
A cascade impactor is an instrument used to sample, fractionate, and collect aerosol particles into discrete size classes based on their aerodynamic diameter. It operates on the principle of inertial impaction through a sequential series of stages. As an air or gas stream is drawn through progressively narrower nozzles, particle velocity increases; particles with sufficient inertia deviate from fluid streamlines to strike and deposit onto collection plates, while smaller particles remain suspended in the flow and proceed to downstream stages.
Cascade impactors are standard tools in atmospheric chemistry, occupational hygiene, air pollution monitoring, and pharmaceutical testing, particularly for the determination of aerodynamic particle size distribution (APSD) in orally inhaled drug products such as metered-dose inhalers (MDIs) and dry-powder inhalers (DPIs).
Cascade impactors fractionate particles according to their aerodynamic behavior rather than geometric dimensions. The aerodynamic diameter ($d_{ae}$) is defined as the diameter of a spherical particle of unit density (1 g/cm3) that exhibits the same settling velocity in air as the particle being evaluated.
A constant volumetric flow rate is maintained through the impactor using a downstream vacuum pump. At each stage, the aerosol stream passes through one or more nozzles directed perpendicularly at a flat collection plate. The fluid stream bends abruptly at an angle of 90° to flow around the plate.
Particles possessing high mass or velocity have sufficient inertia to resist the change in streamline direction, causing them to cross streamlines and impact the surface. Smaller or lighter particles remain entrained within the deflected gas stream and travel to the next nozzle stage.
The probability of impaction is characterized non-dimensionally by the Stokes number ($\mathrm{Stk}$): $$\mathrm{Stk} = \frac{\rho_p d_p^2 C_c v}{9 \eta W}$$ where:
Each stage is defined by a cut-off diameter ($d_{50}$), which corresponds to the aerodynamic diameter collected with 50% efficiency. Because nozzle diameters decrease at each successive stage, fluid velocity ($v$) increases, yielding progressively lower $d_{50}$ values.
In standard atmospheric impactors, the lowest achievable cut-off diameter is approximately 0.25 μm to 0.3 μm; reducing nozzle diameters further to achieve higher velocities is restricted by the speed of sound (Mach 1) and excessive compressibility effects.
To size particles in the ultrafine and nanoparticle ranges (<0.1 μm), low-pressure impactors (LPIs) operate their downstream stages at reduced absolute pressure. Decreased pressure elevates the mean free path of gas molecules, drastically increasing the Cunningham slip correction factor ($C_c$) and enabling particle capture down to approximately 10–50 nm without sonic throttling.
The concept of inertial impaction was first explored in the early 20th century for spore and dust sampling. In 1942, British physicist K. R. May built the first functional multi-stage cascade impactor at the Chemical Defence Experimental Station (now Dstl Porton Down) to quantify windborne military and biological aerosols. May published details of the four-stage glass apparatus in 1945; it sampled droplets and dust between 1.5 μm and 50 μm onto microscope slides.
In 1958, Ariel A. Andersen introduced the multi-orifice cascade impactor (the Andersen Cascade Impactor), replacing single slits with multi-hole plates to avoid sample overloading and increase collection area. In the late 1990s, a consortium of pharmaceutical manufacturers developed the Next Generation Impactor (NGI) to streamline regulatory testing of inhalers, introducing horizontal planar configurations with automated washing cups.
Under standards specified by the United States Pharmacopeia (USP <601>) and European Pharmacopoeia (Ph. Eur. 2.9.18), cascade impaction is the compulsory reference method for determining the aerodynamic quality of inhalation formulations. Crucial derived metrics include:
Cascade impactors fractionate particulate matter in atmospheric monitoring into health-relevant fractions:
Samples are deposited on filters (e.g., quartz fiber or polytetrafluoroethylene) and assayed gravimetrically, by atomic absorption spectroscopy, or by gas chromatography–mass spectrometry (GC-MS) to quantify chemical species, heavy metals, or polycyclic aromatic hydrocarbons (PAHs).