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* Khan Alam &  ** Hussain Majid *Department of Geography and Geology,  University of Salzburg **Department of Bio-Physics University of Salzburg  Measurement of aerosol size distribution, PM concentration and lung deposition calculation at different cities of Pakistan
Part 1 ,[object Object]
The part will cover ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Introduction ,[object Object],[object Object],[object Object],[object Object]
Aerosol???? ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Over 4000 species in gaseous, vapour and particle form are emitted from motor vehicle exhaust NO HC CO 2 CO SO 2 Dust Smoke Fume Mist Clouds Pesticides
Effects of aerosols on climate ,[object Object],[object Object],[object Object]
Direct radiative forcing by aerosols (Direct effect) Solar radiation absorbed (Warming) Solar radiation scattered to space (Cooling) Absorbing  aerosols Scattering  aerosols  e.g. Black carbon, mineral dust e.g. Sulphates, nitrates, organics Most aerosols both absorb and scatter!
Indirect aerosol effect (I) Few aerosols Low droplet concentration Less reflective cloud Numerous aerosols High droplet concentration More reflective cloud (Cooler climate)
Indirect aerosol effect (II) Smaller droplets  Lower Precipitation rate Clouds are longer lived and  retain higher liquid water content
The semi-direct aerosol effect ,[object Object],[object Object],[object Object],Absorbing aerosols in and around a cloud ,[object Object],[object Object]
Classification of Particle Sizes ,[object Object],[object Object],[object Object],[object Object],[object Object]
Formation mechanisms of Aerosol particles ,[object Object],[object Object],[object Object],[object Object]
Standards for particulate matter ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Sampling sites ,[object Object],[object Object],[object Object]
Instrumentation  ,[object Object],[object Object],[object Object],[object Object],[object Object]
Method ,[object Object],[object Object],[object Object]
Cont. Method ,[object Object],[object Object],[object Object]
Results
Particle number and mass size distributions
Mass variation in different cities
PM concentrations
Particulate matter concentration Min.= minimum, Max.= maximum, Avg.= average   No Site TSP(µg/m 3  ) PM 10 (µg/m 3  ) PM 2.5 (µg/m 3  ) PM 1.0 (µg/m 3  ) Min. Max. Avg. Min. Max. Avg. Min Max. Avg. Min. Max. Avg. 1. Peshawar 3467 92399 21924 119 1751 618 38 337 189 28 281 129 2. Rawalpindi 6907 82461 27131 216 1037 489 70 300 159 45 261 121 3 Lahore 3482 23896 6759 146 284 204 64 98 76 47 60 52 4. Karachi Suparco 2372 11508 5941 126 399 270 51 289 151 32 216 114 Saddar 5522 38765 14438 284 860 462 115 320 197 79 267 155 Sea View 794 11223 2308 74 127 93 51 84 64 33 48 38
Chemical Analysis Site Al Ca Cu Fe K Mg Na S Si Zn B Ba Cr Mn Ni P Sr Ti Zr Peshawar 7385 34569 688 8650 2676 4044 5314 2650 3062 1454 20 48 556 199 561 365 110 205 75 Pindi 10766 74955 4984 15026 7437 5981 13249 4413 21809 5032 155 152 787 375 1475 958 296 580 93 Lahore 9521 20675 657 8244 2866 3233 5531 5420 3323 1637 50 100 218 205 360 414 72 207 32 Karachi Suparco 4188 13442 273 3390 1211 1241 2384 2683 1486 757 7 27 156 96 230 133 47 75 11 Saddar 19916 74385 1146 16867 8574 7299 17839 9045 7547 2834 78 180 501 471 545 1557 243 527 42 Sea View 5571 17954 938 7344 1995 2589 11252 5469 1022 1638 21 79 616 162 474 248 58 103 23
WHO AIR QUALITY GUIDELINES 2000 Compound Guideline [ u g   m -3 ]     Averaging Time Carbon monoxide 100 000 15 min   60 000 30 min   30 000 1 hour   10 000 8 hours Nitrogen dioxide   200 1 hour   40  1 year Ozone     120 8 hours Sulphur dioxide   500 10 min   125 24 hours   50 1 year Lead   0.5 1 year 2006 100 20
 
EFFECTS OF AIRBORNE POLLUTANTS ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Health effects of airborne pollutants ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Health effects of selected contaminants ,[object Object],[object Object],[object Object],[object Object],[object Object]
Conclusion ,[object Object],[object Object],[object Object],[object Object],[object Object]
Part 2 ,[object Object]
The part will cover ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Why is this important? ,[object Object],[object Object],[object Object],[object Object]
Tracheaobronchial (TB) Trachea direct air into the lung Bronchial tree is the first part of the lung. This part directs air in the lung Each branch in the tree split into 2 part Bronchial tree can be divide into 5 segment that use to characterize the lung airway Head airway (HA) Air and aerosol enter from here and used to remove dust and other particles from entering the respiratory Humidify the air before entering the lung Separate out food to digestive system Human lung structure Parent Branch Major daughter Minor daughter Bifurcation Trachea Bronchial Tree Mouth Pharynx Larynx Nose
Alveolar or Pulmonary (AV) Alveoli are located at the end of the bronchial tree Gas exchange occur at the Alveoli If particle deposit in this region it can directly enter the blood stream alveoli Alveolar duct Alveolar entrance rings 100µm 100µm Alveoli
Airway Generation ,[object Object],[object Object],[object Object],Modelling and Simulation of Particle Deposition in the Human Lung
Deposition Mechanisms Involved Major: Minor: Diffusion Sedimentation Impaction Interception Electrostatic Naso-pharyngeal:   impaction, sedimentation, electrostatic  (particles > 1 μm) Tracheo-bronchial:  impaction, sedimentation, diffusion (particles < 1 μm) Pulmonary: sedimentation, diffusion (particles < 0.1 μm)
Diffusion Cause by Brownian motion Diffusion is the deposition mechanism for small particles. Diffusion depends increases with decreasing particle size and flow rate. More deposition occurs in the alveoli region because longer residence time and smaller airway.
Sedimentation ,[object Object],[object Object],[object Object],Force Force
Impaction Particle cannot follow the trajectory due to its inertia and hit the wall called impaction. Impaction increases with particle size and flow rate.  This type of deposition occur through out the lung.  This is important, especially in the head airway where most of the large particles are screened out Impaction occurs mostly in the upper generation airways due to high velocity
Factors that Effect Deposition ,[object Object],[object Object],[object Object],Size distribution (MMD, AMD. Etc) Concentration Particle hygroscopicity Gas particle interaction Chemical reaction Particle surface charge Lung structure and morphology Model uses: Weibel, Raabe, and Horsfield  Lung capacity Breathing frequency Tidal Volume
Particle Clearance ,[object Object],[object Object],Particle Clearance mechanisms : The  Naso-pharyngeal  Compartment: •  mucociliary clearance (transport back to nasopharynx ) •  mechanical clearance (sneezing, coughing, swallowing) •  absorption into circulation (soluble particles). The  Tracheo-bronchial  Compartment: •  mucociliary clearance (transport to oropharynx) •  endocytosis into peribronchial region (insoluble particles) •  absorption into circulation (soluble particles) The  Pulmonary  Compartment: •  alveolar macrophage mediated clearance •  endocytosis by lung epithelial cells into interstitum •  absorption into circulation (soluble particles)
Stochastic Lung Model ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Deposition patterns of 0.25-10 µm particles under light exercise breathing condition  (V T  = 500 mL, t = 4s) for three different days at Karachi, Sadar near a road crossing Deposition is normalized to the number of particles entering the trachea. Particle deposition in lung
Deposition patterns of 0.25-10 µm particles under light exercise breathing condition  (V T  = 500 mL, t = 4s) for two different days at Rawalpindi, near a road crossing Deposition is normalized to the number of particles entering the trachea. Particle deposition in lung (cont..)
Conclusions ,[object Object],[object Object],[object Object]
Thank You

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Measurement of aerosol size distribution, PM concentration and lung deposition calculation at different cities of Pakistan

  • 1. * Khan Alam & ** Hussain Majid *Department of Geography and Geology, University of Salzburg **Department of Bio-Physics University of Salzburg Measurement of aerosol size distribution, PM concentration and lung deposition calculation at different cities of Pakistan
  • 2.
  • 3.
  • 4.
  • 5.
  • 6.
  • 7. Direct radiative forcing by aerosols (Direct effect) Solar radiation absorbed (Warming) Solar radiation scattered to space (Cooling) Absorbing aerosols Scattering aerosols e.g. Black carbon, mineral dust e.g. Sulphates, nitrates, organics Most aerosols both absorb and scatter!
  • 8. Indirect aerosol effect (I) Few aerosols Low droplet concentration Less reflective cloud Numerous aerosols High droplet concentration More reflective cloud (Cooler climate)
  • 9. Indirect aerosol effect (II) Smaller droplets Lower Precipitation rate Clouds are longer lived and retain higher liquid water content
  • 10.
  • 11.
  • 12.
  • 13.
  • 14.
  • 15.
  • 16.
  • 17.
  • 19. Particle number and mass size distributions
  • 20. Mass variation in different cities
  • 22. Particulate matter concentration Min.= minimum, Max.= maximum, Avg.= average No Site TSP(µg/m 3 ) PM 10 (µg/m 3 ) PM 2.5 (µg/m 3 ) PM 1.0 (µg/m 3 ) Min. Max. Avg. Min. Max. Avg. Min Max. Avg. Min. Max. Avg. 1. Peshawar 3467 92399 21924 119 1751 618 38 337 189 28 281 129 2. Rawalpindi 6907 82461 27131 216 1037 489 70 300 159 45 261 121 3 Lahore 3482 23896 6759 146 284 204 64 98 76 47 60 52 4. Karachi Suparco 2372 11508 5941 126 399 270 51 289 151 32 216 114 Saddar 5522 38765 14438 284 860 462 115 320 197 79 267 155 Sea View 794 11223 2308 74 127 93 51 84 64 33 48 38
  • 23. Chemical Analysis Site Al Ca Cu Fe K Mg Na S Si Zn B Ba Cr Mn Ni P Sr Ti Zr Peshawar 7385 34569 688 8650 2676 4044 5314 2650 3062 1454 20 48 556 199 561 365 110 205 75 Pindi 10766 74955 4984 15026 7437 5981 13249 4413 21809 5032 155 152 787 375 1475 958 296 580 93 Lahore 9521 20675 657 8244 2866 3233 5531 5420 3323 1637 50 100 218 205 360 414 72 207 32 Karachi Suparco 4188 13442 273 3390 1211 1241 2384 2683 1486 757 7 27 156 96 230 133 47 75 11 Saddar 19916 74385 1146 16867 8574 7299 17839 9045 7547 2834 78 180 501 471 545 1557 243 527 42 Sea View 5571 17954 938 7344 1995 2589 11252 5469 1022 1638 21 79 616 162 474 248 58 103 23
  • 24. WHO AIR QUALITY GUIDELINES 2000 Compound Guideline [ u g m -3 ] Averaging Time Carbon monoxide 100 000 15 min 60 000 30 min 30 000 1 hour 10 000 8 hours Nitrogen dioxide 200 1 hour 40 1 year Ozone 120 8 hours Sulphur dioxide 500 10 min 125 24 hours 50 1 year Lead 0.5 1 year 2006 100 20
  • 25.  
  • 26.
  • 27.
  • 28.
  • 29.
  • 30.
  • 31.
  • 32.
  • 33. Tracheaobronchial (TB) Trachea direct air into the lung Bronchial tree is the first part of the lung. This part directs air in the lung Each branch in the tree split into 2 part Bronchial tree can be divide into 5 segment that use to characterize the lung airway Head airway (HA) Air and aerosol enter from here and used to remove dust and other particles from entering the respiratory Humidify the air before entering the lung Separate out food to digestive system Human lung structure Parent Branch Major daughter Minor daughter Bifurcation Trachea Bronchial Tree Mouth Pharynx Larynx Nose
  • 34. Alveolar or Pulmonary (AV) Alveoli are located at the end of the bronchial tree Gas exchange occur at the Alveoli If particle deposit in this region it can directly enter the blood stream alveoli Alveolar duct Alveolar entrance rings 100µm 100µm Alveoli
  • 35.
  • 36. Deposition Mechanisms Involved Major: Minor: Diffusion Sedimentation Impaction Interception Electrostatic Naso-pharyngeal: impaction, sedimentation, electrostatic (particles > 1 μm) Tracheo-bronchial: impaction, sedimentation, diffusion (particles < 1 μm) Pulmonary: sedimentation, diffusion (particles < 0.1 μm)
  • 37. Diffusion Cause by Brownian motion Diffusion is the deposition mechanism for small particles. Diffusion depends increases with decreasing particle size and flow rate. More deposition occurs in the alveoli region because longer residence time and smaller airway.
  • 38.
  • 39. Impaction Particle cannot follow the trajectory due to its inertia and hit the wall called impaction. Impaction increases with particle size and flow rate. This type of deposition occur through out the lung. This is important, especially in the head airway where most of the large particles are screened out Impaction occurs mostly in the upper generation airways due to high velocity
  • 40.
  • 41.
  • 42.
  • 43. Deposition patterns of 0.25-10 µm particles under light exercise breathing condition (V T = 500 mL, t = 4s) for three different days at Karachi, Sadar near a road crossing Deposition is normalized to the number of particles entering the trachea. Particle deposition in lung
  • 44. Deposition patterns of 0.25-10 µm particles under light exercise breathing condition (V T = 500 mL, t = 4s) for two different days at Rawalpindi, near a road crossing Deposition is normalized to the number of particles entering the trachea. Particle deposition in lung (cont..)
  • 45.

Editor's Notes

  1. Trachea is also know as windpipe. Trachea and Bronchial are cover with a mucus layer that capture particle. The layer move upward and dispose of the particle into the digestive system.
  2. The flow in the alveolar is much lower than in bronchial so there will be more residence time