Document G627Bx0Z7V2DL5M2gQmM9y3w7

-- EnmrrmmmUil Haiti PtrtpKtiva Vo1.11, pp. ISi-ltS, mi Poly(vinyl Chloride) Processes and Products by R. N. Wheeler, Jr.* Poiyivinyl chloride) mine vt produced by four basic procoMt: nupeneion, emuleion, bulk and eoluiion polymerization. PVC euepeneion min. an usually relatively duit-fne and pianular with vatying depreee of particle poroelty. PVC emulsion resins an small particle powders containinp very little free monomer. Bulk PVC resins are similar to suspension PVC resins, though the particles tend to be more porous. Solution PVC reiina an smaller in particle size than suspension PVC with high porosity particles containinp essentially no free monomer. The variety of PVC rain products does not lend itself to broad generalisations concerning health hazards. In studying occupational hazards the particular PVC process and the product must be considered and identified in the study. Poly(vinyl chloride) is a ubiquitous part of our environment today, in that it appears in clothing, upholstery, flooring, wire insulation, food contain ers, phonograph records and an almost infinite variety of other items. Despite this wide applica tion and the size of the industry there is little public understanding of the term. A part of this confusion stems from the human inclination to abbreviate terms--thus, we say PVC when discussing poly(vinyl chloride) resins, poly(vinyl chloride) latexes, poly(vinyl chloride) compounds, polyfvinyl chloride) film and so forth. This confusion has been accentu ated by governmental regulators, who define PVC as a polymer containing any amount of vinyl chlo ride. On taking these two factors into account it has become almost impossible to distinguish what is meant when the term PVC is used in the various media. In order to study possible PVC industryrelated health problems one must know something of the various processes and products to properly evaluate study results. Many study results can have significance only if the source and composition of the PVC is stated. Manufacture of synthetic resins from vinyl chlo ride and other monomers involves reacting these monomers in agitated pressure vessels in the pres ence of catalysts and converting these liquids and/or gases to solid resins. A considerable amount of heat *Uwon Czrbide Corporation, P O. Box 8361, South Charleston, West Virginia 25803. October 1981 is generated by the reaction. This is removed by cooling the vessel. As the monomer is converted to polymer during the reaction, the rate of reaction slows down; thus, after some optimum reaction time, the unconverted remaining monomer is re moved from the reacting mass by heat and vacuum and the resin (PVC) is recovered as a dried white powder or as a liquid latex or solution. This polymerization reaction may take place in pure monomer, in a solution, in a water-monomer emul sion or in a water suspension of monomer. The nature of the polymerization process determines the nature of the subsequent recovery process, and the nature ofthe resin particles produced. Current ly there are four basic vinyl chloride polymerization techniques which give use to the following four processes; (1) suspension polymerization, (2) emul sion polymerization, (3) bulk polymerization, and (4) solution polymerization. Suspension polymerization is the major process used for the manufacture of PVC resins and is used for about 82-85% of U.S. production (Pig. 1). It involves the charging of one or two parts water and one part vinyl chloride monomer or comonomer mixture to an agitated reactor along with initiator and suspending agents such as poly(vinyl alcohol). The mass is reacted at 50-65'C until about 85-90% of the contained monomer is converted to resin. The resin-water mixture is heated, sometimes under vacuum, until the unconverted monomer is substantially removed. The resin is then removed 123 r from the water and dried in rotary, flash or fluid bed dryers by exposure to heated air. The dried resin is transferred to storage silos, whence it is shipped to fabricating plants in bulk containers or in paper bags. If only vinyl chloride monomer is reacted, the product is PVC homopolymer. If a monomer such as vinyl acetate is mixed with the vinyl chloride then a PVC copolymer is produced. The advantages of the suspension resin process are its high productivity per unit reactor volume, its flexibility with regard to polymer composition and resin particle characteristics and the granular nature of its product. The relatively large resin particles (50 to 150 pm) cause problems in removing unconverted vinyl chloride monomer. The mono mer tends to diffuse slowly from the center of the resin particle to the surface, where it is removed by the monomer recovery operation; thus removal often is incomplete. In the past, residual vinyl chloride monomer concentrations in suspension PVC resins ranged as high as 2000 ppm by weight until improved methods were developed in response to recognized need for lower residual levels. The process produces a wide variety of products, each of which presents different monomer release characteristics as well as differing suitability for particular fabricating operations. As a general rule, small particle size resins have lower residual mo nomer than large particle size; porous particle resins have lower residual monomer than nonporous particle resins; and resins containing little or no comonomer have lower residual monomer than resins with significant amounts of comonomer. The relatively large suspension resin particle, while retaining monomer from the manufacturing pro cess, results in a product that has excellent han dling properties such as bulk flow. Recent improvements in monomer stripping technology have resulted in most PVC suspension homopolymer resins containing about 10 ppm residual vinyl chloride monomer at the time of shipment while the residual vinyl chloride monomer in most copoly mers ranges from 25 to 200 ppm at the time of shipment. The stress on residual monomer content at the time of shipment in the preceding paragraph is purposeful. Vinyl chloride monomer is not soluble in the PVC nor is it absorbed or adsorbed in the resin particle. It is entrapped, and, given an opportunity, it escapes to the ambient air. Keating tends to accelerate this escape. PVC resin in a bulk-container loses its residual monomer at a rate of 25 to 50% per month. PVC resin in a paper bag loses its residual vinyl chloride monomer at an approximate rate of 75% per week. Once the residual monomer is gone, there is no source of monomer from the PVC resin, i.e., the resin does not decompose to yield significant amounts of monomer. If heated, the resin gives oft hydrogen chloride and turns black. Thus a year-old PVC resin contains almost no residual monomer; on heating until it blackens it will always give off hydrogen chloride. PVC resin fabricating operations drive off the free residual monomer in the ftrst heating step; thus the probability of a toxic response from vinyl chloride monomer contained in the vinyl film or moldings produced is remote. All PVC processes have a problem with reactor system fouling to some degree. The conversion of a liquid monomer to a high molecular weight solid polymer while contacting reactor walls, baffles and so forth results in the deposition of some of that solid polymer on surfaces. This deposition or foul ing interferes with the reactor operation so that periodically it has to be removed. In earlier times, this was removed manually by a man working in a shutdown reactor. These reactor cleaners were exposed to very high concentrations of vinyl chlo ride monomer (several thousand ppm). It was within the group of men in this cleaning operation that the excess of angiosarcoma was observed by Creech (1). More recently, techniques to minimize fouling and techniques for cleaning such as solvent washing and hydroblasting have reduced or elimi nated the need for reactor entry and cleaning. Emulsion polymerization is the second most wide ly used process for the manufacture of PVC reBins and comprises 10-12% oftotal U.S. production. One of the important things to understand about emul sion polymerization is that it is not a single process but a large family of processes, each producing specialized products that are defined or specifled in terms of performance in a particular application. In the interest of brevity, the two major process families will be discussed: the water-soluble initiator system and the oil-soluble initiator system (Fig. 2). In the water-soluble initiator system, one to two parts water, one part monomer, 0.01 to 0.03 parts surfactant and water-soluble initiator (a redox system or a persulfate salt) are charged or fed to an agitated reactor and reacted at 30-00C to form a synthetic latex. The reactor agitation must be sufficiently vigorous to emulsify the monomerwater mixture but not so vigorous that the latex is coagulated. When 80-95% of the monomer is con verted to polymer, the latex may be gently.stripped of the unconverted monomer with heat and vacu um, or it may be subjected to a second initiator treatment and reacted to essentially 100% mono mer conversion. The product of this polymerization may be simply filtered and shipped to consumers as a latex for coatings, mastics, and the like, or the polymer may be recovered as a dry resin. Recovery techniques vary. The most commonly used is sim ply spray-drying of the latex, though some resins are recovered by coagulating the latex and dewa tering with subsequent drying of the coaguhim (resin). In the oil-soluble initiator system, one part monomer containing an organic peroxide is emulsified in one to two parts water containing 0.01 to 0,03 parts surfactant. The resulting emulsion is reacted at 30-60C to form a synthetic latex. Approximate ly 80-90% of the monomer is converted to polymer. After reaction, the latex is gently heated and vacuum-treated to remove the unconverted mono mer. After stripping, the latex may be shipped as a product though most of it is converted to a dry powder by spray-drying. The bask difference be tween the oil-soluble initiator process and the water-soluble initiator is that the size ofthe emulsified monomer particle determines the resin particle size in the oil-soluble initiator process, while polymer ization technique determines the resin particle size 124 h--i C/i (Jj *tober 1981 SVC LATEX Fwure 2. Emulsion polymerization process. 125 in the water initiator process. The resin particles formed during emulsion polymerization range in size from 0.05 to 2 pm. In the course of recovery and drying these may be agglomerated to particles as large as 30 pm. For some uses the agglomerates may be ground to a median particle size of about 2 pm. The small particle size results in rapid loss of residual vinyl chloride so that the resin contains about 1 ppm free monomer as produced. Because of handling problems, nearly all the resin iB bagged, letting the small amount of monomer retained escape easily before it arrives at a fabricating plant. Nearly all dried emulsion process PVC resin is utilized by paste or dispersion fabrication tech niques. The resin, pigments and other additives are stirred into plasticizer, yielding a thick viscous liquid piastisol. This plastisol 1b spread on a doth or a paper or poured into molds. The coated mold or doth is heated, causing the resin and plasticizer to fuse into a solid forming the finished plastic article. In this fashion, the Bmall manufacturer or the producer of elaborate shapeB or highly styled items can make a product with a minimum capital invest ment. The emulsion polymerization process, in addition to the reactor fouling problem noted for suspension polymerization, has less flexibility with regard to changes in process conditions. Each change in reaction, stripping or drying has an identifiable effect on product properties and quality. Some of these properties are well known, and quality tests keep them under control. Others are not well known and are recognized when customers com plain. Emulsion process resins cost more to pro duce, and plant operators tend to be very conservative in the approach to process changes. Because of this difficulty, emulsion process plants tend to emit more vinyl chloride monomer to the ambient air per pound of resin produced. In Europe particularly there have been reports of worker dermatitis from surfactants and passible pneumoconiosis horn resin dust inhalation in the emulsion process plants (2-J). Bulk polymerization is the third mqjor process in terms of volume for the manufacture of PVC resins but supplies only about 5% of U.S. production (Fig. 3). The process involves the charging of vinyl chloride monomer and initiator to a first-stage polymerizer, where about 10% of the monomer is converted to polymer. Hus batch is then transfer red to a second-Btage polymerizer where additional monomer, and sometimes initiator, are added. The polymerization is continued until about 80-85% of the container monomer is converted to polymer. The unreacted vinyl chloride is removed by heat and vacuum and the finished resin product trans ferred to Btorage bins for later shipment to fabricat ing plants. The absence ofwater in the polymerization stage eliminates the need for the drying step and provides some economy in capital and operating costs. The advantages of the bulk process are its simplicity, the uniformity of the reBin particle size, the high porosity of the resin particles and the purity ofthe polymer (no soaps or suspending aids). The disadvantages are: less flexibility in product mix (homopolymers only) than the suspension pro cess and poorer removal of residual VCM. These bulk process resins are generally directly competi tive with suspension process PVC homopolymers. The relatively large porous resin particles (50 to 150 |im) tend not to retain monomer, thus removal of residual VCM is theoretically easy. The transfer of heat from the reactor wall to the resin particle for stripping is poor thus offsetting the advantages gained by the high particle porosity in removing residual VCM. In the early 1070s, residual VCM in this type ofresin was of the order of 1000 ppm when produced, but more recently these resins have less than 50 ppm in residual VCM when produced. Solution polymerization is a process unique to Union Carbide Corporation and accounts for about 2% of the total resin produced (Fig. 4). Vinyl chloride monomer, comonomer, solvent and initia tor are fed to a continuous reactor system. The polymer formed is soluble in the reacting mass so that the reactor product is a viscous resin solution. This solution is distilled to remove the unconverted vinyl chloride monomer, and the resin product is recovered by treating the resin solution with water and drying the product. The reBin particle is very porous, is always a copolymer, is free of soaps and suspending agents, has a median particle size of 75 tun and contains less than 0.2 ppm residual VCM. Manufacturing investment is high, and the product finds its greatest use as a coating material, i.e., paints and lacquers, that utilize its good dissolving qualities. It iB used in relatively small quantities, and is nearly always shipped in bags rather than bulk. In addition to the basic PVC resins described earlier, there is a wide variety of resin powders, pellets, liquids and latexes in commerce that fall , under the general designation of PVC. These are chemically or mechanically converted PVC resins such as post-chlorinated resins and compounded resins containing plasticizers, stabilizers and the like. As a general rule, the additional processing has removed essentially all ofthe residual VCM and agglomerated the dusts. Converted PVC resins have no involvement with problems related to vinyl chloride monomer exposure. Conclusions Poly(vinyl chloride) resins are produced by four basic techniques: suspension, emulsion, bulk anti solution polymerization. The variety of PVC resin products does not lend itself to broad generalizations concerning hazard to worker health. In evaluating occupational hazards, the PV( process, the PVC product and other material, present must be considered before valid conclusion, can be reached. WATER VERT 12* o 00 October 1981 WASTE WATER Figure 4. Solvent vinyl resin process. If REFERENCES * Mikk, L. Liver disease among polyvinyl workera- Ann, N.Y, Acad, Sa. 246: ' inTM' !`f *>TM*4n' ^ ' Elena, Pauduram, A., and Pascu, Livia. Clinical manifestations in vinyl chloride poi~ oiung, Ann. N.Y, Acad. Sd. 246: 53-69 (1975) HttNEDUWim Qi ncf'ADHC 128 Environmental Health Perspectives