Aerosol Science and Technology 37: 510–527 (2003) c 2003 American Association for Aerosol Research ° Published by Taylor and Francis 0278-6826/03/$12.00 + .00 DOI: 10.1080/02786820390126376 Application of Cloud Dynamics to Dosimetry of Cigarette Smoke Particles in the Lungs David M. Broday1 and Risa Robinson2 1 2 Faculty of Agricultural Engineering, Technion, Israel Institute of Technology, Haifa, Israel Department of Mechanical Engineering, Rochester Institute of Technology, Rochester, New York, USA Clinical data suggest a relationship between in vivo deposition patterns of cigarette smoke particles and the occurrence of tumors in the lung. Traditional dosimetry models fail to predict the preferential proximal deposition of cigarette smoke in the human airways, which resembles deposition of aerosol with a larger mass median aerodynamic diameter (MMAD) than that representative of cigarette smoke. Previous work has shown that accounting for the so-called cloud effect leads to enhanced proximal deposition and to better agreement with clinical and experimental data. This work presents an improved model of transport and deposition of cigarette smoke in the airways of smokers, accounting for possible particle-particle interactions (cloud effect) and their effect on the mobility of individual particles and on the deposition profile. Brinkman’s effective medium approach is used for modeling the flow through and around the cloud, with the cloud’s permeability changing according to the cloud’s solid volume fraction. Although the weakest of all interparticle hydrodynamic interactions is considered, it significantly alters the deposition pattern along the respiratory tract, both alone and simultaneously with other synergistic processes (coagulation, hygroscopic growth) that dynamically modify the particle size distribution. Model results compare favorably with clinical data available on CSP deposition in the lungs and indicate that a combination of cloud behavior, hygroscopic growth, and coagulation may explain the preferential proximal deposition of smoke particles in the tracheobronchial region. INTRODUCTION Tobacco smoke has long been recognized as a major cause of death and disease, responsible for an estimated 434,000 deaths per year in the US (EPA 1993). It is known as a Group A carcinogen in humans, and is associated with a major risk factor for Received 26 March 2001; accepted 8 January 2003. This research was supported in part by the fund for the promotion of research at the Technion and by Philip Morris Incorporated. Address correspondence to David M. Broday, Faculty of Agricultural Engineering, Technion, Israel Institute of Technology, Haifa, 32000, Israel. E-mail: [email protected] 510 heart disease; eye, nose, and throat irritation; and various respiratory chronic disease and pulmonary disorders. In particular, tobacco smoke is known to cause lung cancer (Hoffmann and Hoffmann 1995) and to increase the severity and frequency of asthma episodes in children exposed to environmental tobacco smoke. Health symptoms associated with tobacco smoke occur because of active smoking and as a result of secondary exposure, usually termed secondhand smoking (SHS) or exposure to environmental tobacco smoke (ETS). The latter exposure route involves contact with a mixture of smoke given off by the burning end of a cigarette and smoke exhaled by smokers. Cancer etiology relating to inhaled cigarette smoke requires understanding of the motion and deposition patterns of cigarette smoke particles (CSP) in the human respiratory tract, as well as its postdeposition fate. Exposure to cigarette smoke is known to decrease the ability of the lungs to clear inhaled matter (Churg et al. 1992, 1998; Keeling et al. 1993; Finch et al. 1998). Although chronic CSP clearance failure may be an important cause of tumor initiation, leading to induction of lung cancer, this work does not address this issue. Previous mechanistic deposition models were generally unable to accurately predict the deposition of CSP in the human respiratory tract. In this work we present a new description of the dynamics of cigarette smoke in the airways of smokers, implemented within an improved deposition model. Predictions of the model agree favorably with clinical and measured CSP deposition data. Clinical Studies Clinical studies (see reviews by Ellett and Nelson 1985; Martonen et al. 1987; Yang et al. 1989) established that bronchogenic carcinomas are preferentially spread in proximal airways in the lungs of smokers, whereas adenocarcinomas arise more often in the periphery of the lung. Almost all cancers proximal of the trachea are squamous cell carcinomas. These findings indicate that histologic-type tumors are nonuniformly distributed in the lungs. Data compiled in these and other studies 511 CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES suggest that cancer (with no type distinction) is distributed with the following approximate frequency: ∼13% in the orallaryngeal cavity, <1% in the trachea, 6–28% in the main bronchi, 49–68% in the lobar bronchi, and 10–13% in the periphery including the segmental bronchi. The nature of the large variability in bronchial tumor statistics is unknown to the authors, but may represent, in part, different detection methods. In comparison, in vivo measurements of cigarette smoke deposition in living subjects range from 22 to 89% (see review by Robinson and Yu 2001), depending on the cigarette brand and reflecting intersubject physiological and morphological variability. Based on analyses of clearance rates using radioactive tracers, estimates of regional deposition of CSP in living subjects include 11–23% deposition in the extrathoracic airways, 46–63% deposition in the tracheobronchial (TB) airways, and 26–35% deposition in the pulmonary (P) region (Pritchard and Black 1984; Hicks et al. 1986). In general, these findings suggest a relationship between CSP deposition patterns and the occurrence of tumors in specific regions of the respiratory tract (RT) (Robinson and Yu 2001). Deposition Data The clinical (indirect) evidence is supported by measurements of regional and local CSP deposition in replica casts of the first few generations of the upper human airways (Ermala and Holsti 1955; Martonen et al. 1987). Overall, CSP were found to collect preferentially in specific tracheobronchial regions of the human airways. In particular, hot spots of CSP deposition were found at the carinal ridges, within bifurcation zones, and along the posterior surfaces of downstream tubular airway segments (Churg and Vedal 1996). These findings are consistent with local secondary flow patterns (Martonen 1992; Hofmann 1996). However, such a deposition profile resembles deposition of an aerosol with a much larger mass median aerodynamic diameter (MMAD) than that representative of cigarette smoke. This suggests that cigarette smoke particles deposit as if they have a much larger effective size. Deposition Models A puff of cigarette smoke consists of approximately 70% ambient air, 17% gaseous species originated from combustion and thermal degradation, 8% particulate matter (PM), and 5% miscellaneous vapor components (Jenkins et al. 1979). The particulate matter in fresh CSP has a polydisperse size distribution, with properties as specified in Table 1 (Robinson 1998). In particular, the miniscule solid-to-gas volume fraction (Martonen 1992) indicates that the average interparticle spacing is very large relative to the particle size. Since cigarette smoke is mostly air, previous studies usually neglected the interparticle forces, calculating particle motion and deposition based on a single particle mechanics. This approach results in about 22–53% total deposition, primarily in the pulmonary region (Yu and Diu 1983; Task Group on Lung Dynamics 1966; Muller et al. 1990), which is inconsistent with Table 1 Typical properties of fresh cigarette smoke (compiled from Robinson 1998) Number concentration Density of the solid fraction Solid-to-gas volume fraction Count mean diameter (CMD) Mass mean diameter (MMD) Mass mean aerodynamic diameter (MMAD) Geometric standard deviation (GSD) Coagulation rate 2–7 × 109 cm−3 0.98–2.47 g cm−3 <10−4 0.2–0.35 µm 0.25–0.35 µm 0.35–0.55 µm 1.2–1.64 4.8–23.8 × 10−10 cm3 /s the clinical and experimental studies cited above. These studies considered steady breathing with normal tidal volumes and stable monodisperse particles (i.e., PM of constant size). Yet CSP is known to coagulate (Keith 1982; Robinson and Yu 1998) and to be slightly hygroscopic (McCusker et al. 1981; Kousaka et al. 1982; Hicks et al. 1986; Muller et al. 1990; Robinson and Yu 1999). In addition, smokers have a breathing pattern different from normal breathing, with about twice the tidal volume (Hinds et al. 1983). Yet accounting for these aspects in deposition models, alone and in combination, could not explain the enhanced deposition of CSP in the upper bronchial airways (Robinson and Yu 2001). Cloud Effect The predicted preferential pulmonary CSP deposition is attributed to the smallness of individual particles, the deposition of which is governed by diffusion. Indeed, theoretical considerations suggest that due to their small size, CSP penetrate into distal regions of the respiratory tract and deposit mostly in the pulmonary airways. A plausible explanation for the discrepancy between theoretical deposition results and clinical and laboratory observations may be attributed to particle-particle interactions, sometimes referred to as the cloud or colligative effect (Martonen 1992; Martonen and Musante 2000; Robinson and Yu 2001). Due to screening, particle-particle interactions have the effect of decreasing the drag on some particles, thereby increasing their mobility. This modifies the particle relaxation time and, hence, the parameters that govern particle deposition, and may lead to enhanced deposition in the upper tracheobronchial (TB) region. In fact, cloud behavior has been observed (Slack 1963a,b), and it was suggested that CSP entering the respiratory tract may indeed have characteristics consistent with cloud behavior (Ingebrethsen 1989; Phalen et al. 1994). Possible mechanisms by which clouds of cigarette smoke can form in the human respiratory tract were discussed by Martonen (1992). Interactions among cloud members make cloud mechanics far more complex than that of individual particles. In general there are two types of swarm interactions: hydrodynamic and thermodynamic. While hydrodynamic interactions 512 D. M. BRODAY AND R. ROBINSON require intervening of fluid between the particles, thermodynamic interactions occur as a result of contact between particles or due to the presence of a conservative potential field. Thermodynamic interactions such as volume exclusion, elastoplastic collisions, and electrostatic forces are characterized by strong albeit short-range forces. Hydrodynamic interactions, on the other hand, are relatively weak (with the exception of lubrication forces) but can pertain at a distance. This work considers the weakest among the interparticle hydrodynamic interactions, which nevertheless will be shown to significantly alter the deposition pattern along the respiratory tract. CLOUD MODEL Cloud Definition An aerosol cloud is defined as a region of relatively high aerosol concentration in a much larger region of clean air (Hinds 1999). More precisely, it is a swarm of fine particles distributed throughout an identifiable connected volume (albeit with fuzzy boundaries due to a negligible surface tension) within a much larger expanse of particle-free suspending fluid (air) (Schaflinger and Machu 1999; Machu et al. 2001). Thus, the aerosol cloud represents an effective continuum of excess mass upon which gravity is pulling. In dilute clouds (and droplet suspensions) the pseudo fluid is Newtonian, with a viscosity essentially the same as that of the pure fluid (Martonen 1992). Consider a cloud of n identical spherical solid particles, each with a diameter 2a and density ρ p . For simplicity, the cloud is assumed to be a spherical enclosure of diameter 2b. The number concentration, c, of the particles in the cloud is c= n , 4/3πb3 [1] and the volume fraction, φ, of the solid phase is φ = 4/3πa 3 c = n µ ¶3 a = n R −3 , b [2] R being the size ratio of the cloud and the monodisperse individual particles constituting it. The density of the cloud, ρc , can be expressed as ρc = φρ p + (1 − φ)ρ f , [3] where ρ p is the density of the solid phase (0.98–2.47 times the density of water at standard conditions) and ρ f is the density of the gas phase (∼1.31 mg cm−3 ) (Martonen 1992). The settling velocity (the equilibrium velocity attained by a freely moving particle settling slowly under gravity in a viscous fluid) of infinitely diluted fine solid spherical particles in an unbounded viscous domain, v p∞ , is v p∞ = 2a 2 (ρ p − ρ f )g Cc (a). 9µ [4] Here g is the gravity acceleration, µ is the medium (air) viscosity, and Cc is Cunningham’s slip correction factor. The latter corrects the drag on fine particles for which the continuum regime does not apply, and which may experience slip velocity. For spheres, the Cunningham’s correction factor is (Hinds 1999) Cc (a) = 1 + Kn(1.17 + 0.525 exp{−0.78/Kn}), 0.1 < Kn < 10, [5] where Kn = λ/a is the Knudsen number, measuring the ratio of the mean free path of air at given conditions, λ, to the particle radius. Equation (4) is used to normalize the settling velocities of particle clouds in the models discussed hereinafter. The derivation of Equation (4) is based on the assumption that the relative particle-air velocity can be described as a creeping flow. Namely, that Re p = v p∞ a/ν ¿ 1, where Re p is the particle Reynolds number and ν is the kinematic viscosity of air. A finite swarm of particles may take a meaningful macroscopic identity as a cloud. To be able to describe hydrodynamic interactions within clouds using expressions pertinent to creeping flows requires a more stringent condition, which can be expressed as 2(ρc − ρ f )gb3 = φ R 3 Re p /Cc (a) 9µν = nRe p /Cc (a) < 1, Rec = vc b/ν = [6] where Rec is the cloud Reynolds number. For CSP, Re p is of the order of O(10−8 –10−6 ). If indeed cloud motion occurs in the respiratory tract, the cloud size cannot exceed that of the glottis aperture, d ∼ O(1) mm. For the maximum CSP concentration reported, c = 3×109 cm−3 , the number of particles in the cloud, n, can not exceed O(106 ), hence Rec ≤ O(1). Thus, the disturbance to the local flow induced by the motion of a swarm of fine particles confined to a finite volume can be described in most cases by expressions relevant to low Reynolds number hydrodynamics. If a swarm of particles indeed moves as an effective cloud, the particles constituting it will each move with a common apparent velocity. Since the velocity of cloud members is larger than the velocity of any individual particle had it been moving as an isolated particle, it is important to know whether the motion of the particles is affected by their own inertia. This issue will be addressed in the Deposition Model section. For now, the inertia of individual cloud particles is measured by means of the Stokes number, St, St ≡ m p Mp , dgen /U [7] where m p is the particle’s mass, M p is its mobility, dgen is the airway diameter, and U is the average air velocity in the airway. The denominator in Equation (7) represents a characteristic time the particle stays within an airway, used to normalize the particle’s relaxation time (the numerator). For isolated CSP 513 CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES particles, St ¿ 1. When cloud motion prevails, the particle mobility is altered and, hence, St may be of the order of unity. It will be shown (see Equation (28)) that for a given particle size the larger the cloud the larger the particle inertia, resulting from the increased relative (settling) velocity between the particle and the air. Namely, particle inertia is affected by the presence of nearby like particles via the alteration they induce to its (self) mobility. Cloud Settling Solid Sphere Model. Previous studies addressing the hydrodynamic colligative effect considered the particle cloud to be a solid sphere with air flowing around it (cf. Hinds 1999). Thus, the settling velocity was given in terms of the cloud’s diameter and density. After accounting for buoyancy, the settling velocity relative to Equation (4) is vsolid sphere = φ R2 . Cc (a) [8] Note that since the size of the cloud is large, Cc (b) ∼ = 1 and is neglected in Equation (8). In the unlikely event that Rec > 1, the motion of the cloud will be non-Stokesian. The cloud’s settling velocity, vc , in such cases (normalized with respect to Equation (4)) is approximately (Frielander 1977; Hinds 1999) s φR n ¢ vc = ¡ , [9] 1 + 0.25Re2/3 Cc (a) c since the drag coefficient is C D = 24/Rec (1 + 0.25Re2/3 c ). This expression is considered valid for Rec < 1000, with a maximum of 7% error (Frielander 1977). Fluid Sphere Model. Alternatively, the cloud can be considered a spherical fluid domain of distinct density and viscosity, unmixed with the surrounding air (Martonen 1992). In contrast to the solid sphere model, this model involves nonvanishing shear stresses on the cloud boundary, which induces internal circulation. The density of the fluid region is given by Equation (3); with respect to the bulk viscosity µ, its viscosity µc is modified to first order according to Einstein’s formula, µc = (1+2.5φ)µ, and the force acting on the fluid sphere follows the Hadamard– Rybcznski drag (Happel and Brenner 1973) Ffluid sphere = 6πµbU 3µc + 2µ . 3µc + 3µ [10] In cases when φ ¿ 1, µc ∼ = µ and the factor (i.e., the reduced drag) in Equation (10) equals 5/6. It turns out, therefore, that due to less dissipation experienced when a fluid particle rather than a solid particle travels within a viscous fluid, the normalized settling velocity of the cloud is 20% larger than that given in Equation (8), vfluid sphere = 6φ R 2 . 5Cc (a) [11] The fluid sphere model predicts that small clouds of diameter ranging from 5 to 20 microns (about 10–100 times larger than the CMD of cigarette smoke particles) deposit with a very high deposition efficiency, thus contributing to the ∼99% deposition efficiency predicted in the tracheobronchial airways (Martonen and Musante 2000). This prediction is inconsistent with experimental evidence (Pritchard and Black 1984; Hicks et al. 1986), although it agrees with the integrated spatial distribution of malignant tumors in the upper bronchial airways (Martonen 1992). Both the solid sphere and the fluid sphere cloud models use a simplified approach to describe the colligative effect. Jointly, they consider homogeneous impermeable media and permit only bimodal motion. Namely, individual particles can move either as isolated particles in an ideal viscous flow, being unaffected by the presence of nearby particles, or collectively as a cloud. The cloud is modeled as an impermeable domain with the air passing around it, and its size is the dominant physical parameter. Clearly there are cases where the surrounding air does flow through the cloud and mixes with it, dispersing cloud particles, reducing the cloud’s initial concentration, and deforming its shape. The solid sphere and the fluid sphere models do not account for these processes, since they consider interactions between the cloud and the particle-free fluid surrounding it only via the action of normal and shear stresses on its rigid boundary. Furthermore, they do not account for any interactions among the particles within the cloud. Reflection Method. For weakly interacting, freely moving particles in a dilute cloud, the settling velocity of individual particles can be calculated by the reflections method. Summation of all the pairwise hydrodynamic interactions for a given particle array yields (Happel and Brenner 1973) vreflection = 1 . 1 + kφ 1/3 [12] The constant k ranges between 1.3 and 1.9, depending on the randomness (or orderliness) of the structure of the particle array. For example, for a cubic lattice arrangement k ∼ 1.6. To describe the dynamics of many-particle systems one needs to consider hydrodynamic and thermodynamic interactions, as described above. Unlike thermodynamic interactions, pairwise hydrodynamic interactions between any two particles are modified by the presence of a third nearby particle. Mathematically, the reduced hydrodynamic resistance (per particle) can be described by a modified friction tensor, which replaces the Stokes’ friction tensor for an isolated sphere. The modified drag on any particle can be thought of as an infinite sum of reflections of the disturbances induced by all the particles in the cloud, which alter the local flow field around any particle. Swarm Model. The classical approach to describe the motion of a particle cloud within a viscous fluid is by the cell model (Happel and Brenner 1973), also known as the swarm model (Neal et al. 1973). In this model the cloud is represented by a single typical particle, surrounded by air that fills a hypothetical 514 D. M. BRODAY AND R. ROBINSON spherical fluid domain of diameter 2b∗ . In terms of the actual cloud size, 2b, and the number of particles per cloud, n, b∗ can be expressed as b∗ = bn −1/3 . Using Happel’s well-known formula for the drag on a solid sphere contained in a shear-free cell and implementing Equation (2), the setting velocity is vswarm = 6 − 9φ 1/3 + 9φ 5/3 − 6φ 2 . 6 + 4φ 5/3 [13] Note the canceling out of the Cunningham correction factor in Equations (12) and (13), because these cloud models are based on the motion of a single representative particle. Equation (13) describes the motion of each particle within the cloud, accounting for the crowding effect only in terms of the effect of the finite interparticle spacing on the particle mobility. It is intrinsically assumed that the cloud is monodisperse and that all particles share a similar motion. Therefore, there is no relative motion among cloud particles, i.e., the cloud moves like a rigid, albeit porous, body. One of the main critiques of the swarm model refers to the fact that boundary conditions are fulfilled on a spherical enclosure and, therefore, an aggregate of such cells does not fill the space but rather leaves “holes.” Another problem relates to the boundary conditions imposed on each cell’s boundary, causing it to be detached from neighboring cells. Stokesian Dynamics Simulations. The direct way to account for hydrodynamic interactions among cloud particles is by utilizing Stokesian dynamics (Brady and Bosis 1998). Stokesian dynamics tracks the motion of numerous particles in viscous liquid when thermal motions are overdamped and, hence, random forces are neglected. Recently, Machu et al. (2001) used an even cruder representation of the hydrodynamic interactions among the particles. In their model each particle settles essentially in isolation, with the Stokes settling velocity in Equation (4) relative to the local velocity. The velocity field is obtained by superimposing Stokeslet disturbance fields induced by all the particles, each being regarded as itself settling in isolation relative to its own local flow. At this level of approximation the particles appear like point forces and their size does not enter the calculation directly. The justification for this is that under the influence of a conservative force field, the collective far-field effects rather than the nearest-neighbor interactions dominate the motion of individual particles in a swarm (Brenner 1999). For a sufficiently low volume fraction (0.05 < φ < 0.07) of non-neutrally buoyant particles in a quiescent fluid, the agreement between experimental data and theoretical predictions is remarkable (Machu et al. 2001). These findings support viewing the swarm as a continuum pseudofluid, like in the Brinkman model. Brinkman’s Model. For a solid volume fraction less than ∼30%, it was shown (Durlofsky and Brady 1989; Sangani and Mo 1994) that the drag on and the diffusivity of a test particle, obtained by Stokesian dynamics, are in excellent agreement with those obtained by the much more simplified Brinkman’s effective medium approximation. Since the volume fraction in cigarette smoke is orders of magnitude lower than 30%, it seems appropriate to apply Brinkman’s model to describe the cloud colligative effect. Properties derived by applying Brinkman’s model to porous media with volume fractions not exceeding 30%, such as the medium permeability, its hydrodynamic resistance, and its heat conductivity, are all in excellent agreement with those derived by the rigorous numerical calculations involving averaging over numerous initial stochastic configurations (Sangani and Yao 1988a,b). Furthermore, predictions obtained using Brinkman’s effective medium approach agree favorably with experimental data on homogeneous porous materials (Jackson and James 1986). Hence, the motion of CSP clouds, where individual particles are supposed to weakly interact with each other, will be described here in terms of a sparse porous medium using Brinkman’s equation. Brinkman’s effective medium accounts for hydrodynamic interactions attributed to the presence of a less mobile (quasistationary) particle fraction within the cloud. In essence, since CSP clouds consist of a distribution of particles with respect to size, and since the settling velocity is highly size dependent, at a “local” scale some particles can be regarded as relatively immobile compared to others. In such “fixed” clouds (Hinds 1999) the less mobile particles move uniformly without a relative motion between each other and, hence, the cloud structure remains constant. The presence of a (quasi-) immobile fraction significantly slows the local-scale (relative) motion of particles from the mobile fraction (Dodd et al. 1995; Broday 2000). This so-called Brinkman’s screening dominates the hydrodynamic resistance acting on the mobile fraction, due to the smallness of its characteristic length scale. Brinkman’s equation is a modification of Stokes’ equation, including an additional term that accounts for the hydrodynamic resistance induced by the quasi-immobile fraction, µ ∇ p̃ = − ũ + µ∇ 2 ũ, k [14] where p is pressure, u is the particle velocity, and k is the medium permeability. Two relevant problems can be solved using Equation (14). The first problem involves the motion of a solid spherical particle within a finite random array of like particles that consist a porous structure immersed in a viscous fluid. In fact, this configuration is very close to the original problem, presented by Brinkman (1947) and later reworked by Howells (1974), describing the motion of a solid particle in an unbounded swarm of similar particles. The infiniteness of the array of singularities is of negligible significance for particles far away from the (fuzzy) boundary of the cloud, since the size ratio of the cloud to individual particles is very large, R À 1, and the effect of the boundary decays very fast (James and Davis 2001). Under such conditions, the normalized settling velocity, v p , of such particles is v p = F p−1 = (1 + α + α 2 /9)−1 , [15] CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES where F p is the excess drag on the particle over the Stokesian drag and α ≡ a 2 /k is the reciprocal of the normalized permeability, also called (the square of) Brinkman’s screening length. It can be shown (cf. Broday 2000) that the relation between α and φ is φ= 2α 2 . 9(1 + α + α 2 /3) [16] The other case relevant to this work is the motion of the cloud as a whole in a relatively particle-free viscous domain. Consider a spherical cloud composed of monodisperse fine particles and assume that the cloud does not deform and that it moves in an unbounded viscous domain (the hydrodynamic resistance induced by proximate walls will be discussed in the next section). In our terminology, the drag Fc on a cloud moving in an unbounded viscous domain relative to the Stokesian drag on one of the solid particles consisting it is (Brinkman 1947; Neal et al. 1973; Davis and Stone 1993) Fc = R £ ¤ R) 2(α R)2 1 − tanh(α αR £ ¤. R) 2(α R)2 + 3 1 − tanh(α αR [17] The normalized settling velocity of the cloud by this model is vc = φ R3 . Fc Cc (a) 515 unity. (4) For large φs, the settling velocity of a “Brinkman cloud” asymptotes the settling velocity calculated by the fluid sphere model, the latter accounting for an inner circulation; (5) Brinkman’s effective medium approach provides a simple yet powerful model to describe cloud settling at arbitrary solid fraction (up to φ ∼ 0.3). In practice two regimes are identified, for φ ≤ φcr particles tend to settle individually, being affected slightly by the presence of neighboring particles (the crowding effect). For φ > φcr particles tend to settle as a cloud with a permeability that depends on φ. The transition between the single solid particle behavior and the rigid impermeable cloud regime is continuous, and its smoothness depends on the size of the particles constituting the cloud (via Cc (a)). Judging by the surprisingly good asymptotic behavior of the results of Brinkman’s cloud model, the assumption about the relative stillness of some cloud particles seems to introduce no difficulty. Yet, it is noteworthy that the internal circulation observed within regions of different viscosities (droplets, bubbles) and/or permeabilities (suspension droplets, clouds) cannot be described by Brinkman’s cloud model. Hence, while dilute clouds experience air flowing through them, curved streamlines that bypass the dense region and a diminishing flow through it are evident for less-permeable areas (Broday 2000). The results in Figures 1a and 1b and the data in Table 1 suggest that for CSP, α is of the order of 10−2 . [18] An expression similar to Equation (18) was obtained by Arachi (1999). Model Comparison Figures 1a and 1b depict the cloud’s settling velocity calculated by the different models presented above, with Cunningham’s slip factor calculated for a = 0.15 µm (half the CMD of CSP, see Table 1). The difference in the settling velocities predicted for small φs by the two Brinkman models, Equations (15) and (18), corresponds exactly to the reciprocal of Cc (a). This term appears in Equation (18) as a result of normalization by the settling velocity of a typical particle, which is much smaller than the cloud (R À 1). On the other hand, Cc (a) is missing from Equation (15), since the latter deals with a single particle identical in size to the particle for which Equation (4) was derived. From Figures 1a and 1b it is evident that: (1) the fluid sphere model is not applicable for very dilute clouds, since it does not match the settling of individual particles consisting the cloud; (2) the swarm model underpredicts the settling velocity of particles in dilute clouds (see also Broday 2000); (3) for low φs, the cloud settling velocity in Equation (18) approaches the settling velocity of individual CSP in Brinkman media (Equation (15)), which itself is asymptotic to the Stokes settling velocity. However, due to the normalization, at low φs vc appears in Figure 1 within the Cunningham’s slip correction factor from MOTION OF CSP CLOUDS IN THE HUMAN AIRWAYS During their motion along the respiratory tract, CSP clouds may undergo macroscopic deformation. Simultaneously, the fine particles constituting the clouds may experience coagulation, hygroscopic growth, and deposition on airway surfaces. While hygroscopic growth results in an increase in the cloud’s solid volume fraction, coagulation and deposition processes tend to decrease the number concentration of persistent CSP, weakening the cloud effect in subsequent airways. Furthermore, as will be discussed hereinafter, recent experimental findings suggest that the dynamics of suspension drops (drops containing a swarm of fine particles) is identical to that of liquid drops (a connected volume of homogenous liquid, distinguished by some thermophysical properties from an expanse of outer fluid) with a negligible surface tension (Schaflinger and Machu 1999; Machu et al. 2001). In addressing the motion of CSP in the human airways we will conceptually extend this analogy to particle clouds, accounting for the relevant parameter domain. The motion of particle clouds may be subjected to further effects, such as the proximity to the airway walls. Both particle deformation and particle–wall interactions affect the drag acting on the cloud, and may induce its drift across the streamlines towards or away from the walls. Wall Effect In general, particles approaching bounding walls experience excess hydrodynamic drag as a result of the increased shear in the wall proximity. Due to the linearity of both Stokes’ and 516 D. M. BRODAY AND R. ROBINSON (a) (b) Figure 1. Variation of the cloud settling velocity with the solid volume fraction according to different models (a), and variation of the Brinkman’s cloud settling velocity with the cloud size (b). All models consider monodisperse fine particles with a diameter of 2a = 0.3 µm. CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES Brinkman’s equations, the extra drag imposed by the wall can be accounted for by a factor in the force expression. The linearity also implies that no lift (i.e., normal) force acts on spherical particles that translate slowly along a flat wall (Goldman et al. 1967a,b; Pozrikidis 1990). With respect to the Laplace-like Stokes equation, there are fewer separable solutions in orthogonal coordinate systems for the Helmholtz-like Brinkman equation. In particular, the Brinkman equation is inseparable in a bispherical coordinate system (Kim and Russel 1985), the natural coordinate system to describe particle-particle and particle-wall interactions. Indeed, this explains the lack of analytical expressions for wall effects in Brinkman’s flows. For example, the motion of a porous sphere towards a flat boundary was studied only recently (Davis 2001), whereas translation of a porous sphere proximate to a solid boundary has not been studied yet to the best of our knowledge. For the latter case, a possible approximation may involve using expressions for the excess hydrodynamic drag induced by adjacent walls on solid or liquid particles (Happel and Brenner 1973). The excess drag on a solid sphere that translates slowly in a viscous fluid at a constant separation H from a flat wall, FW,s , is (Happel and Brenner 1973). · FW,s µ 4 ¶¸−1 9a a a3 = 1− +O . + 16H 8H 3 H4 [19] 517 The authors are unaware of any similar expression for nonsolid particles. According to Clift et al. (1978), wall effects significantly alter drop motion if the ratio of the drop to tube radii is greater than 0.1. Applying this criterion to cloud motion as well, CSP clouds moving concentrically in the upper tracheobronchial airways may experience non-negligible excess hydrodynamic resistance resulting from a limited particle-wall spacing. The comparable case of a solid sphere translating parallel to a flat wall in a Brinkman effective medium (i.e., motion of individual particles within a bounded swarm) was recently worked out numerically (Broday 2002). Depending on the separation between the particle and the wall and on the medium permeability, the excess drag is depicted in Figure 2. In general, as H/a decreases the wall effect becomes more appreciable, modifying the particle mobility, increasing the residence times within airway segments, and consequently enhancing particle deposition by diffusion and gravitational settling. Accounting for the radial position of the cloud is beyond the scope of this work. Hence, in the following simulations concentric motion of the cloud in the airways is assumed (see also the Cloud Deformation section of this article). Particle Migration In flows with non-negligible shear, fine particles that either lead ahead or lag behind the bulk flow (e.g., as a result of gravity) Figure 2. Excess drag on a solid sphere that translates in Brinkman and Stokes media parallel to a solid wall. Solid lines are the numerical results (Broday 2002), dashed line is the analytical approximation (Equation (19)). 518 D. M. BRODAY AND R. ROBINSON may experience redistribution as the result of drifting across the streamlines (Broday et al. 1998). In part, the migration results from hydrodynamic interactions between deformable or nonspherical particles and non-reversible inertial effects in the presence of bounding walls. Specifically, isolated drops and bubbles moving in shear flows and characterized by finite Re p tend to migrate toward or away from the bounding wall (Goldsmith and Mason 1962) and to accumulate in an annular region about halfway between the tube centerline and the wall. This behavior resembles that of spherical particles (Happel and Brenner 1973) and fibers (Broday 1996; Broday et al. 1998), where particles migrate across the streamlines even when the fluid inertia is negligible. On the other hand, particle-particle interactions in a swarm tend to spread out droplets and fine solid particles and to disperse them more homogenously in the cross section (Han et al. 1999). The smallness of CSP and their negligible inertia suggest that effects caused by particle migration across the streamlines within the airways are marginal. Cloud Deformation The degree to which particles deform is an outcome of a competition between shear forces and capillary forces, the latter tending to restore an interfacial surface corresponding to minimum free energy. The larger the interfacial surface tension, the larger the tendency of the particle to have a spherical shape (Koh and Leal 1989, 1990; Pozrikidis 1990). For deformable particles, the ratio of the gravity force to the interfacial force that opposes deformation during settling in a quiescent fluid is called the Bond number, Bo = 1ρgb2 /σ , where σ is the surface tension and 1ρ is the density difference between the particle and the surrounding fluid. When deformable particles move in a shear flow, the force ratio is termed the capillary number, Ca = µU/σ , representing the relative magnitude of the shear force to the interfacial force. The ratio of the Bond number to the capillary number corresponds to the relative magnitude of the settling velocity compared to the bulk velocity. Usually, when shear prevails Ca À Bo. When either the Bond or the capillary numbers are large, the surface tension cannot oppose deformation, and deformable particles tend to be nonspherical. The deformation process is highly nonlinear because the shape evolves as a result of shear stresses that are determined by the local disturbance to the flow, caused by the motion of the particle itself. In shear flows, droplets and bubbles extend longitudinally and become elongated (prolate) spheroids that eventually disintegrate into a number of small spherical entities (Brenner 1999). To minimize shear stresses, stretched out droplets tend to align with the flow and situate at the centerline (Koh and Leal 1989, 1990). In our simulations we therefore consider concentric cloud motion. Recently, Schaflinger and Machu (1999) studied the settling of suspension drops in quiescent fluid. Throughout the experiment, a distinct interface between the suspension and the clear fluid surrounding it was visible. Internal circulation was observed within the drop, as well as an evolutionary sequence of deformations that exhibited copious similarities to the deformation process of miscible drops in viscous fluid (Kojima et al. 1984). Following Kojima’s work, an apparent interfacial tension between the pure fluid and the suspension drop was estimated (σ ∼ 3.e-5 Nm−1 for φ = 0.04–0.08).1 The finite interfacial tension is consistent with observations that a spherical blob settling at finite Rec in an unbounded fluid do not experience shape changes (Nitsche and Batchelor 1997). The envelope of closed streamlines surrounding the blob seems to lie slightly inside of the fuzzy spherical boundary of the drop, with particles lying outside of that envelope being swept to the rear, forming a tail. These observations are reminiscent of the Hadamard– Rybchinsky fluid-sphere model of immiscible fluids, for which the drag corresponds to that calculated by Brinkman’s model for a dense, quasi-impermeable, core (Figure 1). For thinner regions (dilute clouds) mixing due to entrainment of clear fluid (air) is expected, resulting from streamlines that cross the cloud “boundary.” From a theoretical perspective, the existence of a macroscopic interfacial tension is expected because of the tendency of a cluster of particles (molecules) to lower its collective potential energy by agglomeration, thus forming a lattice in which inner particles are completely surrounded (Nitsche and Schaflinger 2001). This naturally leads to the standard concept of surface energy, i.e., the work required to increase the number of particles (molecules) residing in an incompletely surrounded state at the surface. This idea can be extended to include interfacial tension-like phenomena even when a clear physical boundary between two domains (i.e., the cloud and the surrounding air) does not exist. This approach was utilized indirectly for simulating the settling and stretching of a swarm of particles (blob) within a bounded domain, accounting for particle-wall interactions (Brenner 1999). If we assume that the interface of a particle cloud (suspension drop) has no mechanical properties other than a pseudosurface tension, continuity of velocity and tangential stresses on it must exist (Batchelor 1967). This conforms with the present description of the cloud in terms of an effective medium and with the boundary conditions applied to Equation (14) in obtaining Equation (17) (Brinkman 1947; Neal et al. 1973; Davis and Stone 1993). The deformation process described by Schaflinger and Machu (1999) and Machu et al. (2001) was observed for suspension droplets settling in viscous liquid under the following conditions: a = 50 µm, R = 80, 1ρ/ρl = 1.32, φ = 0.05–0.075, and a kinematic viscosity 6.6 times higher than that of air. In contrast, the CSP cloud is characterized by CMD of about 0.3 µm, 1ρ/ρg ∼ 750–1800, and φ ≈ 10−4 . Thus, it is not clear whether the findings cited above are relevant to cigarette smoke. Rigorously, the requirements are Rec ¿ 1 and Bo À 1. While the first condition usually holds for CSP clouds with b ≤ O (1 mm), 1 In a subsequent study, however, Machu et al. (2001) presented simulations showing that the deformation of suspension drops may result solely from Stokesian hydrodynamics, without accounting for interfacial forces. 519 CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES the second condition normally requires clouds of size larger than about 5 mm, introducing a contradicting requirement. Yet the importance of the analogy, if it holds, is in the ability to learn about the deformation of CSP clouds within the respiratory tract from studies conducted on the motion of deformable drops in tubes and pipes. The relaxation time for cloud deformation is τ ∼ bµ/σ ∼ R ∗ 10−7 s. For CSP clouds it is expected to be of the order of O(10−6 − 10−3 s), much shorter than the residence time in any bronchial generation. The shape distortion is such that the excess velocity of the particle relative to the air is reduced. Namely, for a given particle mass (volume) the settling velocity is higher for particles with larger interfacial tension. Since we expect very small (if any) interfacial tension for the “miscible” clouds, deformations will be appreciable. According to Bernoulli’s law, cloud deformation will take place up to an equilibrium state, at which point the difference in dynamic pressure between the fore and aft portions of the cloud is balanced by the capillary pressure. Consequently, the cloud extends in the flow direction to an order of magnitude of l ∼ O(2σ/ρU 2 ), while its cross sectional area is of an order of magnitude of S ∼ O(V /l), V being the cloud volume. Cloud fragmentation is expected for extremely elongated or distorted clouds, possibly in bifurcation zones where flow reversal and separation may prevail. Deposition Model General. Deposition of CSP in the human respiratory tract is determined for an adult smoker using the improved trumpet model presented previously by Robinson and Yu (2001), based on Weibel’s model A. In this model CSP size distribution and concentration are updated at each generation, accounting for changes in hygroscopic growth, polydisperse coagulation that results from kinematic effects (turbulence, laminar shear, differential settling), Brownian motion, particle charge, and deposition due to the combined mechanisms of gravitational settling, inertial impaction, diffusion, and electrostatic image forces. These processes are implemented within a transport and deposition model that solves the one-dimensional aerosol general dynamic equation after it is integrated over the crosssectional area of the respiratory airways to yield average concentrations per unit length. It is assumed that concentration changes due to deposition and growth are independent. The model, which has been evaluated against experimental data for stable and nonstable aerosols, was modified here to account for the new cloud effect module. The model allows for an accurate account of the smoker’s breathing pattern, dividing the total 1870 ml tidal volume into a bolus of 54 ml—the puff—followed by clean air (Robinson and Yu 2001). Flow rates are based on a 3 s inhale, 1 s breath hold, and 3 s exhale (Hinds et al. 1983) and a uniformly expanding lung in which only the airways’ diameters change. Uniform velocity profiles and negligible axial diffusion are assumed. The initial CSP size distribution is taken from Keith (1982), which measured the properties of fresh smoke aged for less than 0.05 s (CMD of 0.25 µm, 1.3 GSD). The particle initial charge distribution follows data compiled by Robinson and Yu (2001). Since CSP are characterized by independent size and charge distributions, a three-dimensional array that is updated at each generation, representing discretizeation to 0.1 µm and 1 elementary charge, was used to track the concentration of CSP as they move through the lung. Cloud Behavior. At each generation the calculated CSP volume fraction is used to determine the particle-in-a-swarm and the swarm-of-particles normalized settling velocities, which are Equations (15) and (18), respectively. Particles are assumed to settle in a manner that minimizes energy dissipation (and therefore drag), and thus the model that yields the largest settling velocity (i.e., individual particles versus a cloud) is used. This criterion is similar to the one utilized when the solid sphere (Hinds 1999; Robinson and Yu 2001) or the fluid sphere (Martonen 1992; Martonen and Musante 2000) cloud models were considered. Yet, as seen previously, the transition between the two regimes is smoother for the Brinkman cloud model. All deposition mechanisms depend to a great extent, via the specific deposition parameters, on the particle mobility M p . Similarly, the colligative effect affects the deposition process by modifying the particle mobility and changing the deposition efficiencies accordingly. When only hydrodynamic interactions are accounted for, M p is given by Mp = v fp or Mp = vCc (a) , f c /n [20] where f p is the force acting on individual particles and f c is the collective force acting on the cloud as a whole. From Equations (15) and (17), f p = 6π µav F p /Cc (a) and f c = 6π µav Fc , thus the mobility of individual particles is Mp = C (a) c 6π µa F for single particle motion, p φ R 3 Cc (a) 6π µa Fc [21] for cloud motion. Unlike previous work (cf. Martonen and Musante 2000; Robinson and Yu 2001), we do not consider CSP to move within large rigid particle clouds while “losing” their individual properties. Rather, here CSP behave independently according to their own set of attributes, while simultaneously subjected to reduced drag (increased mobility) resulting from the disturbance to the flow introduced by the presence of numerous similar particles in their vicinity. In essence, CSP move as if contained within clouds while approaching the airway walls, but are susceptible to deposition as individual particles. Diffusion. Diffusion is the most significant deposition mechanism for fine particles that are subjected to and affected by random impaction of air molecules. According to Einstein’s theorem, the diffusion coefficient D is related to the particle 520 D. M. BRODAY AND R. ROBINSON mobility via D = kT M p , [22] where kT is the particle thermal energy. The colligative effect on diffusion of individual particles is accounted for by modifying the diffusion coefficient of individual CSP using the modified mobility given in Equation (21). The expression for deposition by diffusion implemented in the model follows the derivation of Ingham (1975), with the diffusion parameter expressed as 1= DL , 2 U dgen [23] where L and dgen are the length and diameter of airways in the current generation, respectively, and U is the mean air velocity within the airways. Inertial Impaction. Deposition by inertial impaction occurs at locations characterized by sharp streamline curvature, where the particle persistence promotes deposition on posterior airway walls. The efficiency of inertial deposition is calculated using expressions derived by Zhang et al. (1997), with the cloud effect introduced into the calculation via the definition of the Stokes number (Equation (7)), St = 2a 2 ρ p U Cc (a) φ R 3 . 9µdgen Fc [24] Note that when particles move independently of each other (i.e., when no cloud motion occurs) the Stokes number is only marginally affected by the presence of nearby particles, since F p is close to unity (Equation (15) and Figure 1). Gravitational Settling. Deposition by gravitational settling is implemented in the model using the expressions derived by Yu (1978) and Pich (1972), with the settling parameter being ε= 3gLv sin θ , 4dgen U [25] and θ being a typical generation-dependent airway orientation. The settling velocity v is either v p (Equation (15)) for single particle motion, or vc (Equation (18)) when cloud motion prevails. Electrostatic Precipitation. Deposition due to electrostatic image forces is important if the number of charges per particle is greater than ∼30 (Chan and Yu 1982; Yu 1985), with the electrostatic precipitation parameter being ζ = e2 z 2 L Cc (a) , 2 u 96π 2 ε0 µ a dgen [26] where ε0 is the dielectric constant of vacuum, e is the elementary charge, and z is the number of charges per particle. Normally, electrostatic deposition is negligible for CSP, since even after coagulation there are usually less than 10 charges per particle (Robinson and Yu 2001). Cloud Breakup. The total number of CSP in any subsequent (i + 1) generation can be calculated knowing the deposition efficiency in the previous (ith) generation and the details of the coagulation and hygroscopic growth processes in that generation. Yet, the fate of the clouds is unclear. Due to deformation, clouds may change size and increase in number. Furthermore, particle-free air residing in the airways may mix with the puff, diluting it and increasing its effective volume. Lacking experimental data, we account for these processes in a rather simplistic way, changing the cloud size deterministically along the respiratory pathway while keeping the total puff volume constant. Our results show (see below) that for realistic conditions, cloud behavior occurs only in the very proximal tracheobronchial airways, where mixing with resident air is negligible. This is in contrast with the previous predictions of Robinson and Yu (2001), where cloud motion was estimated in distal generations as deep as the 21st Weibel’s generation. Description of the mechanistic processes involved in cloud breakup is beyond the scope of this study. We thus assume here that the relationship between the size of the newly formed cloud and that of the parent cloud is · bi+1 dgen,i+1 = bi dgen,i ¸k , [27] where k = 0, 1, 2. In particular, for k = 0 the size of the cloud remains constant throughout the lung (see Martonen and Musante 2000). By using a nonzero value for k the cloud size changes along the respiratory pathway. Thus, k = 1 represents a size change such that the ratio of the cloud to the airway diameters is constant (Robinson and Yu 2001), while k = 2 represents a constant ratio of the cloud to the airway crosssectional area. Clearly, in all cases conservation of particle mass is ensured. Model Results Deposition of CSP in the human respiratory tract was calculated using three model variants. The simple (S) variant considers a stable polydisperse aerosol and does not account for particle-particle interactions. The cloud model variant (L) considers stable polydisperse aerosol, accounting for the colligative effects as described previously. The base case L-variant comprises a cloud with an initial diameter of 4000 µm and size that changes along the lung pathway according to Equation (27) with k = 1. A cloud diameter of 4000 µm, roughly the size of the glottis, represents an upper bound cloud size expected in the human respiratory tract. The third variant (LHC), in addition to colligative behavior, further includes the effect of hygroscopicity and coagulation on the evolution of the particle size distribution. Effect of Initial Cloud Size. Figure 3 depicts model predictions of CSP deposition profile in the lung for different initial cloud sizes. In contrast to the solely peripheral deposition of noninteracting individual CSP particles (model S), the increase in cloud size is associated with increase in proximal deposition CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES 521 Figure 3. Effect of initial cloud size on the deposition profile of CSP in the lungs, CMD = 0.25 µm, GSD = 1.3, k = 1. (in the trachea, main bronchi, and lobar bronchi) and a simultaneous decrease in pulmonary deposition (Table 2). As expected, the colligative effect is pronounced in the upper thoracic airways and ceases to exist shortly after. This is unlike Robinson and Yu’s (2001) results, where cloud motion prevailed in the pulmonary region (21st generation) as well. Modeled previously as fluid or solid spheres (Martonen and Musante 2000; Robinson and Yu 2001), CSP clouds as small as 40 µm in diameter already showed very high deposition (70– 99%) with proximal preference. Here, CSP clouds of initial size smaller than 1000 µm show negligible cloud behavior, having deposition profile similar to that predicted for noninteracting Table 2 Regional and total CSP deposition for different initial cloud diameter 2b0 and cloud size change parameter k = 1 Cloud size Total (%) No cloud effect 39 (model S) 43 2b0 = 1000 µm 46 2b0 = 2000 µm 55 2b0 = 3000 µm 62 2b0 = 4000 µm In vivo measurements 32–89 Tracheobronchial Pulmonary (%) (%) 4 35 5 15 29 40 46–63 38 31 26 22 26–35 particles (model S). Being essentially unaffected by sedimentation, which usually dominates deposition in the lower thoracic airways, deposition of CSP exhibits a double peak profile. Owing to the swarm effect, particles tend to deposit in the upper airways, whereas particles that survive proximal deposition tend to persist and deposit only in the deep pulmonary region. Indeed, the model predicts a wide and flat deposition minimum in the distal bronchial airways. Table 2 details the total and regional deposition, where tracheobronchial deposition is defined as deposition in generations 0–16 of Weibel’s lung model A. These results compare favorably with those obtained in clinical studies (Ellett and Nelson 1985; Martonen et al. 1987; Yang et al. 1989), and in in vivo (Pritchard and Black 1984; Hicks et al. 1986) and replica casts (Ermala and Holsti 1955; Martonen et al. 1987) measurements. Effect of Cloud Size Decrease Rate. The effect of the degree by which the size of the cloud changes between successive generations, implemented by means of the magnitude of k in Equation (27), is depicted in Figures 4a and 4b. Figure 4a shows deposition profiles of clouds with different size decrease rates, all having initial sizes of 4000 µm. It is evident that the smaller the decrease in size between succeeding generations, the larger the deposition in the proximal tracheobronchial airways (see also Table 3). Note that the initial cloud size implies that the k = 0 case is aphysical, since it represents clouds that cannot penetrate any airways distal of the fourth generation. Figure 4b depicts the effect of cloud size decrease on deposition of CSP 522 D. M. BRODAY AND R. ROBINSON (a) (b) Figure 4. Effect of the extent of cloud size decrease between successive generations on CSP deposition profile in the lungs, CMD = 0.25 µm, GSD = 1.3. (a) Initial cloud size is 2b0 = 4000 µm, (b) final common cloud size is 5 µm. CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES Table 3 Regional and total deposition for different cloud size change parameter, k Cloud rule No cloud effect (model S) k=1 k=2 Total (%) Tracheobronchial (%) Pulmonary (%) 39 4 35 62 48 40 19 22 29 The initial diameter is 2b0 = 4000 µm. that attain a 5 µm cloud size in the airways of the last generation of Weibel’s lung model. The difference between our results for constant cloud size (k = 0) and those obtained by Martonen and Musante (2000) are attributed to the different cloud models used, and in particular to the way by which these models are implemented and modify the particle mobility. Indeed, using the fluid sphere cloud model and considering motion and deposition of rigid clouds, we reproduced Martonen and Musante’s results, obtaining 99% total deposition while reducing drastically the deposition in the peripheral airways (TB 72.7%, P 26.5%). In contrast, the small cloud size in the k = 0 case (2b0 = 5 µm) and the moderate decrease in cloud size in the k = 1 case (2b0 = 220 µm) reveal a negligible cloud behavior according to our model, in agreement with the trend depicted 523 in Figure 3. In fact, the three lines in Figure 4b corresponding to k = 0, k = 1, and “no cloud” (model S) are indistinguishable, representing total deposition of ∼39% (k = 0: TB 3.9%, P 35.2%; k = 1: TB 4.1%, P 35.1%; “no cloud”: TB 3.9%, P 35.3%). On the other hand, the k = 2 case (2b0 = 9640 µm) does show significant cloud behavior, having total deposition of 67.5% (TB 50.4%, P 17.1%). Apart from being in better agreement with in vivo data (see Table 2), it is our belief that accounting for a permeable and deforming (size-changing) CSP cloud represents a more realistic description of the physical process occurring in the lungs. Deposition by Mechanism. Figure 5 portrays the deposition profile by mechanism. As expected, particle inertia and gravitational settling play the major role in promoting proximal deposition. Once the colligative effect (Equation (17)) ceases (due to cloud disintegration) and the Stokes number represents the inertia of individual CSP, which is only slightly affected by the presence of nearby like particles, diffusion becomes the major deposition mechanism. The weak crowding effect (Equation (15)) increases diffusion slightly in the very distal pulmonary airways (Figure 5), but does not change significantly the overall deposition by diffusion. Gravitational settling increases by an order of magnitude, and its contribution to the total deposition becomes comparable to that of diffusion. This is mainly attributed to the decrease in the particle relaxation time, which promotes gravitational settling in the pulmonary region. Overall, predictions of CSP deposition by the L model-variant show significant shift Figure 5. Deposition profile by mechanism. CMD = 0.25 µm, GSD = 1.3, 2b0 = 4000 µm, k = 1. 524 D. M. BRODAY AND R. ROBINSON (a) (b) Figure 6. Deposition profile of CSP with a dynamically changing size distribution. Initial parameters: CMD = 0.25 µm, GSD = 1.3, k = 1, (a) 2b0 = 4000 µm, (b) 2b0 = 7695 µm. CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES Table 4 Deposition predictions for unstable and stable CSP behavior Cloud model No cloud effect (model S) Cloud behavior (model L) Cloud behavior, hygroscopicity, and coagulation (model LHC) Total (%) Tracheobronchial (%) Pulmonary (%) 39 4 35 62 40 22 78 66 12 Cloud diameter 2b0 = 4000 µm, size change parameter k = 1. from distal diffusional deposition (model S) to increased proximal deposition and suppressed deposition in the distal airway generations (Table 4). Effect of Dynamic Size Distribution. As CSP move along the respiratory tract the fine particles undergo coagulation and hygroscopic growth. The decreasing number concentration due to coagulation and deposition reduces the coagulation rate and weakens the colligative cloud effect, promoting single particle dynamics. On the other hand, hygroscopic growth promotes cloud behavior by increasing the volume fraction. The effect of the dynamic size distribution on the deposition profile is demonstrated in Figure 6a. Cloud behavior (model L with initial cloud size of 4000 µm and k = 1) increases CSP deposition in the TB region by 36% over the “no cloud” (S) model (Table 4). Since fewer particles reach the lower airways, deposition in the pulmonary region decreases. The net increase in the total deposition due to the cloud behavior (model L versus model S) is 23%. Accounting for hygroscopicity and coagulation (model LHC) further increases deposition in the TB region by another 26% over model L. Pulmonary deposition further decreases, and the net deposition increases (Table 4). The increased deposition in the LHC model over model L is due mainly to the combination of hygroscopic growth and cloud behavior. Hygroscopic growth of smoke particles occurs only in the trachea, since the particles reach equilibrium size in <0.1 s (Robinson and Yu 1998; Broday and Georgopoulos 2001). This has the effect of changing the initial size distribution of CSP entering the respiratory tract. Thus, although hygroscopic growth does not change the number concentration of CSP, the particle volume fraction increases from about 10−5 in model L to ∼10−4 in the combined LHC model. This increase in φ results in a significant increase in the intensity of the cloud behavior, enhancing interparticle screening. The increased deposition in the TB region is consistent with in vivo regional deposition measurements in human subjects (Pritchard and Black 1984; Hicks et al. 1986), and with in vitro regional deposition in hollow cast models (Ermala and Holsti 1955; Martonen et al. 1987). 525 The different cloud model (“solid sphere”) employed by Robinson and Yu (2001) results in a completely different deposition profile, as seen in Figure 6b. Although Robinson and Yu’s cloud model increased the overall deposition in the lungs, most of the CSP still deposited in the periphery. For example, while Robinson and Yu (2001) reported CSP deposition of 16.5% (TB) and 53.7% (P) for a CSP cloud with an initial size of 7695 µm (their notation was dc = 1/2dx ), Figure 6b depicts 88.6% deposition in the tracheobronchial airways and <0.2% deposition in the pulmonary region. It is noteworthy that these results are referred to here for the mere reason of comparing the two models, since Robinson and Yu considered initial cloud sizes larger than the glottis aperture, and thus unlikely. CONCLUSIONS Contrary to previous models, where bimodal cloud settling was considered, Brinkman’s effective medium approach regards the cloud as a porous medium and accounts for weak hydrodynamic interactions among the particles constituting it. The main features of the model are that the viscosity of the medium is taken identical to that of the surrounding air and the permeability of the cloud is finite and changes according to its solid volume fraction. The finite permeability allows air to pass through the cloud as well as around it, yet Brinkman’s model does not support the development of internal circulation. Only very dense CSP clouds settle like fluid spheres, unmixing with the outer air. Within dilute small clouds particles settle almost in isolation, being only weakly affected by the presence of nearby similar particles. Within denser and/or larger clouds, a non-negligible hydrodynamic screening affects the particle mobility, altering the deposition profile as a result of modifications introduced to the deposition efficiencies of all three major deposition mechanisms. Model results compare favorably with data available on CSP deposition in the human airways and in replica casts. The model predicts that CSP deposition is significantly influenced by the details of cloud formation, deformation, and disintegration. These processes are simulated rather simplistically at present. Much work is still needed to characterize these processes in vivo, parameterize them, and study their effect on the CSP deposition profile. Nonetheless, the model presented here is superior over previous models because it examines the effect of particle crowding on various processes (coagulation, growth, and deposition) simultaneously, and because it implements particle-particle screening effects in a more realistic way. In particular, the present cloud model shows a relatively smooth transition between single particle and cloud behavior. Model results indicate that a combination of cloud behavior, hygroscopic growth, and coagulation may explain the preferential deposition of cigarette smoke particles in the TB region in spite of their smallness. REFERENCES Arachi, S. (1999). Settling of an Aerosol Cloud Under Gravity with Wall and Diffusion Effects, Ph.D. dissertation, SUNY, Buffalo, New York. 526 D. M. BRODAY AND R. ROBINSON Batchelor, G. K. (1967). An Introduction to Fluid Dynamics, Cambridge University Press, Cambridge. Brady, J. F., and Bosis, G. (1998). Stokesian Dynamics, Ann. Rev. Fluid Mech. 20:111–157. Brenner, M. P. (1999) Screening Mechanisms in Sedimentation, Phys. Fluids 11:754–772. Brinkman, H. C. (1947). Proc. K. Ned. Akad. Wet. (Amsterdam) 50, p. 618, erratum p. 821. Broday, D. (1996). Motion and Deposition of Elongated Particles in Clean Rooms, D.Sc. dissertation, Technion, Israel. Broday, D. M. (2000). Diffusion of Clusters of Transmembrane Proteins as a Model of Focal Adhesion Remodeling, Bull. Math. Biol. 62(5):891–924. Broday, D. M. (2002). Translation of a Sphere Near the Interface Between Two Brinkman Effective Media, Bull. Math. Biol. 64(3):531–563. Broday, D., Fichman, M., Shapiro, M., and Gutfinger, C. (1998). Motion of Spheroidal Particles in Viscous Vertical Shear Flows, Phys. Fluids 10(1):86– 100. Broday D. M., and Georgopoulos P. G. (2001). Growth and Deposition of Respirable Hygroscopic Particulate Matter in the Human Lungs, Aerosol Sci. Technol. 34(1):144–159. Chan, T. L., and Yu, C. P. (1982). Charge Effects on Particle Deposition in the Human Tracheobronchial Tree, Ann. Occup. Hyg. 26:65–75. Churg, A., Sun, J. P., and Zay, K. (1998). Cigarette Smoke Increases Amosite Asbestos Fiber Binding to the Surface of Tracheal Epithelial Cells, Am. J. Physiol. Lung Cell Mol. Physiol. 19(3):L502–L508. Churg, A., and Vedal, S. (1996). Carinal and Tubular Airway Particle Concentrations in the Large Airways of Non-smokers in the General Population: Evidence for High Particle Concentration at Airway Carinas, Occup. Env. Med. 53(8):553–558. Churg, A., Wright, J. L., Hobson, J., and Stevens, B. (1992). Effects of Cigarette Smoke on the Clearance of Short Asbestos Fibers from the Lung and a Comparison with the Clearance of Long Asbestos Fibers, Int. J. Exp. Path. 73(3):287–297. Clift, R., Grace, J. R., and Weber, M. E. (1978). Bubbles, Dropes, and Particles, Academic Press, San Diego, CA. Davis, A. M. (2001). Axisymmetric Flow Due to a Porous Sphere Sedimenting Toward a Solid Sphere or a Solid Wall: Application to Scavenging of Small Particles, Phys. Fluids 13(11):3126–3133. Davis, R. H., and Stone, H. A. (1993). Flow Through Beds of Porous Particles, Chem. Engng. Sci. 48(23):3993–4005. Dodd, T. L., Hammer, D. A., Sangani, A. S., and Koch, D. L. (1995). Numerical Simulations of the Effect of Hydrodynamic Interactions on Diffusivities of Integral Membrane Proteins, J. Fluid Mech. 293:147–180. Durlofsky, L. J., and Brady, J. F. (1989). Dynamics Simulations of Bounded Suspensions of Hydrodynamically Interacting Particles, J. Fluid Mech. 200:39–67. Ellett, W., and Nelson, N. S. (1985). Epidemiology and Risk Assessment: Testing Models for Radon-induced Lung Cancer. In Indoor Air and Human, R. B. Gammage and S. V. Kaye, eds., Lewis Publishing, Chelsea, pp. 79–107. Ermala, P., and Holsti, L. R. (1955). Distribution and Absorption of Tobacco Tar in the Organs of the Respiratory Tract, Cancer 8:673–678. Finch, G. L., Lundgren, D. L., Barr, E. B., Chen, B. T., Griffith, W. C., Hobbs, C. H., Hoover, M. D., Nikula, K. J., and Mauderly, J. L. (1998). Chronic Cigarette Smoke Exposure Increases the Pulmonary Retention and Radiation Dose of Pu-239 Inhaled as (PuO2)-Pu-239 by F344 Rats, Health Phys. 75(6):597–609. Friedlander, S. K. (1977). Smoke, Dust and Haze, John Wiley & Sons, New York. Goldman, A. J., Cox, R. G., and Brenner, H. (1967a). Slow Viscous Motion of a Sphere Parallel to a Plane Wall. I. Motion Through a Quiescent Fluid, Chem. Engng. Sci. 22:637–652. Goldman, A. J., Cox, R. G., and Brenner, H. (1967b). Slow Viscous Motion of a Sphere Parallel to a Plane Wall. II. Couette Flow, Chem. Engng. Sci. 22:653–660. Goldsmith, H. L., and Mason, S. G. (1962). The Flow of Suspensions Through Tubes. I. Single Spheres, Rods, and Disks, J. Colloid Sci. 7:448–476. Han, M. S., Kim, C., Kim, M., and Lee, S. (1999). Particle Migration in Tube Flow of Suspension, J. Rheol. 43:1157–1174. Happel, J., and Brenner, H. (1973). Low Reynolds Number Hydrodynamics, Prentice-Hall, Englewood Cliffs, NJ. Hicks, J. F., Pritchard, J. N., Black, A., and Megaw, W. J. (1986). Experimental Evaluation of Aerosol Growth in the Human Respiratory Tract. In Aerosols: Formation and Reactivity, 2nd Int. Aerosol Conf. Berlin, Pergamon Journals Ltd., Oxford, UK, pp. 244–247. Hinds, W. C. (1999). Aerosol Technology: Properties, Behavior and Measurement of Airborne Particles, John Wiley & Sons, New York. Hinds, W. C., First, M. W., Huber, G. L., and Shea, J. W. (1983). A Method for Measuring Respiratory Deposition of Cigarette Smoke During Smoking, Am. Ind. Hyg. Assoc. J. 44:113–118. Hofmann, W. (1996). Modeling Techniques for Inhaled Particle Deposition: The State of The Art, J. Aerosol Med. 9(3):369–388. Hoffmann, D., and Hoffmann, I. (1995). Tobacco Consumption and Lung Cancer. In Lung Cancer: Advances in Basic and Clinical Research, H. Hansen, ed., Kluwer Academic, Boston, pp. 1–42. Howells, I. D. (1974). Drag Due to the Motion of a Newtonian Fluid Through a Sparse Random Array of Small Fixed Rigid Objects, J. Fluid Mech. 64:449– 475. Ingebrethsen, B. J. (1989). The Physical Properties of Mainstream Cigarette Smoke and Their Relationship to Deposition in the Respiratory Tract. In Extrapolation of Dosimetric Relationships for Inhaled Particles and Gases, Academic Press, San Diego, CA. Ingham, D. B. (1975). Diffusion of Aerosols from a Stream Flowing Through a Cylindrical Tube, J. Aerosol Sci. 6:123–132. Jackson, G. W., and James, D. F. (1986). The Permeability of Fibrous Porous Media, Can. J. Chem. Eng. 64:364–374. James, D. F., and Davis, A. M. J. (2001). Flow at the Interface of a Model Fibrous Porous Medium, J. Fluid Mech. 426:47–72. Jenkins, R. W. Jr., Francis, R. W., Flachsbart, H., and Stober, W. (1979). Chemical Variability of Mainstream Cigarette Smoke as a Function of Aerodynamic Particle Size, J. Aerosol Sci. 10:355–362. Keeling, B., Hobson, J., and Churg, A. (1993). Effects of Cigarette Smoke on Epithelial Uptake of Nonasbestos Mineral Particles in Tracheal Organ Culture, Am. J. Respir. Cell Mol. Biol. 9(3):335–340. Keith, C. H. (1982). Particle Size Studies on Tobacco Smoke, Beitr. zur Tabakforschung 11(3):123–131. Kim, S., and Russel, W. B. (1985). The Hydrodynamic Interactions Between Two Spheres in a Brinkman Medium, J. Fluid Mech. 154:253– 268. Koh, C. H., and Leal, L. G. (1989). The Stability of Drop Shapes for Translation at Zero Reynolds Number Through Quiescent Fluid, Phys. Fluids A 1:1309– 1313. Koh, C. J., and Leal, L. G. (1990). An Experimental Investigation on the Stability of Viscous Drops Translating Through a Quiescent Fluid, Phys. Fluids A 2:2103–2109. Kojima, M., Hinch, E. J., and Acrivos, A. (1984). The Formation and Expansion of a Toroidal Drop Moving in a Viscous Fluid, Phys. Fluids 27: 19–32. Kousaka, Y., Okuyama, K., and Wang, C. (1982). Response of Cigarette Smoke Particles to Change in Humidity, J. Chem. Eng. Jap. 15:75–76. Machu, G., Meile, W., Nitsche, L. C., and Schaflinger, U. (2001). Coalescence, Torus Formation, and Breakup of Sedimenting Drops: Experiments and Computer Simulations, J. Fluid Mech. 447:299–336. Martonen, T. B. (1992). Deposition Patterns of Cigarette Smoke in Human Airways, Am. Ind. Hyg. Assoc. J. 53:6–18. Martonen, T. B., Hoffmann, W., and Lowe, J. E. (1987). Cigarette Smoke and Lung Cancer, Health Physics 52(2):213–217. Martonen, T. B., and Musante, C. J. (2000). Importance of Cloud Motion of Cigarette Smoke Deposition in the Lung, Inhalation Toxicology 12(Suppl. 4): 261–280. McCusker, K., Hiller, C., Mazumder, M., and Bone, R. (1981). Dynamic Growth of Cigarette Smoke Particles, Chest 80(3):349. CLOUD DYNAMICS OF CIGARETTE SMOKE PARTICLES Muller, W., Hess, G. D., and Scherer, P. W. (1990). A Model of Cigarette Smoke Particle Deposition, Am. Ind. Hyg. Assoc. J. 51:245–256. Neal, G., Epstein, N., and Nader, W. (1973). Creeping Flow Relative to Permeable Spheres, Chem. Engng. Sci. 28:1865–1874. Nitsche, J. M., and Batchelor, G. K. (1997). Break-up of a Falling Drop Containing Dispersed Particles, J. Fluid Mech. 340:161–175. Nitsche, L. C., and Schaflinger, U. (2001). A Swarm of Stokeslets with Interfacial Tension, Phys. Fluids 13(6):1549–1553. Phalen, R. F., Oldham, M. J., and Mannix, R. C. (1994). Cigarette Smoke Deposition in the Tracheobronchial Tree: Evidence for Colligative Effects, Aerosol Sci. Technol. 20:215–226. Pich, J. (1972). Theories of Gravitational Deposition of Particles from Laminar Flows in Channel, J. Aerosol Sci. 3:351–361. Pritchard, J. N., and Black, A. (1984). An Estimation of the Tar Particulate Material Depositing in the Respiratory Tracts of Healthy Male Middle- and Low-tar Cigarette Smokers, In Aerosols, C. Liu, D. Pui, and H. Fissan, eds., Elsevier Science, New York, pp. 989–992. Pozrikidis, C. (1990). The Instability of a Moving Viscous Drop, J. Fluid Mech. 210:1–21. Robinson, R. (1998). Deposition of Cigarette Smoke Particles in the Human Respiratory Tract, Ph.D. dissertation, SUNY, Buffalo, New York. Robinson, R., and Yu, C. P. (1998). Theoretical Analysis of Hygroscopic Growth Rate of Mainstream and Sidestream Cigarette Smoke Particles in the Human Respiratory Tract, Aerosol Sci. Technol. 28:21–32. Robinson, R., and Yu, C. P. (1999). Coagulation of Cigarette Smoke Particles, J. Aerosol Sci. 30(4):533–548. Robinson, R. J., and Yu, C. P. (2001). Deposition of Cigarette Smoke Particles in the Human Respiratory Tract, Aerosol Sci. Tech. 34:202–215. 527 Sangani, S.A., and Mo, G. (1994). Inclusion of Lubrication Forces in Dynamic Simulations, Phys. Fluids 6:1653–1662. Sangani, S. A., and Yao, C. (1988a). Transport Processes in Random Arrays of Cylinders. I Thermal Conduction, Phys. Fluids 31:2426–2434. Sangani, S. A., and Yao, C. (1988b). Transport Processes in Random Arrays of Cylinders. II Viscous Flow, Phys. Fluids 31:2435–2444. Schaflinger, U., and Machu, G. (1999). Interfacial Phenomena in Suspensions, Chem. Eng. Technol. 22:617–619. Slack, G. W. (1963a). Sedimentation of a Large Number of Particles as a Cluster in Air, Nature 200:1806. Slack, G. W. (1963b). Sedimentation of Compact Clusters of Uniform Spheres, Nature 200:466–467. Task group on Lung Dynamics. (1966). Deposition and Retention Models for Internal Dosimetry of the Human Respiratory Tract, Health Physics 12:173– 207. US EPA. (1993). Respiratory Health Effects of Passive Smoking: Lung Cancer and Other Disorders. Technical report no. EPA/600/6-90/006 F, US Environmental Protection Agency, Research Triangle Park, NC. Yang, C. P., Gallagher, R. P., Weiss, N. S., Band, P. R., Thomas, D. B., and Russel, D. A. (1989). Differences in Incidence Rates of Cancers of the Respiratory Tract by Anatomic Subsite and Histologic Type: An Etiologic Implication, J. National Cancer Institute 81(21):1828–1831. Yu, C. P. (1978). Exact Analysis of Aerosol Deposition During Steady Breathing, Powder Tech. 21:55–62. Yu, C. P., and Diu, C. K. (1983). Total and Regional Deposition of Inhaled Aerosols in Humans, J. Aerosol Sci. 14:599–609. Zhang, L., Asgharian, B., and Anjilvel, S. (1997). Inertial Deposition of Particles in the Human Upper Airway Bifurcations, Aerosol Sci. Technol. 26:97–110.
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