| Код ТН ВЭД | |
| Название продукта | Перхлоретилен |
| Химическое название | тетрахлоэтилен |
| Номер регистрации Cas | 127-18-4 |
| Номер ООН | 1897 |
| Молекулярная формула | C2Cl4 |
| молекулярный вес | 165,83 г/моль |
| Физическое состояние | Жидкий |
| внешность | Бесцветный |
| запах | Эфироподобный |
| точка кипения | 121,1 ° C |
| точка плавления | -22,3 ° С |
| плотность | 1,622 г/см3 при 20 °C |
| давление паров | 18,5 mmHg при 25 °C |
| плотность пара | 5,83 (воздух = 1) |
| Растворимость в воде | 0,15 г /л при 20 ° C |
| ЛогП | 3,40 |
| показатель преломления | 1,505 при 20 ° C |
| вязкость | 0,89 кП при 20 °C |
| точка вспышки | Нет (непрозоряемый) |
| Температура самозажигания | 500 ° С |
| удельный вес | 1,62 при 20 ° C |
| Константная закона Генри | 0,0175 атм*м3/моль |
Как аккредитованный завод по производству перхлоретилена, мы соблюдаем строгие протоколы качества - каждая партия подвергается строгим испытаниям для обеспечения последовательных стандартов эффективности и безопасности.
| Упаковка | Перхлоретилен упакован в 55-галлонные стальные барабаны, ООН 1897, с опасными этикетками, запечатанными крышками и соответствующей маркировкой DOT. |
| Погрузка контейнера (20-футовый контейнер) | Перхлоретилен (UN1897, класс 6.1), загруженный в контейнер 20' FCL, закрепленные барабаны, маркированные и документированные для опасной морской перевозки. |
| Доставка | Описание перевозки: UN1897, перхлоретилен, 6.1, PG III. Это токсичная, непрозоряемая жидкость, для которой требуются утвержденные ООН герметичные барабаны или цистерны, этикетки/плакаты класса 6.1 и соответствующая транспортная документация. Следовать правилам DOT, IATA и IMDG; часто маркировка морских загрязнителей. Держите подальше от пищи, окислителей и тепла; обеспечить вентиляцию и сдерживание разлива. |
| Хранение | Храните перхлоретилен в плотно закрытых, маркированных контейнерах в прохладном, сухом, хорошо вентилируемом районе, подальше от прямого солнечного света, тепла, искр и пламени. Держите отдельно от сильных окислителей, щелочных и реактивных металлов. Используйте совместимые материалы, обеспечивайте вторичное содержание и наземные контейнеры во время передачи. Обеспечьте адекватную вентиляцию, проверяйте утечки и никогда не храните их рядом с пищей или питьевой водой. |
| Срок годности | Перхлоретилен стабильен при рекомендованном хранении; защищать от света, тепла, влаги и металлов. Срок хранения, как правило, около двух лет, когда правильно запечатаны. |
In third-generation dry-to-dry perc machines, solvent-to-garment ratio is managed as a dynamic parameter because fabric retention, lint filter absorption, and distillation losses shift during the cycle. The circulating working-solvent volume is recharged from the clean solvent tank to maintain a solvent-to-load ratio between 4 L/kg and 8 L/kg for standard woven garments, with the lower end applied to heavyweight cotton and the upper end to structured polyester blends. Detergent injection is set at 0.5–1.5 vol% of the working-solvent charge for anionic or nonionic detergents formulated with 5–15 wt% water to create a reversed micelle system; moisture is metered separately through a spray bar at 0.25–1.0 vol% based on fibre hydrophilicity. The wash cycle is typically 60–95 seconds for classifications 1–3, followed by extraction at drum speeds of 350–800 rpm to reduce residual solvent before drying at cage outlet temperatures of 60–70 °C. The closed-loop machine uses a plate-and-shell condenser and carbon adsorber in series; the adsorber is regenerated by hot air or steam at 110–120 °C, and recovered solvent is returned to the clean tank after water separation. In the United States, dry-cleaning facilities operating perchloroethylene equipment are regulated under 40 CFR Part 63 Subpart M; third-generation machines are required to meet closed-loop design, refrigerated condenser, and carbon adsorber emission controls. Equipment installation, solvent storage, and ventilation arrangement follow NFPA 32. Finished garment residual solvent is controlled by sensor-driven drying endpoints, and loads containing polyurethane-coated fabrics, PVC trim, or polyvinyl butyral buttons must be excluded because perc causes irreversible swelling and delamination.
A top-loading vapour degreaser processing aluminium die castings and copper tube assemblies uses perchloroethylene meeting ASTM D4376-15 vapour-degreasing grade, with a boiling point of 121.1 °C at standard atmospheric pressure, liquid density of 1.62 g/cm³ at 20 °C, and vapour density approximately 5.8 times that of air. The cleaning sequence is staged: hot vapour immersion, ultrasonic immersion in a side sump, and cross-condensation rinse. The ultrasonic sump is operated at 40 kHz with a power density of 20–35 W/L; the vapour zone is superheated until the condensation line travels 2–5 cm above the top of the work load, and freeboard ratio is maintained above 75% of the open-top tank height to reduce air intrusion and solvent loss. The stabilizer system is consumed by acid formation from water contamination and aluminium chloride complexes, so the sump is continuously decanted and the water content held below 50 ppm as measured by Karl Fischer titration (ASTM E203). Acid acceptance is monitored by ASTM D2942 and is maintained above 0.10 wt% NaOH equivalent; below this threshold, acidic attack on aluminium creates metal fines that accelerate stabilizer depletion and form sludge. Make-up solvent is automatically metered at 0.5–1.5 L per 100 kg of metal cleaned, with the exact rate set by sump level and distillation recovery. Terminal components proceed to plasma vapor deposition, precision welding, or anodizing without aqueous intermediate washing when residual surface contamination is required below 10 mg/m² as determined by solvent extract gravimetry.
On production lines running mixed aluminium and brass loads, the acid acceptance decline is faster than on ferrous-only loads because copper and aluminium form a galvanic couple in the presence of water, accelerating chloride ion release. In such lines, the solvent charge is typically dropped to a still after every 8–10 °C boiling point rise, and non-volatile residue is kept below 10 mg/100 mL as specified by ASTM D2109. Air handling around the degreaser must maintain a capture velocity of 0.4–0.5 m/s across the loading opening to meet occupational exposure limits; the lower explosion limit is absent, but thermal decomposition above 165 °C in hot spots produces phosgene and hydrogen chloride. The operational boundary for this grade is therefore set by simultaneous control of freeboard stability, sump dryness, and acid acceptance; any single variable moving outside its band produces rapid sludge accumulation and solvent breakdown.
| Operating control | Measurement method | Operating band | Corrective action |
|---|---|---|---|
| Freeboard ratio | Laser level or dipstick | 75–90% | Reset hoist travel or lower cooling coil temperature to 15–20 °C |
| Water content | ASTM E203 Karl Fischer | <50 ppm | Replace decanter pad; inspect tank liner |
| Acid acceptance | ASTM D2942 | >0.10 wt% NaOH eq. | Drain side sump; add fresh stabilizer charge |
| Boiling point rise | Digital ebulliometer | 121.1–122.5 °C | Distil and recover solvent; remove accumulated oil fractions |
The catalytic hydrofluorination of perchloroethylene to HFC-125 proceeds over a chromium oxyfluoride catalyst supported on fluorinated alumina. The stoichiometric hydrogen fluoride demand is 5 mol HF per 1 mol C2Cl4, producing 4 mol HCl as by-product. Industrial reactors are run with an HF-to-perchloroethylene molar feed ratio between 6:1 and 10:1, with the excess HF recovered by distillation and recycled to the vaporizer. The reaction is carried out in Inconel 600 or Hastelloy C-276 tube bundles at 320–400 °C and pressures of 0.5–1.5 MPa, with gas-phase contact time maintained between 5 s and 15 s. Lower HF ratios increase the formation of partially fluorinated intermediates and tars that blind the catalyst surface; higher ratios raise selectivity toward HFC-125 but increase acid recovery load. Feed-grade perchloroethylene for this route is specified with water below 10 ppm (ASTM E203), acidity below 5 ppm as HCl, and total organic chlorides below 0.1 wt%; water ingress above the limit converts HF into aqueous acid, strips the protective metal fluoride layer from reactor internals, and generates chromium fluoride fines that plug the catalyst bed. The crude reactor effluent is quenched with chilled 20 wt% hydrochloric acid, then compressed and passed through a sequence of hydrogen chloride absorber, caustic scrubber, drying columns, and two-stage fractional distillation. Unreacted perchloroethylene and intermediate trichloroethylene are recycled to the reactor feed; light ends are purged to thermal oxidizer. The distilled HFC-125 is blended into refrigerant compositions such as R-410A, which contains 50 wt% HFC-125 and 50 wt% HFC-32 and is controlled under AHRI Standard 700 for water, acidity, and high-boiling residue. Published data for specific catalyst formulations and deactivation rates in this perchloroethylene-to-HFC-125 configuration are limited because most patent and licensor data remain restricted; however, the feed-ratio and moisture boundaries are consistent with publicly available fluorination process design literature.
Leather garment processing with perchloroethylene differs from standard textile dry cleaning in that the solvent charge is reduced and the extraction profile is truncated to prevent defatting of hide structure. Suede and sheepskin jackets are processed in dedicated dry-to-dry machines at a solvent-to-load ratio of 2–4 L/kg, which is roughly half the textile dry cleaning ratio; wash time is limited to 30–60 s, and mechanical action is restricted to one-third of textile drum speed. Fatliquor is injected into the solvent at 0.4–1.2 wt% of clean solvent mass to replace natural skin lipids extracted by perchloroethylene; the fatliquor emulsion is prepared with lanolin, phosphate ester, or synthetic sperm oil substitutes and metered by a dosing pump during the final rinse. Drying of leather articles is conducted at a maximum core temperature of 35–40 °C, because higher temperatures denature collagen bundles and cause shrinkage, boardiness, and grain cracking. The process is performed under the same closed-loop emission controls as textile dry cleaning (40 CFR Part 63 Subpart M in the United States; NFPA 32 for facility design), and solvent recovery from the still must be monitored for leather oil accumulation; still bottoms are removed when viscosity exceeds the manufacturer limit. Terminal products are finished leather garments with residual solvent below the sensor-triggered drying endpoint and restored softness. This application is confined to garments with stable dye systems and chrome- or vegetable-tanned leathers; combination garments with polyurethane bonded leather or solvent-soluble adhesives are not processed.
Automatic blanket and roller wash systems in sheetfed offset presses use perchloroethylene-containing wash formulations at 70–90 wt% solvent concentration, with co-solvent dibasic ester or glycol ether at 10–20 wt% and surfactant at 1–5 wt%. The wash is metered at 3–8 mL per cleaning cycle per print unit, applied through a spray bar onto EPDM or polyurethane blanket surfaces, and wiped after 10–30 s dwell with a cloth cassette or brush. The solvent must dissolve UV-cured ink, paper coating binder, and calcium carbonate pigment residues without swelling the rubber blanket; blanket swell is measured by durometer change not to exceed 5 Shore A after 24 h immersion. Compliance is governed by hazardous air pollutant regulations for printing operations in the relevant jurisdiction; solvent-laden cloth cassettes are sealed and handled as hazardous waste under 40 CFR Part 261. The terminal product is a restored blanket and roller surface ready for the next print run. Perchloroethylene must not contact ink metering rollers with polyvinyl chloride covers, because plasticizer migration and softening occur within minutes.
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