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Plastic polymers in the wine industry.

Plastics are ubiquitously used in the food and beverage industry and are an alternative to traditional packaging materials for wine. Ingredients used in manufacturing plastics may include additives such as heavy metals that act as catalysts in the plastic polymerization process and plasticizers used to modify and improve the applicability and durability of plastics.

Common plastic ingredients include bisphenols and phthalates. Phthalates are typically used to soften plastics and are used in many products from polyvinyl chloride (PVC), lubricants, emulsifying agents, binders and gelling agents, to enteric coatings on pharmaceutical tablets.

Bisphenols, such as bisphenol A (BPA), are used to harden plastics and include polycarbonate plastics and epoxy coatings. Many additives intercalate within plastic polymers and may leach into materials in contact with the plastic.

As plasticizers, phthalates do not chemically bind to the plastics in which they are mixed, and plastic-bisphenol polymers can be hydrolyzed or may be incompletely polymerized, therefore, both types of chemicals can leach from the products into the environment.

Contamination of wine with plastic additives can occur during processing, storage and transport. GC-MS and LC-MS are among the most common analytical tools to analyze for bisphenols and plasticizers.

Plastic ingredients

Inorganic or organic substances may be added to plastics to enhance the processing and properties of the plastics (e.g. stabilizers, plasticizers, biocides, flame retardants, pigments and others). (11) One of the largest and most controversial groups of additives is plasticizers.

Plasticizers are a class of organic compounds added to plastics to improve flexibility and durability, without which plastic may be too rigid and brittle. (25, 45) PVC polymers use almost 90% of plasticizers produced worldwide. (5)

The most common types of plasticizers are the phthalate esters (Table I). PVC is predominantly plasticized with diethylhexyl phthalate (DEHP). However, due to health concerns and governmental regulatory changes, (14) DEHP use is declining and being replaced with non-phthalate plasticizers such as polyester. (47)

The bisphenols, of which BPA is the most widely used, are used in the production of epoxy resins and polycarbonates. Epoxies are used in applications such as lining metal cans and concrete wine tanks.

Polycarbonate plastics are used in food and beverage storage containers. BPA may also be used as an antioxidant in PVC production. (20)

Health issues

Many plastics have additives or unreacted feedstock of the component plastics that may have biological consequences. BPA and phthalates are used in food and beverage packaging materials, including wine packaging, and have been found to leach into foodstuffs over time. (16,45) Exposures to phthalates and BPA can cause endocrine disruption and estrogenic effects that have been linked to human health problems. (19,25)

BPA has been suggested to alter human development and cause breast and prostate cancers. (2) It leaches from plastic bottles and food packaging, especially when heated or brought into contact with acidic food. (16) This prompted many companies, such as those that manufacture baby bottles, to discontinue the use of BPA in their products. (31)

The European Union and the United States Food and Drug Administration prohibited BPA use in baby bottles in 2011 and 2012, respectively. (29,33) California intends to list BPA on its Prop. 65 list, which lists chemicals known to the state to cause cancer or reproductive toxicity. (30) While many manufacturers have switched from using BPA and claim to be "BPA-free," they may instead be using other bisphenols that also test positive for estrogenic activity. (27)

World production of phthalates is estimated to be several million tons per year. (34,52) Unlike some plasticizers, phthalates are not chemically bound to plastic products and therefore can leach into foodstuffs. (57) The U.S. Environmental Protection Agency (EPA) limits phthalates according to the Phthalates Action Plan, because the amount of leaching into water sources can be toxic to terrestrial and aquatic animals. (35-50)

The most common phthalate is diethylhexyl phthalate (DEHP, CAS 117-81-7), which is regulated under the EPA's Safe Drinking Water Act at a maximum contamination limit of 0.006 mg/L. (49) DEHP is classified by the EPA as a class B2 probable human carcinogen and acts as an endocrine disruptor in the body. (57)

Polyethylene is generally considered to be plasticizer-free. Polyethylene polymers provide ranges of flexibility suitable for various uses and therefore usually do not require plasticizers to alter their flexibility, and bisphenols are not required in their manufacture.

Nevertheless, a study that investigated children's exposure to DEHP and di-n-butylphthalate (DBP) from school meals found that the estimated daily intake for these chemicals was variable but could reach levels near the tolerable daily intake levels set by the European Food Safety Authority. (10)

Polyethylene terephthalate (PET), also known as Dacron, or polyester, is used for bottled water and fruit juices and has been shown to be a source of phthalates as well as antimony, the catalyst used in PET production, especially if stored at elevated temperatures.

In some cases, concentrations of phthalates and antimony in PET-bottled water have been reported to exceed regulated limits. (23-36-46) Recycled PET could be a source of other chemical compounds that may have health implications.

Plastics and plastic additives in wine

Plasticizer contamination is common through storage in plastic containers and possible pollution of raw materials. Recent incidents with plasticizer contamination include a food safety emergency in Taiwan in May 2011. (24-55)

Plasticizers have also been found in Chinese baijiu, a white spirit usually distilled from sorghum or other grains. The Jiungui liquor company found that samples of the product contained 1.04 mg/kg of DBP, which is more than three times higher than the 0.3 mg/kg standard set by the Ministry of Health in June 2011.9-58 Large-scale tests of China's liquor have shown that almost all alcohol products contain an average level of 0.537 mg/ kg of plasticizers. (59) DBP and diisobutyl phthalate were found in more than 94% of food samples, but they were significantly higher in wine and beer compared to other beverages. (22) These chemicals may come from pneumatic press and pump materials, pump lines, storage and transportation vessels and/or added flavorings.

Just as in liquor manufacturing, various stages in winemaking may involve plastic products containing teachable plasticizers and other additives that are potentially extractable if the wine comes in contact with them. In March 2013, three brands of French Cognac were prohibited from entering China's market because they reportedly contained excessive levels of plasticizers. (18)

Plastics are used in the manufacture, transport and storage of wine (Table II). It has been estimated that synthetic closures have taken 19% of the world's closure market, with metal screwcaps making up 11% of the market of approximately 20 billion wine bottles per year. (43)

The use of artificial closures, screwcap plastic liners and other plastic closures or plastic containers such as bag-in-box, may expose wine to plastic leachates that can alter organoleptic properties in the wine as they do with other foods and beverages. (37,53)

A wide range of plasticizers have been used in plastic closures compared to other sources of plasticizers in the winemaking process. (4,39) Saranex used in both screwcap liners and synthetic closures is a barrier film consisting of layers of Saran resin (polyvinylidene chloride, PVDC) and thermoplastic polymer resins. (12)

Plasticizers that have been found in PVC-based films include DEHA and phthalates such as DBP and DEHP. (21) Lowdensity polyethylene (LDPE) is used as a replacement for PVC in Saran, (38) however it provides a poor oxygen barrier and can scalp flavors from foods. (42)

Plastic packaging may scalp the volatile flavors from wine, or the wine may absorb undesirable aromas from the plastic. (32) Packaging materials may also contain BPA, such as plastic stoppers used to seal partially consumed bottles of wine and the lining of concrete fermentors, which are commonly coated with epoxy that may contain PVC. (37,40,44)

Due to the widespread environmental contamination, use and presence of plasticizers and bisphenols, there are a variety of sources of potential contamination in the winemaking process. Besides packaging materials, pumps, tubing, transport containers, pneumatic press material and additives can all contain or be contaminated with plasticizers or bisphenols. (4,6,39)

Options to reduce toxicity due to plasticizer leachate include the use of alternative plasticizers such as the replacement of petroleum-based plasticizers with those derived from natural compounds.

Biopolymers derived from polysaccharides, proteins, lipids and microbes are potential sources for natural plasticizers. Biopolymers have less toxicity, leachability and are biodegradable, however, they tend to have reduced mechanical properties and performance.52 Biopolymers currently only share 5% to 10% of the market and cost more than their non-biopolymer counterparts.

Many petroleum-based plastics contain leachable additives that have the potential for health effects. Nevertheless, many food contact-approved plastic resins, such as specific formulations of polyethylene, currently offer useful functional properties and do not contain additives or other substances that cause cancer, birth defects or reproductive harm at levels that would require a warning under California Prop. 65. (13)

Examples of polyethylene products available to the wine industry include wine bottle closures and wine tanks. Nevertheless, even polyethylene products can contain bioactive ingredients added for various purposes (UV stabilization), but not necessarily in all cases.

While manufacturers may state that their products contain no PVC and phthalates are not added during the production process, the plastics used may contain additives that are not bisphenols or phthalates.

It may be relevant to certain wine producers and their customers that some plastics, such as polyethylene, may contain additives synthesized from animal extracts such as fatty acids produced by the hydrolysis of animal fats (tallow), and there may be corresponding declarations of compliance or noncompliance with various religious dietary laws such as kosher laws. (13)

Concerned users of plastic products may want to contact manufacturers for details about the identity and/or purity of the plastic resin(s) used, notwithstanding nondisclosure of proprietary information.

Currently there is no simple way of identifying the purity of these products except by the manufacturer's resin code and supporting regulatory data sheet, or independent lab tests. Even independent lab testing can yield compromised results due to the use of plastic products in laboratory systems and their potential to contribute leachates. (26)

Naturally, wine producers could also simply continue to employ traditional materials (wood, stainless steel, glass and cork) for production and packaging, which largely avoid potential sources of petroleum or animal-based chemicals.

Analytical methods and results

Bisphenols and phthalates are mostly found at trace levels (nanograms per milliliter or less), therefore analytical quantification in both solids and in liquid samples start with liquid-liquid extraction, solid-phase extraction, or solidphase micro-extraction to concentrate the analytes prior to chromatographic analysis. Phthalate analysis is based mainly on GC-FID, GC-MS, GC/IT-MS, LC-MS, while HPLC and fluorescence detection have been used for bisphenols. (3,7)

DBP, BBP, and DOP have been found in wines, including DEHP at levels exceeding the EPA limit (6 g/L) for DEHP in water, particularly in a wine with synthetic or agglomerated cork stoppers. (7,39) Total phthalates in the wines analyzed ranged between 2.7 and 15 pg/L. (7) BPA also has been found in wine stoppers and wines stored in steel, wood and plastic vats, glass bottles and Tetra Paks (mean concentration 0.58 [micro]g/mL). (3)

Bisphenols and phthalates are present in disposable laboratory plasticware such as pipette tips. Other additives such as oleamide and biocides have been found to leach from laboratory polypropylene disposable plasticware that affected protein function in biological research. (26) Therefore plastic contamination presents significant data compromise challenges.

Similar to materials used in winemaking, laboratories can seek manufacturers that disclose information on the additives content as well as leachable reaction components used in the manufacture of their plastics. Regardless, researchers may still need to confirm the absence of effects or account for them in their assay methods and results.


Plastics and their additives, including those that cause health concerns, are ubiquitous in the environment and in food and beverage processing and packaging materials. There are numerous opportunities for wine to leach additives from plastics. Reported work has shown some wines contain certain plasticizers at concentrations that are prohibitory in some markets.

Wine producers should be aware of the possible sources of plastic additives, the potential for these to accumulate in their products and health concerns and regulations regarding their presence in the "most healthful and hygienic of beverages," (Louis Pasteur).

Improved transparency from manufacturers regarding potential leachates in their products would be helpful as well as increased availability and affordability of alternatives such as bio-based or additive-free plastics.

Other issues to be aware of include plastic permeability to gases such as oxygen, as well as permeability and adsorption/flavor scalping potential of low molecular weight flavor and aroma compounds that could impact the quality of the product that comes into contact with plastics.

Some plastic ingredients may also be objectionable to various market groups such as those that follow certain religious or personal guidelines. HACCP approaches that identify and prevent potential hazards (including marketing hazards) from occurring may lead to safer products and better customer trust, marketability and ultimately sales of a winery's product.


(1.) Amerine, M.A., and M.A. Joslyn. 1970 Table Wines: The Technology of Their Production. University of California Press.

(2.) Barrett, K. 2008 "Safety of water bottles, baby bottles questioned." ABC News.

(3.) Brenn-Struckhofova, Z. and M. Cichna-Markl, 2006 "Determination of bisphenol A in wine by sol-gel immunoaffinity chromatography, HPLC and fluorescence detection. Food Additives & Contaminants 23, 1227-1235.

(4.) Buglass, A.J. 2011 Handbook of alcoholic beverages: technical, analytical and nutritional aspects. John Wiley & Sons. pp. 1086-1090.

(5.) Cadogan, D.F., and C.J. Howick. 2000 Plasticizers, in: Ullmann's Encyclopedia of Industrial Chemistry. Wiley-VCH Verlag GmbH & Co. KGaA. doi: 10.1002/14356007.a20_439.

(6.) Carlo, M.D., A. Pepe G. Sacchetti, JD. Compagnone, D. Mastrocola and C. Cichelli. 2008 "Determination of phthalate esters in wine using solid-phase extraction and gas chromatography-mass spectrometry." Food Chemistry. Ill: 771-777.

(7.) Carrillo, J.D., M.P. Martfnez and M.T. Tena. 2008 "Determination of phthalates in wine by headspace solid-phase microextraction followed by gas chromatography-mass spectrometry: Use of deuterated phthalates as internal standards." J. of Chromatography A 1181, 125-130.

(8.) Cartridges and Elements for Wine Production [WWW Document], n.d.. Pall Corp. URL main/food-and-beverage/cartridges-and-elements (accessed 3.14.14).

(9.) 2012 "Chinese alcohol maker apologizes for contamination [WWW document]." URL 11 /22/content_27200395.htm (accessed 11.13.13).

(10.) Cirillo, T., E. Fasano, E. Castaldi, P. Montuori, and R. Amodio Cocchieri. 2011 "Children's Exposure to Di(2-ethylhexyl)phthalate and Dibutylphthalate Plasticizers from School Meals." J. Agric. Food Chem. 59, 10532-10538. doi: 10.1021/jf2020446.

(11.) Deanin, R.D. 1975 "Additives in plastics." Environ Health Perspect. 11:35-39.

(12.) Dow. 2013 Product Safety Assessment: SARANEXTM Films.

(13.) Dow. 2014 Regulatory Data Sheet: DOW DPDA3135 NT 7 Medium Density Polyethylene Resin.

(14.) EU. 2008 European Union Updated Risk Assessment Report. Bisphenol A, CAS No. 80-057. Institute for Health & Consumer Protection, European Chemicals Bureau, European Commission Joint Research Centre, 3rd Priority List, Luxembourg: Office for Official Publications of the European Communities.

(15.) EU. 2011 Commission Regulation (EU) No 10/2011 of 14 January 2011 on plastic materials and articles intended to come into contact with food (L 12/1, 15.1.2011). Official J. of the European Union. L 12/1, 15.1.201 1. eur-lex. 2011:012:0001:0089:EN:PDF.

(16.) Fasano, E., F. Bono-Blay, T. Cirillo, P. Montuori, and S. Lacorte. 2012 "Migration of phthalates, alkylphenols, bisphenol A and di(2-ethylhexyl)adipate from food packaging." Food Control 27, 132-138.

(17.) Food Storage Containers [WWW Document]. 2011. Nat. Resour. Def. Counc. URL (accessed 6.4.14).

(18.) Global Times. 2013 "Plasticizer scandals dull French cognac luster." [WWW document]. Global Times. 2013-3-3 23:43:01.

(19.) Grignard, E., S. Lapenna, and S. Bremer., 2012 "Weak estrogenic transcriptional activities of Bisphenol A and Bisphenol S." Toxicology in Vitro 26, 727-731.

(20.) Grossman, R.F. (Ed.). 2008 Handbook of Vinyl Formulating, 2nd Edition. John Wiley & Sons.

(21.) Groth, E., and M. Silbergeld. 1998 "Endocrine Disrupting Chemicals in Plastic Wraps: Letter from consumers union to the FDA." Accessed Feb. 2, 2014.

(22.) Guo, Y., Z. Zhang, L. Liu., Y. Li, N. Ren, and K. Kannan. 2012 "Occurrence and profiles of phthalates in foodstuffs from China and their implications for human exposure." J. of Agricultural & Food Chem. 60 (27):6913-6919.

(23.) Hansen, C., A. Tsirigotaki, S.A. Bak, S.A. Pergantis, S. Sturup, B. Gammelgaard, and H.R. Hansen. 2010 "Elevated antimony concentrations in commercial juices." J. Environ. Monit. 12, 822-824. doi: 10.1039/B926551A

(24.) Kang J., S. Chu, Z. Wu, S. Chou, S. Tsai, and W. Chiu. 2012 "Crisis management turns Taiwan's plasticizer nightmare into progressive policy." J. of Formosan Medical Assoc. 111:409-411.

(25.) Latini, G., C. De Felice, and A. Verrotti. 2004. "Plasticizers, infant nutrition and reproductive health." Reproductive Toxicology. 19:27-33.

(26.) McDonald, G.R., A.L Hudson, S.MJ. Dunn, H. You, G.B. Baker, R.M. Whittal, J.W. Martin, A. Jha,

D.E. Edmondson, and A. Holt. 2008 "Bioactive Contaminants Leach from Disposable Laboratory Plasticware." Science 322, 917-917. doi: 10.1 126/science. 1162395.

(27.) Molina-Molina, J.-M., E. Amaya, M. Grimaldi, J.-M Saenz, M. Real, M.F. Fernandez, P. Balaguer, and N. Olea. 2013 "In vitro study on the agonistic and antagonistic activities of bisphenol-S and other bisphenol-A congeners and derivatives via nuclear receptors." Toxicol. Appl. Pharmacol. 272, 127-136. doi: 10.1016/j. taap.2013.05.015

(28.) Nara, K., K. Nishiyama, H. Natsugari, A. Takeshita, and H. Takahashi. 2009 "Leaching of the Plasticizer, Acetyl Tributyl Citrate: (ATBC) from Plastic Kitchen Wrap." J. Health Sci. 55, 281-284. doi: 10.1248/jhs.55.281

(29.) Newman, J. 2010. "BPA in baby bottles banned by European Union." Consumer Reports, news. n ned-by-eu ropea n-un ion. htm I.

(30.) OEHHA. 2013 "Proposition 65 Notice of Intent to List: Bisphenol A. [1/24/13]." Calif. Environ. Prot. Agency's Off. Environ. Health Hazard Assess. OEHHA. URL (accessed 2.2.14).

(31.) Perrone, M. 201 1 "BPA no longer used in bottles, chemical makers say." Huffington Post, 000580.html.

(32.) Peyches-Bach, A., C. Dombre, M. Moutounet, S. Peyron, and P. Chalier. 2012 "Effect of ethanol on the sorption of four targeted wine volatiles compounds in a polyethylene film." J. of Agric.I & Food Chemistry. 60 (27): 6772-6781.

(33.) Raloff, J. 2012. "FDA band BPA in baby bottles, cups." Science News, generic/id/342352/description/FDA_bans_BPA_ in_baby_bottles_cups..

(34.) Rudel, R.A., and I.J. Perovich., 2009 "Endocrine disrupting chemicals in indoor and outdoor air." Atmospheric Environment A3, 170-181.

(35.) Russo, M.V., I. Notardonato, G. Cinelli, and P. Avino. 2012 "Evaluation of an analytical method for determining phthalate esters in wine samples by solid-phase extraction and gas chromatography couples with ion-trap mass spectrometer detector." Anal. Bioanal. Chem. 402 (3): 1373-1381.

(36.) Sax, L. 2009 "Polyethylene Terephthalate May Yield Endocrine Disruptors." Environ. Health Perspect. 118, 445-448. doi: 10.1289/ehp.0901253.

(37.) Scheer, R. and D. Moss. 2012 "Is the plastic in boxed-wine liners BPA-free?" Scientific American.

(38.) S.C. Johnson, n.d. Saran Premium Wrap [WWW Document]. SC Johns. URL aspx (accessed 3.14.14).

(39.) Sendon, R., A. Sanches-Silva, J. Bustos, P. Martin, N. Martinez, and M.E. Cirugeda., 2012 "Detection of migration of phthalates from agglomerated cork stoppers using HPLC-MS/MS." J. Sep. Science 35, 1319-1326.

(40.) Sheftel, V.O. 2000 "Indirect Food Additives and Polymers." CRC Press, pp. 1177.

(41.) Six, T., and A. Feigenbaum. 2003 "Mechanism of migration from agglomerated cork stoppers. Part 2: Safety assessment criteria of agglomerated cork stoppers for champagne wine cork producers, for users and for control laboratories." Food Addit. Contam. 20, 960-971. doi: 10.1080/02652030310001597583

(42.) Smith, J.S. and Y.H. Hui. 2008 Food Processing: Principles and Applications. John Wiley & Sons. pp. 120.

(43.) Steeman, A. 2012 "Wine bottle closures-the synthetic or plastic stopper for wine bottles (Part 4)." Best In Packaging, stopper-for-wine-bottles-part-4/.

(44.) Teichgraeber, T. 2005 "Concrete Fermenters: from old school to New World." Wines & Vines. 22-26.

(45.) Till, D.E., R.C. Reid, P.S. Schwartz, K.R. Sidman, J.R. Valentine, and R.H. Whelan. 1982 "Plasticizer migration from polyvinyl chloride film to solvents and food." Food & Chemical Toxicology. 30: 95-104.

(46.) Tukur, A., L. Sharp, B. Stern, C. Tizaoui, and H. Benkreira. 2012 "PET bottle use patterns and antimony migration into bottled water and soft drinks: the case of British and Nigerian bottles." J. Environ. Monit. 14, 1236-1246. doi: 10.1039/ C2EM10917D.

(47.) U.S. DHHS. 2011 "12th Report on Carcinogens (RoC) - National Toxicology Program." U.S. Dep. Health Hum. Serv. URL.

(48.) U.S. EPA. 1993. Integrated Risk Information System: Bisphenol A. (CASRN 80-057): Oral RfD Assessment: Bisphenol A. (Retrieved Nov. 12, 2013).

(49.) U.S. EPA. 2009 "National Primary Drinking Water Regulations." U.S. Environ. Prot. Agency.

(50.) U.S. EPA., 2012. Phthalates Action Plan [WWW document]. U. S. Environ. Prot. Agency. URL actionplan_revised_2012-03-14.pdf (accessed 3.14.14).

(51.) U.S. FDA. 2013 "CFR - Code of Federal Regulations Title 21: Sec. 165.1 10 Requirements for Specific Standardized Beverages: Bottled Water." U.S. Food Drug Adm. URL cfm?fr=l 65.110 (accessed 11.12.13).

(52.) Viera, M.G.A, M.A. da Silva, L.O. dos Santos, and M.M. Beppu. 2011 "Natural-based plasticizers and biopolymer films: A review." European Polymer J. 47:254-263.

(53.) Wagner, M. and N. Flauser. 2009 "Endocrine disruptors in bottled mineral water: total estrogenic burden and migration from plastic bottles." Environmental Science & Pollution Research. 16: 278-286.

(54.) Wine Filtration Systems, 2011. Available at: webserver?mwsld=SSSSSuH8gc7nZxtUNY_vo8_eevUqe9Uz7vTSevTSeSSSSSS-&fn=70-0201-8684-0. PDF.

(55.) Yen, T., D. Lin-Tan, and J. Lin. 2011 "Food safety involving ingestion of foods and beverages prepared with phthalate-plasticizer-containing clouding agents." J. of Formosan Medical Association. 110:671-684.

(56.) Zapel, C. 2011 "Behind the Science: Is there BPA in my wine?" Wine Spect. URL (accessed 2.14.14).

(57.) Zhou, Y., H. Wang, Y. Chen, and Q. Jiang. 2011 "Environmental and food contamination with plasticisers in China." LANCET 378 (9803):E4-E4.

(58.) Zhu, J. 2012 "Plasticizers found in Chinese wine." China Dly. URL http://www. 1 /20/content_l_5946156.htm (accessed 3.14.14).

(59.) 2012 "China probes liquor containing excessive plasticizer." People's Dly. Online Engl. URL (accessed 2.3.14).

Brent Trela [1] and Cassandra Plank [2]

[1] Alert Aesthetics, [2] Texas Tech University

Table I. Common phthalate esters, bisphenols and organochloride.

class            Compound                 Abbr.   Limits

Phthalate        Dimethyl phthalate       DMP
                 Diethyl phthalate        DEP
                 n-Dibutyl phthalate      DBP
                 Diisobutyl Phthalate     DIBP
                 Butyl cyclohexyl         BcEP
                 Butyl benzyl phthalate   BBP
                 Bis-(2-ethylhexyl)       DEHP    0.006 mg/L
                   phthalate                        (49-51)

Bisphenol        Bisphenol A              BPA     0.05 mg/kg/day
                 Bisphenol S              BPS

Organochloride   Vinyl chloride           VCM     0.002 mg/L

Table II. Potential sources of plastic exposure in
the production of wine.

Activity      Type               Item

Transport     Container          Flexible transport tank
                                 Intermediate bulk containers
                                 (IBCs), drums, totes and bins

Equipment     Crush              Press bladder membrane
                                 Conveyor belts

              Pumps + hoses      Seals, impellers,
                                 bearings, lines, hoses

              Tanks,             Poly tanks
              containers,        Fiberglass tanks
              barrels            Concrete

Ingredients   Fining             Resins

Filtration    Media + housings   Pads and resins
                                 Reverse osmosis membranes
                                 Ultrafiltration media

Packaging     Bottle stoppers    Synthetic "cork"
                                 Agglomerate corks
                                 Natural cork coatings
                                 Screwcap liners

              Containers         Bag-in-box
                                 PET bottles
                                 Aluminum can lining

Activity      Type               Material

Transport     Container          Polyethylene, polypropylene,
                                 polyester, PVC
                                 Polyethylene, HDEP,

Equipment     Crush              PVC, Rubber, silicone (carcass
                                 polyester, nylon, cotton)

              Pumps + hoses      Polyethylene, polyacetal, PVC

              Tanks,             Polyethylene
              containers,        Fiberglass-epoxy/PVC
              barrels            May be lined with epoxy, (56)
                                 which may contain PVC (3740-44)

Ingredients   Fining             ?

Filtration    Media + housings   ?
                                 Polypropylene, nylon,
                                 polyethersulfone, silicone
                                 elastomer (8'54)
Packaging     Bottle stoppers    #4 low density polyethylene
                                 or #7 mixed plastics
                                 Paraffin, waxes, silicon,
                                 other polymer coatings (1)
                                 #4 LDPE, PVC, PVDC

              Containers         Polyethylene, #7 mixed
                                 plastics/ polycarbonate
                                 Thermoplastic polymer resin
                                 of the polyester family
                                 Epoxy/PVC, #7 mixed
                                 plastics (37)/ polycarbonate
                                 plastic (17)

Activity      Type               Potential Plasticizer

Transport     Container          DBP, DEP, DEHP, DMP (4)
                                 DBP, DEP, DEHP, DMP (4)

Equipment     Crush

              Pumps + hoses      DBP, DEP, DEHP, DMP (4), BPA

              Tanks,             DEHA, DBP, DEHP21
              containers,        BPA

Ingredients   Fining             ?

Filtration    Media + housings   ?
                                 ATBC, ATEC, BPBG, Butyl
                                 Stearate, p-tert -Butyl
                                 phenyl salicylate, DBS,
                                 DEP, Diisobutyl Phthalate

Packaging     Bottle stoppers    DBP, DEP, DEHP, DMP (4),
                                 DEHA (21), DBP/DnBP, DIDP,
                                 DEHP (41)
                                 DBP, DEP, DEHA; DEHP,
                                 DMP (4-1-28)

              Containers         DBP, DEP, DEHP, DMP (4),
                                 BPA (37)
                                 DBP, DEP, DEHP, DMP (4)


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Comment:Plastic polymers in the wine industry.(HACCP CONSIDERATIONS)
Author:Trela, Brent; Plank, Cassandra
Publication:Wines & Vines
Date:May 1, 2015
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