths, it is also highly absorptive at ultraviolet wavelengths. However, although titanium dioxide is a highly effective 4 ultraviolet light stabilizer for polyvinyl chloride compositions, it does have several serious drawbacks. An important disadvantage is the cost of titanium dioxide which has historically tended to be high compared with filler or extender pigments such as calcium carbonate and talc. Another significant disadvantage of using titanium dioxide as an ultraviolet stabilizer in unplasticized polyvinyl chloride compositions is that historically titanium dioxide has been periodically in short supply. The relatively high cost of titanium dioxide is an especially significant disadvantage for the manufacture of articles for exterior use from unplasticized polyvinyl chloride compositions because such articles must often have substantially greater dimensions, for structural reasons than the effective penetration depth of ultraviolet light in the articles. Thus, it is highly desirable to able to reduce the level of titanium dioxide in such a composition without experiencing an accompanying increase in the rate of degradation and reduction in service life. Although it seems to decrease the level of titanium dioxide in the PVC composition will tend to increase the effective penetration depth of ultraviolet length and will consequently accelerate the degradation of the PVC, the experimental observations do not support such an expectation. Since PVC compositions consist generally of from about 0.5–5 parts by weight of rutile titanium dioxide per hundred parts by weight of the polyvinyl chloride, there is no guarantee for the bulk of titanium dioxide to locate near the external surfaces of articles exposed to sun lights. In this study, usability of magnesium oxide with titanium dioxide in the PVC compositions for forming of the exterior articles such as door and window profile is investigated in terms of determining discoloration and some mechanical properties of the articles under accelerated weathering test. 2. Materials and methods PVC compositions widely used to form the exterior articles such as door and window profiles consist essentially of about five parts (by weight) stabilizers, five parts rutile titanium dioxide, five parts fillers, and 0.1-3 parts 5 process aids per hundred parts by weight of the polyvinyl chloride resin. Polyvinyl chloride is subject to thermal degradation by dehydrochlorination. Since many processes for forming useful objects from polyvinyl chloride compositions, such as extrusion and molding, subject the composition to elevate temperatures, most include thermal stabilizing agents that tend to inhibit thermal degradation of the polymer during processing. Example of commonly employed thermal stabilization agents includes barium/cadmium and organotins including mercaptides, maleates and carboxylates. Polyvinyl chloride is also subject to degradation by exposure to ultraviolet light. Articles formed from polyvinyl chloride compositions, which are exposed to ultraviolet light such as vinyl siding and vinyl window and window frame components typically include an ultraviolet stabilizer. In this study, five different compositions of PVC were used to fabricate door and window profiles. These profiles are faded under accelerated weathering conditions. Discoloration and some mechanical properties of the profiles are determined to choose the most suitable polyvinyl chloride composition used to form the exterior articles. For window profiles up to nine repeated extrusion processes were investigated. The properties like impact strength, modulus, Vicat temperature, thermal stability, etc. of recycled window frame profiles from 20 to 25 years old windows are determined, it is shown that such recycled PVC is suitable for reprocessing. The heat impact of PVC bottle materials during the recycling process at 160– 180 , was investigated by IR- and UV-spectroscopy and by DSC. The bottle samples are slightly and considerably affected at these temperatures as shown by determination of the formed decomposition products, colour change, loss of volatile components and peroxide formation in air. However, since these decompositions occurred at about 30 min of experimental time which is about six-fold of that of real process times, the reclaimed material was found recyclable which makes the use of this material 6 in the production of window sections, profiles, pipes and even bottles possible. Investigations on the mechanical properties of recycled PVC bottle material separated from the postconsumer waste stream show significant reduction in strength and ductility. It is believed that the main reason for this is the presence of impurities, especially PET, which although present at levels below 0.5% had a large effect on the properties. Also investigated was the degradation that occurs during multiple reprocessing of recycled PVC from post-consumer bottles using IR-analysis and molecular weight measurements. Batches of recycled flake and powder as well as pure but processed bottle flake materials were subjected to simulated multiple recycling using a torque rheometer. The results indicated a rapid degradation of the recycled material compared with purer bottle flake PVC. Multiple recycling of bottle flake mixed with 0.2% polyethylene showed that the PE impurities accelerate the degradation process. Restabilization by adding new bottle flake material surprisingly prevented degradation even at small levels of new material (30%) and even after 15 recycling steps. Recycled PVC bottle material can be used successfully in calcium–zinc stabilized PVC foam formulations to produce profiles of saleable quality. Increasing amounts of bottle recyclate had no significant effect on gelation time, melt rheology or plate-out characteristic and gave rise to an improvement on thermal stability. Foam blends can be extruded to produce profiles of good surface finish and low foam density. Up to 100% PVC bottle recyclate did not affect the density, cell structure or impact properties of co-extruded foam profiles. Foamed PVC recyclate can also be used for inner layers in tubes where densities at about 0.5 g/cm3 arepossible. The reuse of recycled PVC in cable insulations is described in Ref. For this purpose, it is necessary to recover copper and PVC from cable forms originating from used motor cars. PVC can be dissolved and separated to be reused in cable and wire insulating. It is reported that cables using 100% recycled PVC have successfully passed preliminary tests. Cable forms with 50% PVC recyclate 7 have been released for the production of new cars by several manufacturers. Since 1990 PVC floor coverings were collected and recycled in Germany. First results and practical experiences are reported in Ref. Other recycling concepts have been developed for use of recycled PVC packaging or bottle material as core in co-extruded cellular profiles. The products had satisfactory density, foam structure, colour and surface finish. Using up to 100% bottle recyclate did not affect the impact properties of the foam profile.Recycled supermarket trays actually gave an improvement in impact properties, probably due to high levels of impact modifier used in tray formulation. Also, recovery and reuse of waste PVC coated fabrics is described, extracting PVC with a selected aqueous ethyl methyl ketone solution. This so-called swelling method is a simple procedure with minimum environmental impact. The behaviour of the swelling system and the swelling properties of recovered components can be characterized by refractive index, swelling degree and the average particle size of recovered PVC. A detailed analysis of the components separated from PVC coated PET fabrics is also described. The recovered PET staple fibre scrap can directly be used to reinforce epoxides or to form a non-woven fabric on a special machine. 2.1. Materials PVC used in the experiments was obtained from Petkim (PVC S27/R-63). The rutile titanium dioxide (Kronos 2220 TiO2) was supplied by Sayman Chemical Materials. Acrilic polymer used in the experiments as a impact modifier was obtained from LG Chemical Ltd (IM 808). TThe tin stabilizer (TIN-41) used in the study was supplied by Kimfor Chemical Ltd. The internal lubricants coded by ESKAY-4 (polyethylene oxide, compound of calcium stearate) and the external lubricants coded by WCBA (polyethylene wax) were also supplied by Kimfor Chemical Ltd. Magnesium oxide was supplied by MAGOX company. 8 中文翻译 关于混有二氧化钛的氧化镁在PVC门窗型材中的可用 性研究 1 简介 聚氯乙烯是最广泛使用的合成有机高分子材料。增塑聚氯乙烯很常见，如乙烯基板材产品和从塑料溶胶中提取的对象。而市面上的各种聚氯乙烯中还有一些可以用于挤出具有刚性且不含增塑剂成分的产品。 塑料长期暴露在阳光下，阳光中的紫外线辐射会导致其物理性能的下降，这种物理性能的下降可以通过颜色变化和脆化降解体现出来。同样，普通荧光灯的紫外线也可以降解聚合物以及聚合物中所使用的多种添加剂。 地表的有效紫外线辐射波波长约为290-400纳米，对塑料降解作用最强的波长为300纳米左右的高能紫外线恰好在这个范围内。而一些人造高能量辐射源如汞弧灯、氙弧灯、碳弧灯以及各种日晒灯能发出波长低于290纳米的辐射波，这些辐射波对塑料的降解作用比自然阳光更强。因此，它们通常用于塑料的加速试验。 波长为290-400纳米的紫外线所含的辐射能可以使目前聚合物中绝大多数的化学键断裂。聚合物对于紫外线辐射的抗性并不相同，如聚甲基丙烯酸酯和碳氟化合物对于紫外线辐射的抗性就比较低。另外有一些能够抗紫外线的纯聚合物则由于会吸收紫外线形成污染源而已经被淘汰。 聚合物分子吸收辐射能会产生跃迁，如果吸收的能量足够多，达到化学键断裂所需要的能量，就会造成碳碳、碳氢、碳卤等内键的断裂，从而使聚合物降解。PVC的降解是脱氯化氢、自动氧化和断链等反应共同作用的结果。 脱氯化氢现象在PVC的加工过程中普遍存在。在降解的过程中PVC的物理性质会发生脆化。通过实物模型得到的理想的PVC的结构应该是稳定的，这就需要假定脱氯化氢的反应是从含有不稳定氯碳键的高分子开始的。热和阳光都可以导致PVC的降解。PVC若长期暴露在阳光中的紫外 9 线下会根据下述反应方程而释放出氯化氢: Heat，，,(CH,CHCl),,,,,,CH,CH,，nHCl2nn 随着反应程度的加剧，PVC的颜色会逐渐由黄色变为黑色。一旦该反应开始，PVC就会迅速并逐步发生外观(如表面质量、光泽、粉化、颜色、电性能、拉伸强度和延伸率)上的变化，并最终达到完全脆化和降解。 聚合物由于暴露于紫外线中而发生的降解可以按照不同的方式进行，这种降解通常被称为光降解，也经常被认定为光氧化反应。聚合物分子可以通过吸收紫外线辐射达到高能量激发态而变得不稳定。 如果多余的能量通过一种不影响聚合物分子本身的方式被消耗掉，例如使它发出荧光或磷光，或者将能量转换成可以被带走的热，或将或将能量转给另一个分子，这样光化学反应就不会发生，聚合物降解也就不会发生。但是，这种方式很少发生，因为大多数的聚合物不能够不经过发生降解反应过程就消耗掉激发能量。 从理论上讲，许多纯聚合物不应该吸收紫外线辐射，因此就不会产生光降解。然而，在实践中大多数聚合物，如含有羰基或羧基或氢过氧化物的聚合物，很容易吸收290-400nm范围内的辐射而导致降解。因此，化学反应可以通过自由基在聚合物结构内发生并扩大。聚合反应过程中产生活性基团是不可避免的。同样，金属离子也会作为催化剂残留物，或复合添加剂(如热稳定剂，抗氧化剂，着色剂，填料和其它助剂)的成分而出现在大多数聚合物中。金属离子极易吸收紫外线辐射，并快速将吸收的能量转移给周围的聚合物分子，因此，金属离子作为光增敏剂，同时能促进降解。 另一种使聚合物产生光降解的是氧气。氧气有助于紫外线产生自由基并传播氧化作用，因此，氧气造成的光降解是长效的。 聚氯乙烯热稳定性很差。其降解以自催化脱氯化氢的方式在聚合物链不稳定处反应。这会导致严重的变色和力学性能的降低。脱氯化氢反应很有可能是一种连锁反应机制，反应过程中会产生自由基中间体。 无机和有机热稳定剂的加入通常可以起到保护聚合物，而使之发生热降解的作用。其中最广泛使用的紫外线稳定剂是二氧化钛颜料。二氧化钛填充聚氯乙烯，在其表面形成一种色素组合，可以大大降低紫外线有效穿 10 透深度。 穆罕默德等人发现，巴比妥酸和硫代巴比妥酸是两种高熔点、无毒的有机热稳定性的材料。这两种材料含有活性亚甲基，可通过自身的烯醇式氢组提供H-，来阻止PVC热降解产生自由基。他们研究了使用巴比妥酸及其硫代物作为硬质PVC热稳定剂的可能性。 有效的稳定往往需要抗氧化系统的结合，这涉及到不同机械作用的互相影响。这种通常被称为协同作用的行为，让他们想到了使用马来酸丁基锡和三硝基及其酯类同系物的共混物。马来酸和硝基二丁基酯的稳定剂可延缓有些PVC的降解。我们希望当PVC受到热和紫外线的共同作用时，这种稳定的复合稳定体系的稳定效果比单独稳定剂的效果总和要好。特罗迪等人研究了二丁基锡和三硝基马来酸及其酯类同系物对自然暴露在大气中的聚氯乙烯的协同稳定效应。他们的研究，通过颜色的变化、拉伸强度和断裂伸长率、粘度的降低和脆裂时间，对降解和稳定反应进行了检测。 钛白粉是目前最重要的白色无机颜料，具有全面的适用性。金红石型钛白粉对可见光有很好的反射作用，并且能够高度吸收紫外线。不过，虽然二氧化钛是一种高效的聚氯乙烯紫外线光稳定剂成分，但它有几个严重的缺点。一个重要的缺点是钛白粉的成本，与碳酸盐和滑石粉等填料或颜料相比，其价格往往要高得多。另一个使用二氧化钛作为硬聚氯乙烯紫外线稳定剂成分的显著缺点是，历史上二氧化钛一直存在周期性供不应求的现象。 二氧化钛是一种成本相对较高的物品外墙使用硬聚氯乙烯成分，因为这类物品必须经常有更大的尺寸大大超过了在文章紫外线的有效穿透深度结构性原因，制造特别是重大的缺点。 成本相对较高，是钛白粉作为制造外墙使用的硬质聚氯乙烯物品的添加成分的一个特别明显的缺点，因为这类物品由于结构性原因经常必须大幅度扩大范围，而不必首要考虑制品的有效紫外线穿透深度。因此，用这样的组合来减少太白粉的使用而不增加制品使用寿命退化和减少的的速度是非常好的做法。虽然看起来减少钛白粉的使用将导致有效的紫外线穿透深度和长度的增加而加快PVC的降解，实际上实验结果并不是这样。由于每百分质量的聚氯乙烯中金红石型钛白粉的添加量一般约为0.5-5分，没 11 有证据表明暴露在阳光下的聚氯乙烯制品的外表面附近聚有大量的钛白粉。 本项研究，通过确定变色和某些条件下加速老化试验的力学性能来研究混有二氧化钛的氧化镁在户外用PVC门窗异型材制品中的可用性。 2 材料和方法 户外用聚氯乙烯门窗异型材产品，每百分质量的聚氯乙烯树脂中通常主要添加有5分的稳定剂，5分金红石型钛白粉，5分填料，0.1-3分的加工助剂。 聚氯乙烯容易因热降解而脱氯化氢。所以在利用聚氯乙烯加工成可用的制品的诸多过程(如挤出成型)中，由于加工温度较高，大部分都加有稳定剂以抑制加工过程中聚合物的热降解。普遍采用的热稳定剂的有钡/镉热稳定体系、有机锡类热稳定剂等。 聚氯乙烯也会因为受到紫外线辐射而降解。因此，由于在户外使而长期接受紫外线辐射的聚氯乙烯制品，如乙烯基壁板、乙烯基窗和窗框组件等通常都添加有紫外线稳定剂。 本项研究，采用5种不同组分的PVC来制作门窗型材。并在加速风化条件下对这些制品进行褪色实验。以这些制品的变色情况和一些力学性能为依据，最终从中选出能够良好外观的最适合的聚氯乙烯组分。 对于窗框来说，调查显示至少需要九次的重复挤压工艺。对于已经使用了20年到25年的旧窗来说，冲击强度、模量、维卡温度、热稳定性等一些性能都是一定的，调查也表明,这类回收的聚氯乙烯也适合进行再加工。我们通过红外线和紫外线光谱学和扫描电镜等方法对聚氯乙烯瓶装材料在加工过程中180oc的温度下热冲击进行研究，瓶子样品在这样的温度下或多或少的受到一些影响，影响程度的大小主要取决于先前产品的分解、变色、挥发性组分的损失、在空气中过氧化物的形成等。 关于再回收利用聚氯乙烯瓶装材料机械性能的调查表明，使用后的废液在强度和延展度上有很大的降低。人们普遍认为之所以如此，主要是因为有杂质的存在，特别是聚对苯二甲酸乙二醇酯，即使它的浓度很低，在0.5%以下，但是聚对苯二甲酸乙二醇酯对机械性能的影响却是很大。调查 12 的结果表明利用回收材料制成的瓶子比用纯聚氯乙烯材料制成的聚氯乙烯瓶子更容易分解。如果我们把0.2%的聚乙烯和经过多次加工的瓶子薄片混合在一起，那么会由于聚乙烯杂质的影响加速它的降解过程。通过加入新的瓶子薄片材料来进行稳定，那么会非常有效的阻止降解，即使新材料的含量很低(比如30%)、经过了15次循环利用，都非常有效。回收再利用的聚氯乙烯瓶子材料可以成功的应用到钙锌作为稳定剂的聚氯乙烯泡沫材料中，能够制造出质量比较好的产品。随着瓶子材料的数量的增加，并没有给聚合物带来明显的影响，比如说凝胶时间、熔化流变性、电镀性能，也没有提高它的热稳定性。 泡沫混合可以通过挤出完成，生产出来的产品表面性能好、泡沫密度低。泡沫聚氯乙烯材料可以用作管材的内层材料，在这样的情况下， 3的密度并不那么高，大约在0.5g/cm。 在参考文献中我们可以看到用于电缆绝缘材料的聚氯乙烯的回收。用于电缆和电线隔离材料的聚氯乙烯可以被溶解，并被分离出来。有报道曾经描述到用100%?的回收再利用的聚氯乙烯做成的电缆成功的通过了初步的测验。已经有一些厂商用50%?的回收再利用的聚氯乙烯材料制成的电缆用于新车的制造。 在德国自1990年以来就已经有了收集并回收聚氯乙烯地毯的行动了。在参考中报道了聚氯乙烯材料手的第一次结果和经验。 其他一些材料回收的概念是在包装材料和瓶子材料回收以后提出的，这些材料主要是用作内层共同挤出微孔型材的。这些产品拥有令人满意的密度、泡沫结构、色泽和表面性能。用100%的聚氯乙烯瓶子材料制成的泡沫产品并没有对它的性能产生多大的不利影响。再循环超级市场托盘有很好的冲击性能，主要是因为托盘公式中有高的抗冲改性剂。我们经常提到的膨润法是一种比较简单的处理方法，并且对环境的影响较小。膨胀体系和膨胀性能可以用折射指数、膨胀度、平均粒度来表示。由聚对苯二甲酸乙二醇酯纤维作为裹层的的聚氯乙烯的详细分析可以在报道中查到。聚对苯二甲酸乙二醇酯人造纤维可以在一个专门的机器中直接生成非纤维织物。 13 2.1 材料 实验中使用土耳其土耳其石化公司生产的聚氯乙烯(PVC S27/R-63)。金红石钛白粉为Sayman Chemical Materials生产的Kronos 2220 型TiO。2实验中使用LG Chemical Ltd生产的亚力克作为抗冲击改性剂(IM808)。研究中使用的有机锡稳定剂(TIN-41)产自Kimfor Chemical Ltd。内润滑剂(ESKAY-4)为聚环氧乙烷和硬脂酸钙的复合体系，外润滑剂(WCBA)为聚乙烯蜡，二者购自Kimfor Chemical Ltd。氧化镁采用的是MAGOX公司的产品。 14