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Ascent Petrochem Holdings Co., Limited

Green Catalytic Method For Pollution Reduction Retrofitting Bromochloromethane Production Lines

How Does Catalyst Pellet Geometry Influence Pressure Drop Across a Fixed-Bed Halogen-Exchange Reactor?

The retrofitted reactor section replaces the legacy stirred-tank cascade—previously operating with anhydrous aluminium chloride sludge suspended in a dichloromethane‑bromine mixture at 35–42 °C—with a single downflow adiabatic fixed-bed vessel loaded with extruded H‑ZSM‑5 zeolite catalyst (Si/Al ratio 28–32, binder content 20 wt% pseudo‑boehmite, pellet diameter 3.2 mm, length 5–8 mm). The tube-side distributor plate is specified as 6 mm thick Hastelloy C‑276 perforated with 2.0 mm orifices on a triangular pitch of 8.0 mm, yielding an open area ratio of 5.7 %. Under a methylene chloride feed rate of 1200 kg·h⁻¹ conditioned to ≤ 50 ppmw water via an upstream 3 Å molecular sieve dryer, and a bromine flow metered by a magnetically coupled gear pump with tantalum wetted parts to achieve a Br₂/CH₂Cl₂ molar ratio of 1.03:1, the superficial mass velocity at the bed inlet is maintained at 1.8–2.2 kg·m⁻²·s⁻¹. Confining the pressure drop to ≤ 0.30 bar across the catalyst bed is non‑negotiable, because the feed booster compressor’s discharge rating is 3.5 bar(g) and the downstream distillation column requires an overhead pressure of 2.8 bar(a) for effective separation of bromochloromethane from unreacted methylene chloride. Pellet geometry was found to be the dominant variable: initial trials with 1.6 mm trilobe extrudates caused a pressure drop of 0.52 bar within 72 hours due to inter‑pellet void collapse from thermal cycling between 120 °C (reaction exotherm) and 60 °C during intermittent idling, whereas the larger cylindrical pellets show a stable ΔP of 0.27–0.29 bar over 2000 hours of operation as measured by differential pressure transmitters tapped to the bed support grid and the top of the inert ceramic ball pre‑heat section. Catalyst mechanical strength, tested per ASTM D7084‑18 (single‑pellet crush strength ≥ 2.5 daN), and attrition resistance (≤ 0.3 wt% fines generated after 30 min in a rotating drum per ASTM D4058‑15) were adopted as release criteria after a full‑bed plugging incident traced to 18 kg of catalyst dust accumulating on the outlet collection screen, which elevated the pressure differential sufficiently to trip the reactor high‑pressure interlock (3.8 bar) and initiate an emergency bromine containment sequence. The adiabatic temperature rise—calculated from the exothermic halogen‑exchange heat of reaction of approximately −28 kJ·mol⁻¹—is constrained to a maximum outlet of 210 °C to avoid hydrothermal dealumination of the zeolite framework; to maintain this, a quench box injecting recycled cold bromochloromethane (15 °C, 150 kg·h⁻¹) is positioned at the bed mid‑point, with the injection nozzle fabricated from PTFE‑lined carbon steel to withstand the corrosive mixture containing dissolved hydrogen bromide at 0.8 wt%. Process gas chromatography (online micro‑GC with a Molsieve 5 Å and a PoraPLOT Q column, sampling every 4 minutes) tracks the dibromomethane by‑product concentration, which must remain below 0.15 mol% to meet the 99.5 wt% bromochloromethane purity required for subsequent pharma‑grade propellant applications. Published data for this specific zeolite‑catalysed halogen exchange at >2 tpd scale are limited, but pilot‑plant runs conducted in a DN100 reactor tube at WHSV = 0.8 h⁻¹ confirm that selectivity to bromochloromethane exceeds 94 % over the first 600 hours, declining to 87 % by 1200 hours due to coking, at which point an oxidative regeneration cycle—ramping from 200 °C to 450 °C at 2 °C·min⁻¹ in a flow of 2 vol% oxygen in nitrogen, certified to ≤ 5 ppmv halogens—restores initial selectivity within ± 1.5 %. The legacy halocarbon purification train, consisting of three packed distillation columns originally designed for an effluent containing 3–5 wt% dissolved aluminium chloride complexes, required substantial re‑engineering when the homogeneous catalyst was eliminated. Without the Lewis acid dissolved in the crude product, the corrosive load on the reboiler shifted from a mixed acid‑chloride corrosion mechanism to a dew‑point corrosion regime driven purely by wet hydrogen bromide, which concentrates in the first column overhead to 0.7–1.2 bar partial pressure at 112 °C. The original 316L stainless steel tube bundles, which had exhibited a corrosion rate of 0.12 mm·year⁻¹ in the presence of AlCl₃‑derived chloroaluminate ionic species, were replaced with Alloy 625 (UNS N06625) U‑tube bundles conforming to ASME BPVC Section VIII‑1, with a wall thickness of 2.11 mm and a design corrosion allowance of 0.5 mm. The overhead condenser, previously a shell‑and‑tube unit with 304L tubes, was re‑tubed with tantalum‑clad copper (cladding thickness 0.4 mm) to eliminate the risk of chloride stress corrosion cracking observed in the former unit after 14 months of service, manifested as transgranular branching cracks initiating from the tube‑to‑tubesheet weld joints. The dry hydrogen bromide off‑gas stream, now free of entrained aluminium chloride particulates, is routed through a halogen‑resistant back‑pressure regulator set at 3.0 bar(g) and fed directly to a falling‑film absorber where it is re‑dissolved in process water to produce 48 wt% hydrobromic acid, which is subsequently polished through a 0.5 µm PTFE membrane filter and reused in upstream bromine generation cells, eliminating the need for external lime neutralization that previously generated 120 tonnes·year⁻¹ of calcium bromide‑contaminated solid waste classified under EWC code 06 02 04*. The control of trace dibromomethane (CH₂Br₂) in the final bromochloromethane product gains heightened significance when the halon‑replacement material is utilised as a feedstock for synthesising the pharmaceutical intermediate bromochloromethane‑d₂, where deuterium exchange cannot proceed without isotopic scrambling if the CH₂Br₂ level exceeds 0.05 mol%. The retrofitted line therefore incorporates a side‑stream melt crystallisation unit operating at −88 °C, the temperature at which the bromochloromethane‑dibromomethane eutectic exhibits a solid‑phase purity of 99.98 mol% after three fractional crystallisation stages, each employing a scraped‑surface crystalliser with a wall temperature differential of 1.5 °C and a residence time of 45 minutes. Impurity monitoring is conducted via cryogenic gas chromatography using a 60 m × 0.32 mm DB‑624 column, with quantification limits validated according to ISO 17025:2017 at 0.005 mol%. The cold utilities demand—220 kW of refrigeration duty at −95 °C—is met by a cascade system using R‑507 in the high stage and R‑1150 (ethylene) in the low stage, with screw compressors sized for 75 % part‑load operation; any interruption of the refrigerant flow for more than 8 seconds triggers an automatic switchover to a reserve nitrogen‑pressurised storage tank to prevent the crystalliser wall from crossing the −93 °C threshold at which the solid‑phase bromochloromethane undergoes a phase transition producing glassy deposits that foul the scraper blades.

Avoiding Amine‑Based Stabilisers: Catalyst Deactivation and Metal Chelation in Downstream Processing

Pre‑retrofit production protocols tolerated the deliberate addition of 1,2‑butylene oxide and N‑methylmorpholine as acid scavengers to suppress aluminium chloride‑induced side reactions. With the heterogeneous zeolite catalyst bed, any amine‑based stabiliser will preferentially adsorb on the Brønsted acid sites within the 10‑membered ring channels, forming quaternary ammonium adducts that reduce the total acid site density as measured by temperature‑programmed desorption of ammonia (NH₃‑TPD, ASTM D4824‑21) by up to 40 % after a cumulative exposure of 50 g amine per kilogram of catalyst. The deactivation is not fully reversible by oxidative regeneration because the nitrogen‑containing residues form refractory carbonaceous species that require prolonged burn‑off at 550 °C—a temperature exceeding the zeolite’s critical de‑alumination onset of 510 °C for the given Si/Al ratio. Consequently, the formulation of the feed conditioning system has been reconfigured to substitute amine‑based inhibitors with a trialkyl phosphate stabiliser (tributyl phosphate, 0.08–0.12 wt% in the methylene chloride storage tank), which functions as a sacrificial proton acceptor without entering the zeolite micropores, as demonstrated by a ≤ 0.5 % decline in steady‑state conversion over 1000 hours. A further incompatibility arises in the downstream bromine recovery loop: residual ammonia or low‑molecular‑weight amines liberated during the oxidative regeneration vent gas and subsequently captured in the scrubber system can react with dissolved bromine to form explosive nitrogen tribromide precipitates, documented as a sensitivity risk when the local concentration exceeds 3 mg·L⁻¹ in the aqueous phase, requiring continuous spectrophotometric monitoring at 340 nm per a validated in‑house method aligned with US EPA Method 330.5. Where the liquid‑phase halogen‑exchange legacy plant discharged a spent catalyst slurry containing 15–20 wt% aluminium chloride, chlorinated solvent residues, and adsorbed heavy metals (zinc, iron) that required solidification prior to landfilling under EU Landfill Directive 2003/33/EC leachability limits, the solid zeolite catalyst inventory of 890 kg per charge is replaced on a 3‑year cycle, with the spent extrudates classified as non‑hazardous after leachate testing per EN 12457‑3:2002 (L/S = 10 L·kg⁻¹), provided the zinc content—introduced as a binder component—does not exceed the 400 mg·kg⁻¹ limit specified for inert waste disposal. Each batch of spent catalyst is sampled at 12 points across the bed and submitted for analysis of purgeable organic halogens (POX) according to DIN 38414‑S17; values exceeding 50 mg·kg⁻¹ require a supplementary thermal desorption step at 350 °C carried out in an indirectly heated rotary kiln with a nitrogen sweep before the catalyst can be landfilled or sent to a zeolite recycling smelter. --- **Comparative Performance of Catalyst Systems for Bromochloromethane Production at 2.5 tpd Scale**
Parameter Homogeneous AlCl₃ (Pre‑retrofit) Fixed‑Bed H‑ZSM‑5 (Retrofit) Test Method / Standard
Reactor temperature range 35–42 °C (jacketed CSTR) 120–210 °C (adiabatic bed) In‑situ thermocouple array, ±1.5 °C
Pressure 1.2 bar(g) 2.8–3.2 bar(a) EN 837‑1 gauge
Crude bromochloromethane selectivity 88–91 mol% 94–96 mol% GC‑FID, internal standard method
Dibromomethane by‑product 4–7 mol% 1.5–3.0 mol% GC‑MS, ISO 16000‑6:2011
Solid waste generation 145 kg·t⁻¹ product (spent AlCl₃ sludge, EWC 06 03 14) 0.8 kg·t⁻¹ product (spent catalyst, EWC 16 01 22 if screened) Mass balance over 30‑day campaigns
HBr recovery efficiency 72 % (off‑gas neutralisation lime consumption 0.38 t·t⁻¹ BCM) 98 % (closed‑loop absorber, lime demand 0.01 t·t⁻¹ BCM) Titrimetric HBr balance, ISO 21438‑2:2009
Wastewater COD 3200 mg·L⁻¹ 420 mg·L⁻¹ ISO 6060:1989
Catalyst regeneration frequency Continuous (AlCl₃ makeup 22 kg·h⁻¹) Every 1200–1500 hours online Pressure drop criteria
--- The off‑gas treatment system originally consisted of a single‑stage caustic scrubber packed with 25 mm polypropylene Pall rings, sized for a gas flow of 850 Nm³·h⁻¹ and designed to neutralise hydrogen chloride and bromine slip to comply with a stack emission limit of 10 mg·Nm⁻³ for total halogens. Following the catalyst retrofit, the halocarbon‑laden vent from the product distillation column still contained 120–180 mg·Nm⁻³ of methylene chloride and 25–50 mg·Nm⁻³ of bromochloromethane, neither of which is adequately hydrolysed by caustic at ambient temperature. A regenerative thermal oxidiser (RTO) was inserted upstream of the scrubber, equipped with a 3‑bed ceramic media heat exchanger and designed to achieve 99.5 % destruction efficiency at a combustion chamber temperature of 950 °C and a residence time of 1.2 seconds. To prevent the formation of polychlorinated dibenzo‑p‑dioxins and dibenzofurans (PCDD/Fs), the quench section after the thermal oxidiser rapidly cools the flue gas from 950 °C to 180 °C within 0.3 seconds using a venturi quench injecting atomised demineralised water, a configuration validated by stack testing per EN 1948‑1:2006 to demonstrate dioxin emissions ≤ 0.05 ng TEQ·Nm⁻³. The scrubbing medium was switched from 10 wt% sodium hydroxide to a 15 wt% sodium sulfite solution buffered to pH 8.5–9.0 with sodium carbonate, which irreversibly quenches residual bromine as bromide without generating the hypobromite disproportionation products that had previously caused pH excursions and foaming in the scrubber sump. Continuous emission monitoring uses a heated flame ionisation detector calibrated with a propane standard (EN 12619:2013) and a Fourier‑transform infrared analyser for inorganic halogen hydracids, with data logged to a plant‑wide environmental management system certified to ISO 14001:2015 and reported to the competent authority at 30‑minute block averages. Process safety within the retrofitted line is governed by the requirement that no operation be permitted while the reactor skin temperature at the carbon‑steel pressure shell exceeds 80 °C, a limit derived from the corrosion rate doubling for every 10 °C rise in the presence of trace hydrogen bromide leakage, as determined by weight‑loss coupons exposed according to NACE TM0169‑2012. To achieve this, the reactor is clad internally with 3 mm of PTFE bonded to a 2 mm chemically resistant epoxy primer system, with the annulus continuously purged with dry nitrogen at 0.5 bar(g) and monitored for bromide breakthrough by an ion‑selective electrode alarm set at 2 ppmv. The entire bromine‑bearing section—from the feed tank to the reactor inlet—is maintained under a 50 mbar nitrogen blanket with ullage analysis performed every 15 minutes using a process mass spectrometer; any excursion of the bromine vapour concentration into the flammable range of the solvent‑air mixture triggers a controlled water fog deluge and isolation of the feed line via ASME Class VI metal‑seated ball valves with tantalum‑coated internals. The automatic depressurisation system routes reactor contents in a runaway exotherm scenario to a quench vessel containing 2500 litres of 10 °C calcium bromide solution, which instantly halts the halogen‑exchange reaction, a design validated by adiabatic calorimetry testing (ASTM E1981‑22) indicating a maximum self‑heat rate under worst‑case runaway of 12 °C·min⁻¹. Within the catalyst make‑up and handling section, the green retrofit imposes strict pre‑drying requirements for all process auxiliaries. The fresh zeolite extrudates are received in 1000‑kg flexible intermediate bulk containers with an aluminised barrier layer and a desiccant pouch; upon opening, the moisture content must be verified to be ≤ 0.5 wt% by a Karl Fischer oven method (ISO 15512:2019) before loading into the catalyst hopper. Loading is performed under a dry air purge with a dew point of −55 °C using a sock‑type dense loading device to minimise attrition; after loading, the bed undergoes a 24‑hour drying period at 250 °C with a nitrogen flow of 1.0 bed‑volume·min⁻¹ prior to the introduction of halogen‑containing feed. Failure to adhere to the moisture specification has resulted in a processing bottleneck where condensed water reacts with bromine to form a persistent bromic acid fog that corrodes the downstream demister pad and forces an unplanned 18‑hour shutdown for pad replacement, as recorded in the plant’s corrective action log for Q3 2023. When the bromochloromethane‑rich distillate is destined for high‑purity fire‑suppressant blending under ISO 14520‑5:2019 (gaseous fire‑extinguishing systems), the permissible non‑volatile residue is capped at 10 mg·L⁻¹, a parameter that cannot be reliably met by simple distillation alone due to the carryover of sub‑micron catalyst fines generated during bed settling. The solution incorporated into the retrofit is a two‑stage filtration unit consisting of a back‑flushable 10 µm sintered Alloy 625 filter element followed by a 0.45 µm hydrophobic PTFE membrane housed in a 316L sanitary housing; the differential pressure across the membrane is limited to 0.7 bar to prevent rupture, and the filter assembly is steam‑sterilisable per ASME BPE 2022 guidelines for pharmaceutical‑grade halocarbons. Particle counts measured by a liquid‑borne optical particle counter (ISO 21501‑2:2019) are documented in the batch record as part of the release criteria for FDA 21 CFR 211.165 compliance when the material is shipped to a drug master file holder. --- **Emissions and Compliance Cross‑Reference Matrix for Retrofitted BCM Production**
Environmental Aspect Limiting Regulation / Permit Condition Measurement Method / Standard Retrofit Compliance Basis
VOC emission to air (stack) IED 2010/75/EU Annex VII Part 2: 20 mg·C·Nm⁻³ for halogenated VOC >100 g·h⁻¹ EN 12619:2013 (FID) RTO + wet scrubber, verified 12 mg·C·Nm⁻³
Dioxin/furan emission IED 2010/75/EU Annex VI: 0.1 ng TEQ·Nm⁻³ EN 1948‑1:2006 Rapid quench design, demonstrated 0.04 ng TEQ·Nm⁻³
Bromine and HBr in scrubber effluent Site‑specific discharge permit: pH 6‑9, bromate <0.5 mg·L⁻¹ ISO 15061:2001 (ion chromatography) Sulfite scrubber, pH control, bromate <0.2 mg·L⁻¹
Spent catalyst classification EU Waste Framework Directive 2008/98/EC, Decision 2000/532/EC EN 12457‑3:2002 (leaching) Tested non‑hazardous (Zn <400 mg·kg⁻¹)
Product purity for fire suppression ISO 14520‑5:2019 Table 1: Bromochloromethane >99.0 mol%, non‑volatile residue <10 mg·L⁻¹ ISO 14520‑5:2019 Annex A analysis Filtration + crystallisation, average 99.6 mol%
Worker exposure to methylene chloride EU Directive 2019/130 (carcinogen), 8‑h TWA 50 mg·m⁻³ EN 689:2018+AC:2019, personal sampling Closed sampling, local exhaust ventilation, 12 mg·m⁻³
--- The bromine recovery column reboiler, a vertical thermosiphon unit with 52 m² heat transfer area, was identified as the primary site of cumulative fouling after the catalyst change. Under the homogeneous process, the aluminium chloride carried into the column formed a viscous, pumpable heel that could be continuously withdrawn from the sump. With the heterogeneous catalyst, the crude feed to the column contains no such liquid‑phase metal halides, but instead carries 5–25 ppmw of ultrafine zeolite particles (median particle size 1.2 µm by laser diffraction, ISO 13320:2020) that originate from attrition during bed expansion. These sub‑micron particles settle on the reboiler tube surfaces and, in the presence of dissolved hydrogen bromide, form a tenacious agglomerate layer of silica‑rich scale that reduces the overall heat transfer coefficient from an initial 850 W·m⁻²·K⁻¹ to 490 W·m⁻²·K⁻¹ within 21 days, forcing a chemical cleaning cycle with 5 wt% ammonium bifluoride solution heated to 60 °C. To extend the run length, a cross‑flow microfiltration loop was inserted on the reboiler feed line, employing a 0.2 µm ceramic membrane (α‑alumina, 19‑channel, length 1200 mm) operated at a transmembrane pressure of 0.6 bar and a cross‑flow velocity of 4.5 m·s⁻¹. The permeate, containing ≤ 0.5 ppmw suspended solids, is routed to the reboiler, while the retentate is returned upstream of the quench box, creating a closed‑loop solids‑management system that has extended the reboiler cleaning interval to beyond 180 days. Operating the process at production scale revealed a narrow thermal processing window for the zeolite catalyst during the initial startup sequence. If the temperature ramp rate from ambient to the minimum light‑off temperature of 110 °C exceeds 8 °C·h⁻¹, differential expansion between the zeolite crystallites and the alumina binder induces micro‑cracking within the extrudates, leading to a measurable increase in the pressure‑drop accumulation rate by a factor of 2.3 over the first 200 hours. Consequently, the automated startup logic has been programmed to override manual heating controls and enforce a positive temperature soak at 60 °C, 80 °C, and 100 °C for 90 minutes each, monitored by 24 bed‑mounted thermocouples. Only when the radial temperature spread across the bed cross‑section is ≤ 4 °C does the control system allow bromine injection to begin at a minimal flow of 15 kg·h⁻¹, ramping to full load over 6 hours. Retrofitting the drum handling area for the bromine supply introduced a dedicated enclosed ventilated cabinet with a −50 Pa negative pressure relative to the process hall, equipped with chlorine‑rated ductwork and a 99.97 % HEPA filter before discharge through a 15‑metre stack. The cabinet is purged with air dried by a twin‑tower desiccant dryer to a dew point of −70 °C, as moisture ingress into the bromine headspace accelerates the formation of a corrosive bromine‑water azeotrope that attacks the mild‑steel drum shells and has, in a legacy incident, generated a pinhole leak releasing bromine vapour into the loading bay. The humid air exclusion is verified by a dew‑point transmitter that initiates an automatic line‑isolation valve closure if the dew point rises above −60 °C. Deep within the solvent recovery loop, the retrofitted line’s dependence on anhydrous conditions made it necessary to abandon the former practice of using live steam injection for cleaning column trays, as residual moisture would later contaminate the recycled methylene chloride stream and reduce the catalyst’s halogen‑exchange activity. Instead, a solvent‑based wash using 99.9 % dichloromethane purified over a molecular sieve bed is circulated at 40 °C for 4 hours, followed by nitrogen drying until the dew point reaches −50 °C. The effectiveness of the cleaning is verified by extracting a solvent sample and analysing it for chloride and bromide ions via ion chromatography (ISO 10304‑1:2007); results exceeding 1 mg·L⁻¹ trigger a repeat wash cycle. The instrument air supply to all pneumatic actuated valves in the bromine and hydrogen bromide service was converted to a “clean dry air” specification with a particulate filter to 0.01 µm and a maximum oil content of 0.003 mg·m⁻³, because the presence of compressor lubricant aerosols in the legacy system was found to react with bromine vapour, producing brominated organic acids that deposited on valve seat O‑rings and caused stick‑slip behaviour leading to inaccurate position feedback and a loss of SIL‑2 certified loop integrity. The air is now supplied by a separate oil‑free rotary screw compressor package rated per ISO 8573‑1:2010 Class 1 for particles and oil. Where the converted facility retains its historical brine cooling loop for the crystalliser jacket, the brine composition—originally a 30 wt% calcium chloride solution inhibited with 0.5 wt% sodium dichromate—was changed to a monopropylene glycol‑based coolant at 55 vol% concentration with a corrosion inhibitor package compatible with the C‑276 plate heat exchanger gaskets, tested per ASTM D1384‑05 to maintain a corrosion rate on copper and steel below 2 mils per year. The change was driven by the discovery that any leakage of chromate‑inhibited brine into the product through a micro‑crack in the crystalliser wall would contaminate the bromochloromethane with hexavalent chromium, a substance restricted under EU REACH Annex XVII entry 47, rendering the batch non‑compliant for electronic cleaning‑agent applications even at 0.1 ppm levels. The control system interlocks associated with the bromine dry‑scrubber bypass valve were redesigned to respond to a heat‑release rate signal from the oxidiser combustion chamber; should the measured rate‑of‑rise exceed 15 °C·s⁻¹, indicative of a halogen‑initiated bed media reaction, the bypass diverts the vent to an emergency carbonate‑filled emergency scrubber within 1.5 seconds, a response time validated by a full‑scale functional safety audit compliant with IEC 61511‑1:2016 and documented in the plant’s safety requirement specification.