Solvent evaporation from DCAC graffiti remover formulations is governed by the coupled mass and heat transfer across the liquid–vapour interface rather than by boiling point alone. In a typical DCAC blend containing 45 wt% dichloromethane, 35 wt% acetone, and 20 wt% propylene carbonate, the headspace vapour at 23°C is enriched in dichloromethane because its vapour pressure of 47 kPa exceeds that of acetone at 24 kPa and propylene carbonate below <0.01 kPa. Under ASTM D3539-11, the thin-film evaporometer normalizes air velocity at 0.15 m/s, temperature at 25°C, and relative humidity at 50%; dichloromethane exhibits a relative evaporation rate of approximately 14.5, acetone approximately 5.6, and n-butyl acetate the reference value of 1.0. The evaporation flux J from a 250 µm wet film on a non-porous substrate can be expressed as J = k_c(C_s − C_∞), where k_c is the gas-side mass transfer coefficient, C_s is the saturation vapour concentration at the liquid-surface temperature, and C_∞ is the bulk vapour concentration. Because dichloromethane has a heat of vaporization near 337 kJ/kg and acetone near 539 kJ/kg, rapid mass loss extracts latent heat from the liquid layer and the substrate, commonly lowering the interface temperature by 6°C to 12°C within 8 min at 0.5 m/s crossflow. This evaporative cooling reduces the saturation vapour pressure of the remaining dichloromethane and slows the mass transfer rate even as the bulk air temperature remains constant. The consequence for graffiti removal is that the effective dwell time required to swell a crosslinked acrylic polyurethane aerosol paint increases from 6 min to 18 min when the same DCAC is applied as a 250 µm film instead of a saturated rag poultice. The addition of a high-boiling co-solvent such as propylene carbonate at 20 wt% does not alter the initial dichloromethane flux; it creates a solvent-retentive liquid matrix that suppresses the later-stage dry-out transition from an evaporating film to a solvent-starved gel. Viscosity data from ASTM D2196-20 on a thickened variant containing 2.5 wt% fumed silica show an initial Brookfield viscosity of 1,200 mPa·s at 10 rpm and 23°C, rising to 4,800 mPa·s after 20% mass loss. This shift is caused by the evaporation of the low-viscosity acetone and dichloromethane, which leaves an enriched silica and polyol ester phase. Formulations thickened with fumed silica are incompatible with strongly alkaline additives such as sodium metasilicate above 0.5 wt% because the pH shift above 9.5 destabilizes the silica network and produces 12% syneresis within 24 h at 23°C. Equipment wetted parts should be 316L stainless steel or PTFE rather than unalloyed aluminium, because dichloromethane can generate hydrogen chloride in the presence of aluminium chloride catalysts formed by surface contamination.
| Component | CAS No. | Boiling point at 101.3 kPa (°C) | Vapour pressure at 20°C (kPa) | Relative evaporation rate (n-butyl acetate = 1.0) under ASTM D3539-11 |
|---|---|---|---|---|
| n-butyl acetate | 123-86-4 | 126 | 1.0 | 1.0 |
| Acetone | 67-64-1 | 56 | 24 | 5.6 |
| Dichloromethane | 75-09-2 | 40 | 47 | 14.5 |
| Propylene carbonate | 108-32-7 | 242 | <0.01 | <0.01 |
Preferential evaporation of acetone from DCAC remover creates a composition drift that is not captured by the initial closed-cup flash point. In a virgin blend containing 35 wt% acetone and 45 wt% dichloromethane, the Tag closed-cup flash point measured under ASTM D56-21a is approximately -9°C. After 10 min of open evaporation with a surface-to-volume ratio of 0.4 cm-1, the liquid-phase acetone concentration falls to approximately 26 wt% while the dichloromethane concentration rises to 51 wt%; the measured flash point rises to +4°C. This effect occurs because acetone is the only component with a normal boiling point below 60°C and a vapour pressure high enough to produce a flammable vapour layer at the Tag cup surface. Dichloromethane does not exhibit a conventional closed-cup flash point under ASTM D56, but its vapour is combustible between 12 vol% and 22 vol% in air and acts as a diluent that can suppress acetone flame propagation at very high concentrations. In a recirculating airless spray system operating at 12 L/min through a 0.013 in. tungsten carbide tip, the return line contains a coarse mesh filter and a 200 µm in-line strainer. Evaporation from the spray fan and tank headspace produces a vapour mixture that, in the confined pump skid, can reach 8 vol% acetone and 6 vol% dichloromethane after 45 min of continuous operation; both values exceed 10% of the lower flammable limit for acetone and require forced ventilation of 0.8 m/s face velocity at the enclosure opening. The liquid composition shift also affects cleaning efficacy: at acetone concentrations below 18 wt%, the paint film lift rate on a methacrylate-based graffiti tag measured by crosshatch tape removal after 15 min dwell drops from 95% removal to 62% removal. This is a process conflict because the formulation contains acetone both as a fast penetrant and as a flash-point modifier; evaporation of the fast penetrant increases flash point safety but reduces the swelling rate of polar polyacrylate binders. Published data for the exact flash point of recirculated DCAC after 20% mass loss are limited, but the directional shift is reproducible in ASTM D3278-20 small-scale closed-cup testing when the evaporated blend is re-sealed and tested within 10 min.
Graffiti on porous masonry shifts the evaporation failure mode from a uniform thin-film loss to a competition between capillary imbibition and surface evaporation. The Washburn equation x = (r γ cosθ t /2η)1/2 describes penetration depth x as a function of pore radius r, liquid surface tension γ, contact angle θ, time t, and dynamic viscosity η. For a DCAC blend with a liquid surface tension of 26 mN/m and a viscosity of 1.1 mPa·s, the capillary penetration depth into a 0.3 µm median pore radius concrete after 60 s is approximately 13 mm. Simultaneously, the surface film loses mass by evaporation at a rate equivalent to a 0.05 mm/min thickness reduction under ASTM D3539-11 conditions. This means that solvent that enters the pore network is partially protected from air movement and surface convection, but the solvent that remains at the tie-coat interface is rapidly depleted. A residue crust of re-deposited paint binder and silica thickener forms when the surface evaporation loss exceeds 25 wt% of the applied film mass; the crust has a measured surface hardness of 2H pencil hardness under ASTM D3363-22 and reduces further solvent ingress into the graffiti layer. In practice, contractors compensate by applying a saturated cotton poultice with a film thickness of 1.0 mm to 1.5 mm and covering it with low-density polyethylene sheet to reduce the gas-phase mass transfer coefficient. The poultice changes the evaporation rate from 0.05 mm/min to approximately 0.008 mm/min because the polyethylene sheet imposes an additional diffusive resistance equivalent to a mass transfer coefficient of 0.002 m/s instead of the open-air coefficient of 0.012 m/s. Published data for solvent penetration into graffiti binders on specific porous substrates are limited, but the dominance of capillary flow in medium-porosity masonry is well established in liquid transport literature.
On south-facing rendered concrete, a DCAC remover applied during late autumn may enter a narrow process window where evaporative cooling suppresses paint swelling kinetics. The swelling of a two-pack polyurethane graffiti finish in dichloromethane follows an Arrhenius-like rate with an apparent activation energy of 35 kJ/mol; a drop in interface temperature from 18°C to 4°C therefore reduces the swelling rate constant by approximately 60%. The evaporative cooling effect is strongest during the first 5 min of application, when the dichloromethane flux is highest. Infrared thermography of a 300 µm wet film on rendered concrete at 15°C and 40% relative humidity recorded an interface temperature of 5°C after 4 min, rising to 10°C only after the majority of the acetone and dichloromethane had evaporated. The low interface temperature also causes atmospheric moisture condensation when the dew point is above 5°C; the resulting micro-emulsion reduces contact angle from 28° to 41° and produces visible whitening of the graffiti surface. Formulators counteract this by adding 10 wt% of a low-vapour-pressure solvent such as dimethyl sulfoxide or propylene carbonate, which lowers the initial dichloromethane partial pressure in the headspace and extends the evaporative cooling plateau. In an immersion-type dwell test on rendered concrete panels, a control DCAC with 35 wt% acetone removed 85% of a two-component acrylic polyurethane graffiti in 20 min at 15°C; the modified formulation with 12 wt% propylene carbonate and 28 wt% acetone removed 90% in the same period. The processing window is nevertheless narrow: adding more than 18 wt% propylene carbonate increases the liquid viscosity to 4,500 mPa·s at 10 rpm and prevents the formulation from wetting the chalky render surface within the 60 s applicator spread time. Production-scale mixing in a 500 L jacketed vessel at 350 rpm with a cowles disperser requires a 10°C cooling jacket temperature during acetone addition to avoid a 9°C exotherm that would alter the headspace composition and reduce the retained acetone content by 2.5 wt%.
Field data from a 30:1 air-assisted airless pump with a 0.013 inch tungsten carbide tip show that atomized DCAC droplets with a Sauter mean diameter of 85 µm develop a surface temperature depression of 6°C before impact at a 25 cm standoff. The d²-law evaporation timescale for a single solvent droplet is t_d = d₀² /K, where d₀ is the initial droplet diameter and K is the evaporation coefficient; for a dichloromethane-rich droplet in air at 20°C and 40% relative humidity, K is approximately 0.4 mm²/s. An 85 µm droplet therefore has an evaporation lifetime of approximately 18 ms, and smaller satellite droplets below 20 µm fully evaporate before reaching the substrate. This droplet-size-dependent evaporative loss shifts the composition of the deposited film away from dichloromethane and acetone and toward propylene carbonate and thickener. When the spray transfer efficiency is measured by collecting the deposited film on PTFE panels and comparing mass to delivered mass, the deposited film shows an acetone content of 22 wt% compared to 35 wt% in the supply tank. The viscosity of the deposited film immediately after spray is 2,100 mPa·s at 10 rpm and 23°C, compared with 1,200 mPa·s for the bulk liquid. This viscosity increase causes poor substrate wetting on vertical steel substrates and produces a pebbled surface after drying, with a measured surface roughness R_a of 18 µm under ISO 4287:1997. To reduce droplet evaporation, operators lower fluid pressure from 80 bar to 55 bar and increase the tip size from 0.013 in. to 0.015 in., which raises the Sauter mean diameter to 110 µm and reduces small droplet mass below 30 µm from 25% to 12% of total volume. The trade-off is a higher applied film thickness of 350 µm instead of 250 µm, which increases dwell time and risk of runoff on vertical surfaces.
Manual brush application to smooth steel surfaces with a laminar 0.3 mm film does not generate measurable preferential evaporation because the surface-to-volume ratio is below 5 m²/kg.
In enclosed lift stations, where a graffiti remover is applied to metal panel interiors with limited air exchange, the evaporation rate of DCAC is controlled less by the solvent's inherent volatility than by the air change rate and the height of the worker's breathing zone. The steady-state vapour concentration C_ss can be approximated as C_ss = k E /Q_v, where k is the mixing factor, E is the emission rate, and Q_v is the volumetric airflow rate. For a 2.0 g/m² application area releasing 0.4 g/min of dichloromethane and 0.2 g/min of acetone, an air change rate of 1.5 h⁻¹ in a 25 m³ lift car produces a time-weighted average dichloromethane concentration of approximately 185 ppm over a 15 min dwell. The OSHA 8-hour permissible exposure limit for dichloromethane is 25 ppm, and the ACGIH threshold limit value is 50 ppm; the short-term exposure limit is 125 ppm for 15 min under 29 CFR 1910.1052. The confined-space vapour gradient is steeper than the open-air gradient because the low airflow suppresses the gas-side mass transfer coefficient; at 0.1 m/s face velocity, k_c falls below 0.002 m/s, compared with 0.005 m/s at 0.5 m/s. Operators applying DCAC in such spaces without forced ventilation exceeding 0.5 m/s face velocity risk exceeding the short-term exposure limit within 12 min of application. The vapor-phase composition also affects paint removal; a high acetone concentration in the lift-station air can recondense on the cold metal surface and dilute the dichloromethane film, reducing its lift activity by 20%. A portable activated-carbon filtration unit with a bed depth of 100 mm and a filter face velocity of 0.25 m/s reduced dichloromethane concentration to 35 ppm in a 15 min trial, but acetone breakthrough occurred at 8 min, indicating that the unit must be selected for the early acetone peak rather than for total solvent mass. Published data for solvent vapour gradients in lift stations are limited, but the mixing factor of 0.3 used in occupational exposure models for small rooms is conservative and supported by field screening with photoionization detectors calibrated against ISO 16017-1:2000.
Batch processing of DCAC graffiti remover in a 1,000 L stainless steel reactor with a vacuum-rated lid creates headspace composition shifts that affect evaporation rate, viscosity, and flash point. When the vessel is charged with 450 kg dichloromethane, 350 kg acetone, and 200 kg propylene carbonate at 20°C, a vacuum of 200 mbar absolute applied during mixing at 250 rpm for 20 min removes 6.0 wt% of the total charge into the solvent recovery condenser. The condensate composition is 80 wt% acetone and 20 wt% dichloromethane because acetone has the higher vapour pressure at the reduced temperature and is selectively stripped. The resulting batch consequently contains 32 wt% acetone rather than the target 35 wt%, and its initial Brookfield viscosity is 1,350 mPa·s instead of 1,200 mPa·s at 10 rpm and 23°C. The evaporated mass also causes a 7°C liquid temperature drop from latent heat removal; if the jacket temperature is set to 25°C, the actual liquid temperature at the end of mixing is 18°C. This temperature depression reduces the vapour pressure of the remaining dichloromethane and slows the subsequent solvent recovery step. To control headspace composition drift, production facilities use a nitrogen blanket at 1.1 bar absolute instead of vacuum and limit mixing speed to 200 rpm; this reduces total volatile loss to 0.8 wt% and keeps batch-to-batch acetone variance below ±0.5 wt% as measured by headspace gas chromatography with flame ionization detection. The headspace gas chromatograph is calibrated according to ASTM E260-96(2019) and uses a 60 m polar capillary column with a 0.32 mm internal diameter and 1.0 µm film thickness. Batch-to-batch variation in acetone content of more than 1.0 wt% produces a measurable shift in the relative evaporation rate under ASTM D3539-11 from 9.8 to 8.9, which alters the dwell time required for complete removal of a nitrocellulose-based aerosol graffiti from 9 min to 13 min. This processing conflict is often unnoticed because the finished product density changes by less than 0.005 g/cm³, and standard quality-control tests for total solids under ASTM D2369-20 do not resolve the acetone-dichloromethane ratio.