Week 13 - Control of Air Pollution
Natural Cleansing of the Atmosphere
Physical characteristics - influence natural removal mechanisms
Very small particles - bounce around randomly, collide, coagulate, and fall out as large particles
Particles with an electrical charge - grow by attracting particles of opposite charge
Small particles - act as nuclei within a raindrop
Raindrops - collide with particles which adhere to the surface of the drop and fall out
Air Quality Control
Objective: Maintain an atmosphere in which pollutants have no negative impact on human activities
Best way: Don't produce the pollutants to begin with
Example: Eliminate lead emissions by burning unleaded fuels
Alternative: Add-on devices
Example: Automobiles use carbon canisters to absorb hydrocarbons emitted from the carburetor and gas tank
Catalytic converters chemically reduce hydrocarbon emissions
Other add-ons: Scrubbers and bag houses used in industrial applications
Dispersion: Used to control local air quality
Shift emissions to tall stacks which allow more time to disperse before reaching the ground
Less desirable than pollution elimination or add-on alternatives
Example: Electric heating
Shifts the emissions from short residential stacks to tall utility stacks in remote areas
Particle Emission Control
Equipment must handle solid and liquid particles
Size: 1 µm to larger than 100 µm
Smaller particles - much harder to collect
Gravitational Settling Chambers
Simple, inexpensive collectors
Use the laws of gravity to settle the particles
Simple duct that expands, forcing the horizontal velocity to slow to allow time for the particles to settle
Forces acting on the particle
Horizontal viscous force is negligible
Particle moves at the horizontal velocity of the gas stream
Simple gravitational settling chamber
Efficiency of the settling chamber
SUB g=1-exp[-{gd SUB p SUP 2 SUB p L} OVER {18µuH}]
SUB g=1-exp[-{u SUB t L} OVER {uH}]
Where:
g = efficiency of removal (fraction)
L = Length of the collector, m
H = Depth of the collector, m
u = horizontal velocity of the gas and particles through the collector, m/sec
ut = terminal settling velocity of the particles, m/sec
dp = diameter of the particle, m
d = density of the particle, kg/m3
g = gravitational constant, m2/sec
µ = dynamic viscosity, kg/m-s
Example: Estimate the 50 percent cutoff diameter for particles of CaO suspended in an airstream at 100oC and at atmospheric pressure for a gravitational settling chamber 3 m long and 1 m high when the gas velocity in the collector is 1 m/sec.
p for CaO = 3310 kg/m3
µ for air = 2.17x10-5kg/m-s (@100oC)
Note: The 50% cutoff diameter is defined as the particle diameter at which the efficiency is 50%.
SUB g = 0.5 = 1-exp[-{gd SUB p SUP 2 SUB p L} OVER{18µuH } ]
0.5=exp[-{9.81x3310x3xd SUB p SUP 2} OVER {18x2.17x10 SUP {-5}}]
d SUB p SUP 2=ln(0.5)x[-{18x2.17x10 SUP{-5}} OVER {9.81x3310x3}]
d SUB p = 53µm
d SUB p SUP 2=28x10 SUP {-10}m SUP 2
Note: The cutoff diameter is not sharp
In practice, particles larger and smaller will be collected due to turbulence and flow variations
Inertial Collectors
Rely on centrifugal forces to separate the heavier particles from the lighter gas molecules
Two types - Skimmers and Cyclones
Skimmers - increase the particle concentration in a separated gas stream - remove particles by cyclones or settling chambers
Cyclones
- Particle laden gases enter tangentially
- Forced in a downward spiral motion
- Particles migrate outside
- Gases forced back up through center
Centrifugal particle skimmer and cyclone
Magnitude of the centrifugal force
F SUB c = m SUB p {u SUB T SUP 2} OVER r = { d SUB p SUP 3} OVER 6 SUB p {u SUB T SUP 2} OVER r
Where: mp = mass of the particle
uT = tangential velocity
r = radius of curvature
p = density of the particle
dp = diameter of the particle
Removal efficiency varies:
directly with diameter cubed
directly with density
directly with the square of the velocity
inversely with the radius
Cyclones with large r: traditional
Cyclones with r < 7.5 cm: high eff.
Uses for inertial and gravitational settlers
May be fabricated using metals that can withstand high temperatures and resist corrosion
Effective for solid or liquid particles
Wet collectors
Also called scrubbers
Designed to increase particle sizes using water or slurry droplets, because larger particles are easier to collect
Many different types (look at 2, conventional and venturi scrubbers)
Sketch of an absorber or scrubber
Absorber or scrubber
Upper part of tower - water droplets collide with and collect particles from the upward-flowing gases
Packed section of tower - special shapes are added to increase the area of contact between the liquid and aerosol (gas + particles)
Below the packed section - flooded perforated disc which supports several cm of water - allows contact between bubbles carrying particles and water
Below flooded disc - water drains through perforations to develop another falling-drop collector section
Absorber or scrubber (Continued)
Demister collects droplets that are left in the stream
Not every collision between water and particles results in collection - due to surface tension of droplet and particle wettability characteristics
Chemicals may be added to the water to reduce the surface tension OR to improve the ability of the particles to absorb gases in addition to particles
Liquid containing particles is collected at the bottom of the tower and pumped to a settling basin or filter
Liquid is recirculated to reduce makeup water and disposal water
Difference between a scrubber and an absorber
Absorber - designed primarily for gas removal
Scrubber - designed primarily for particle removal
Performance
Size of water drop is critical to performance of the scrubber
Water drops large relative to particle size - aerodynamic forces (drag) will displace the particles out of the path of the falling drops - number of collisions will decrease significantly
Performance (Continued)
Water drops same size as particles - collisions also decrease because drag causes the collecting liquid droplets to move with the gas stream and particles
Water drops a little larger or smaller than the particles - optimal
Scrubber must be well maintained to ensure that the correct droplet size is achieved
Performance also depends on the physical and chemical characteristics of the particles, the collecting liquid, and the final droplet collector (demister)
Venturi scrubbers
* Gases and particles accelerate in the throat followed by rapid deceleration as expansion occurs
* Liquid is injected into the throat - solid stream perpendicular to the gas flow
* Relative difference in velocity between gas and liquid tears apart the liquid and forms drops
* Particles collide and become entrained
* Some additional particle collection in the expansion section
* Droplets are removed as large particles as velocity decreases
Performance of Venturi meters
Critically dependent on the gas stream velocity and physical and chemical characteristics of the liquid and particles
Must operate at a constant gas flowrate if performance is to be maintained for a given particle size and concentration
Venturis have been designed in which throat area can be changed while device is operating
Pressure loss and efficiency
Absorbers and Scrubbers:
Pressure loss (conventional scrubbers) 15 - 40 cm of water
Efficiency increases with pressure loss and may be up to 95% for dp>5µm
Venturi scrubbers:
Pressure loss 50 - 200 cm of water
Efficiency as high as to 99% for dp>1µm
Fabric and fibrous mat collectors (baghouse collectors)
Similar to vacuum cleaners on a grand scale
Remove dry particles from low-temperature (0-275oC) gas streams
Cloth "socks" are suspended in a chamber and air is forced through
Socks
15 to 30 cm in diameter
Up to 10 m in length
Woven (most common) or made of felt
Fabric - cotton, synthetics, and fiberglass
Material selection - depends on gas and particle properties
Summary of data on the common filter media used in industrial baghouses
Fabric and fibrous mat collectors (Continued)
May be designed with multiple cells to allow for maintenance during operation
Cloth may have holes exceeding 100 µm across - collector will perform with 99%+ efficiency for particle diameters > 1µm
Small particles are trapped in the filter cake
As thickness of cake increases, power costs increase
If cake becomes too thick, pressure may collapse the cake and make it nonporous (moisture also)
Cleaning
Remove filter cake by shaking the bag in small collectors
Large collectors - reverse the flow of air
To avoid frequent shaking and to achieve an effective cake thickness - operate at a volume flowrate of 0.5 to 2 m3/sec per m2 of cloth
Pressure drops - 5 to 40 cm of water
Shaking periods - 4 to 5 per hour up to once in several hours
Bag life - 2 to 3 years
Electrostatic precipitators
Voltage difference (field strength) between the electrode and the collector plates is maintianed at as high a level as possible (but below spark-over)
Electrons are released and attach themselves to particles
Particles then migrate to grounded surface due to electrostatic forces
Electrostatic precipitators (Continued)
Efficiencies as high as 99% for particles > 2 µm at pressure losses of 5 cm of water or less
Units built of metal
Used extensively on processes that discharge:
corrosive gases
elevated temperatures
very large volumes
high percentage of particles >1 µm
Fire and explosion hazard - particularly because of the danger of ignition by spark-overs
Gas emission control
Four fundamental ways to reduce emission of undesirable gases:
1. Reduce or eliminate the production of undesirable gases
2. Induce the gases to react after production in chemical processes to produce different, less objectionable emissions
3. Selectively remove the undesirable product from a gas stream by aborsorption, which is the transfer of gas molecules into a liquid
4. Selectively remove the undesirable gas by adsorption, which is deposition of gas molecules on a solid surface
Adsorption
Pass gases through through beds of solid adsorptive material
Amount of adsorbate which a solid can take up is a function of the chemical and physical properties
Activated carbon and activated alumina are excellent adsorbants for several gases
Silica gel is a good adsorbant for water vapor and other selected gases
Surface area
Activated carbon: 500-1,500 m2 per g
Silica gel: 175 m2 per g
Regenerated using hot steam
Adsorptive capacity of activated carbon
Substance
|
Adsorptive capacity weight (%)
|
Carbon tetrachloride
|
80-110
|
Gasoline
|
10-20
|
Methanol
|
50
|
Comparison of Air Pollution Control Equipment
Source: Handbook of Environmental Management and Technology, Chapter 8, G. Holmes, B. Singh, and L. Theodore, John Wiley and Sons, Inc., 1993.
USE 455/555 - Class 12
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