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Home / Blog / Absorption Tower Technology: Two-Film Theory, Fluid Dynamics, Pressure Drop, PFD and Stripping

Absorption Tower Technology: Two-Film Theory, Fluid Dynamics, Pressure Drop, PFD and Stripping

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Author:
Nikulin V, Head of Engineering
Michael-Klepik
An absorber looks simple from the outside: a tower, a fan, a pump, and a stream of dirty air entering at the bottom. What decides whether the outlet meets the permit is invisible — molecular transport across a phase boundary and the hydraulics that keep that boundary large and fresh. This article covers the engineering logic behind absorption tower technology: how a pollutant crosses into the solvent, where the stable operating window lies, what the ΔP gauge is telling you, and how the column fits into a complete flowsheet. Basic definitions and equipment types are covered in our overview article, and the full sizing procedure in the calculation guide.

How a Pollutant Crosses the Phase Boundary

Most design methods in gas scrubbing trace back to the two film theory of a gas absorption tower, proposed by Whitman in 1923. The model assumes both phases are well mixed except for two thin stagnant layers on either side of the boundary, with all resistance to transport concentrated inside those layers. At the boundary itself the phases are taken to be in equilibrium, usually described by Henry's law. The absorption tower interface concentration therefore cannot be read from any instrument; it is reconstructed from the ratio of the film coefficients, and the driving force in each film is the distance between the bulk value and that equilibrium point.

The practical payoff is the idea of a controlling film. Mass transfer in a gas absorption tower is gas-film limited when the pollutant dissolves readily or reacts instantly with the solvent — HCl or NH₃ captured by water, SO₂ by caustic. For sparingly soluble species such as NO or CO₂ in plain water, the liquid side controls. The distinction changes hardware decisions: a gas-film-limited duty rewards developed contact surface, while a liquid-limited one rewards intense surface renewal or a reagent that consumes the dissolved molecule and holds its concentration in the solvent near zero. That is why NOx systems run on NaOH or H₂O₂ solutions instead of plain water.
Counter-current flow inside a fixed random packing scrubber: solvent trickles down over the rings, gas rises through the irrigated layer.
Counter-current flow inside a fixed random packing scrubber: solvent trickles down over the rings, gas rises through the irrigated layer.

Column Hydraulics

Counterflow is the default arrangement because it preserves a driving force along the entire height: the cleanest air meets the freshest solvent at the top, the richest stream meets the most loaded liquid at the bottom. Absorption tower fluid dynamics then determine how hard that arrangement can be pushed. At low loads the solvent runs as a thin film over the media while air passes freely. Raise the velocity and the column enters the loading regime — liquid holdup grows, films thicken, and interfacial area actually improves. Push further and drainage fails: liquid accumulates, slugs form, droplets leave with the outlet stream. This is flooding, and it sets the ceiling.

Design practice places the operating point at roughly 60–75% of the flooding velocity — close enough to benefit from the turbulence of the loading regime, far enough to survive surges in flow or temperature. Internals shift where that ceiling sits. In the Torch-Air line, the TORNADO SP with structured media offers the lowest hydraulic resistance and the most compact tower, while the TORNADO RP filled with random rings (Raschig, Pall, Intalox) reaches the same efficiency in a taller, cheaper body. Co-current and cross-flow layouts trade part of the driving force for lower resistance and height; the horizontal BOREAS series uses the cross-flow scheme where headroom on site is limited.
Expert commentary by Michael Klepik, Torch-Air CEO: operation, efficiency, and maintenance of ring-type scrubbers.

Estimating and Reading Pressure Drop

Engineers regularly ask how to estimate pressure drop in absorption tower systems before any detailed sizing exists. A workable first pass: according to U.S. EPA air pollution control technology fact sheets, an irrigated fixed layer typically loses 0.5–1.0 in. w.c. per foot of depth, and every tray stage adds its own fixed increment on top of that. Multiply by the required height, add the mist eliminator and ductwork, and you have a preliminary fan specification.

In operation the same number turns into a diagnostic. Plotted against air velocity, ΔP first rises along a straight line, then breaks upward at the loading point, then goes nearly vertical at flooding — the ceiling from the previous section, visible on a gauge. Trended over weeks, the curve tells a story: slow creep upward means scale, salt crystallization, or dust blinding the internals; a sudden fall means channeling or a failed irrigation nozzle; oscillation means the unit is hunting near the flooding line. ACGIH industrial ventilation practice recommends selecting the fan with reserve precisely because fouling raises resistance long before removal efficiency visibly drops. Irrigation rate deserves the same attention as velocity: raising it improves contact up to a point, beyond which it mostly adds holdup, resistance, and pump power.

The Absorber in the Flowsheet

A process flow diagram of an absorption tower rarely shows the column alone. The usual loop: a blower, sometimes a quench to knock the temperature down, the column with a mist eliminator on top, a recirculation tank below, a pump, pH instrumentation dosing fresh reagent, and a blowdown line removing accumulated salts. When the reagent is cheap alkali and the product is a neutral salt, the loop ends there — the Silicon Valley system described below runs exactly this way.

When the solvent is expensive or the captured compound has value, regeneration closes the circuit, and gas cleaning becomes a process consisting of an absorption tower and a stripping tower. The absorber shifts the pollutant into the liquid at low temperature; the stripper reverses the equilibrium with heat, steam, or vacuum and returns lean solvent to the top of the first column. Amine CO₂ capture and H₂S removal at refineries both run on this pair.

The oldest industrial example is the contact process absorption tower in sulfuric acid production: SO₃ leaving the catalytic converter is taken up by 98–99% acid; contact with water would generate a persistent acid mist that no eliminator could hold. Where regeneration is impractical and flows are small — tank breathing, for instance — a compact tank vent unit or a dry adsorber is often the simpler answer.
Steam Stripping — Using Heat and Steam to Remove Volatile Contaminants

Choosing the Configuration

Selection starts from the stream and follows the logic of the first section. A readily soluble or reactive contaminant makes the duty gas-film limited, which points to fixed media with generous surface — TORNADO SP or RP, 600–30,000 CFM. A poorly soluble one calls for chemistry first: pick a reagent that consumes the dissolved molecule, then size the liquid circuit. Heavy dust load rules out fixed internals — a mobile layer of light spheres inside the TORNADO FB (100–175,000 CFM) or the two-stage Venturi TORNADO-FB keeps working where rings would blind within weeks. Very large flows with modest removal targets favor the foam action of the TYPHOON tray unit; sticky aerosols favor the hollow TORNADO ST. Temperature narrows the field further: polypropylene bodies serve up to 175°F, steel versions of the same models up to 570°F, with PVDF and PTFE linings reserved for aggressive chemistry.

Three mistakes repeat across audits. Sizing the fan for clean-condition resistance, leaving no room for fouling. Installing fixed media on a dusty stream because the quoted efficiency looked better on paper. And chasing maximum ΔP where the pollutant is a soluble vapor — energy spent on shattering droplets adds nothing over a low-resistance column. Torch-Air engineers run the selection against your actual stream data, typically within 1–2 days.
Installation of the TORNADO RP at a customer facility.
Installation of the TORNADO RP at a customer facility.
Essential Data for Selecting a Wet Scrubber or Dust Collector
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We always perform precise calculations and offer expert assistance in selecting the optimal dust collection or gas cleaning systems, typically completing this process within 1 to 2 days
Head of Engineering,
Vladimir Nikulin
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