Air / Water Gas Exchange The distribution of a chemical across the air-water interface between the atmospheric gas phase and the water dissolved phase.

Slides:



Advertisements
Similar presentations
Heat Transfer in Fermentation
Advertisements

The removal of volatile contaminants from water and contaminated soils
Subsurface Fate and Transport of Contaminants
MAE 5310: COMBUSTION FUNDAMENTALS
Laminar Premixed Flames and Diffusion Flames
Ecotoxicology Transport of contaminants. The transport of contaminants in the atmosphere takes place: Globally Large-scale:> 1000 km Meso-scale:
ERT 313/4 BIOSEPARATION ENGINEERING MASS TRANSFER & ITS APPLICATIONS
Dept of Chemical and Biomolecular Engineering CN2125E Heat and Mass Transfer Dr. Tong Yen Wah, E , (Mass Transfer, Radiation)
Introduction to Mass Transfer
Chapter 2: Overall Heat Transfer Coefficient
Reading: Text, (p40-42, p49-60) Foken 2006 Key questions:
高等輸送二 — 質傳 Lecture 7 Fundamentals of Mass Transfer
Chapter 13 Set 2. Solute-Solvent Interaction Polar liquids tend to dissolve in polar solvents. Miscible liquids: mix in any proportions. Immiscible liquids:
Atmospheric Analysis Lecture 3.
Introduction to GW contamination and
Momentum flux across the sea surface
Divide yourselves into groups of three (3). Write your names and your complete solution into your answer sheet, and box / encircle your final answer.
Diffusion Diffusion means atoms moving and changing places. This happens in solids and liquids, exactly in the same way that an unpleasant smell moves.
Atmospheric Analysis Lecture 2.
Gas Exchange Week 4. Daltons Law The partial pressures of the 4 gases add up to 760mm Hg. Dalton’s Law; in a mixture if gases, the total pressure.
Lecture Diffusion, Osmosis and Osmotic Pressure.
External Gas Transport Chapters 20 & 21 Respiration The process of acquiring oxygen and releasing carbon dioxide.
* Reading Assignments:
Bioseparation Dr. Kamal E. M. Elkahlout Chapter 3 Mass transfer.
ADVANCED MASS TRANSFER
Gases Ch. 6 Chemistry II Milbank High School. Kinetic Molecular Theory All matter is composed of tiny, discrete particles called molecules They are in.
Scheme of the equilibrium Environmental Compartments Model.
Respiration I. Introduction Oxygen and Carbon Dioxide.
Evaporation Slides prepared by Daene C. McKinney and Venkatesh Merwade
Molecular Transport Equations. Outline 1.Molecular Transport Equations 2.Viscosity of Fluids 3.Fluid Flow.
Air-Surface Exchange of Persistent Substances by Michael McLachlan ITM, Stockholm University for the summer school The Advances.
Bio301 Overview of Topics Intro Bioprocessing – Biotechnology: Make money from bioprocesses Inputs are of lower value than outputs (products) Computer.
Chapter 39 Physical Principles of Gas Exchange
高等輸送二 — 質傳 Lecture 8 Forced convection
PM3125: Lectures 7 to 9 Content of Lectures 7 to 9:
Respiratory System Diffusion Xinping Yue Department of Physiology LSUHSC-NO.
R. Shanthini 31 July 2009 PM3125 Lectures 7 to 9 Lecture Content of Lectures 7 to 9: Mathematical problems on heat transfer Mass transfer: concept and.
Environmental Engineering Course Note 8 (Transport Processes II) Joonhong Park Yonsei CEE Department CEE3330 Y2013 WEEK3.
Where do these two models leave us? F = K ol * ( C w – C a / H) Whitman two film model un-measurable parameters: z w & z a Surface renewal model un-measurable.
Lesson 13 CONVECTION HEAT TRANSFER Given the formula for heat transfer and the operating conditions of the system, CALCULATE the rate of heat transfer.
Aquatic Respiration The gas exchange mechanisms in aquatic environments.
Transport You are on a train to NYC. You are stirring the milk into your coffee. The train and everything in it are moving toward NYC via directed or advective.
ERMSAR 2012, Cologne March 21 – 23, 2012 Experimental Determination and Analysis of Iodine Mass Transfer Coefficients from THAI Test Iod-23 K. FISCHER,
What Happens to Precipitation?
Evapotranspiration Eric Peterson GEO Hydrology.
Condensed States of Matter: Liquids and Solids Chapter 14
Kinetic Energy In The Atmosphere Kinetic Energy is the energy of motion Heat - the total kinetic energy of the atoms composing a substance (atmospheric.
Module 4b Absorbers. MCEN 4131/ Preliminaries VOC project assignment Project night this Thurs 5-6:30 Party Thurs Apr The Sink.
CVEN 5424 Environmental Organic Chemistry Lecture 8 – Henry’s Law Constant and Air-Water Exchange Kinetics.
GASES Chapters 13 and 14. Nature of Gases  Kinetic Molecular Theory (KMT)  Kinetic energy- the energy an object has because of its motion  According.
Dissolved oxygen (DO) in the streams
Derivation of Oxygen Diffusion Equations:
Heterogeneous Catalysis: Kinetics in Porous Catalyst Particles
3.3 Gas exchange Turbulent vertical motions in both the atmosphere and ocean are strongly suppressed near the air-sea interface.  STAGNANT FILM MODEL.
Mass Transfer transport of one constituent from a region of higher concentration to that of a lower concentration.
Reynolds Number (Re) Viscosity: resistance of a liquid to change of form. Inertia: resistance of an object (body) to a change in its state of motion.
Environmental Engineering Lecture Note Week 11 (Transport Processes)
Chemical Reaction Engineering (CRE) is the field that studies the rates and mechanisms of chemical reactions and the design of the reactors in which.
A First Course on Kinetics and Reaction Engineering
Air / Water Gas Exchange
Mass Transfer and Its Applications
Mass Transfer.
Review: Steps in a Heterogeneous Catalytic Reaction
Biopharmaceutics 4th year
Theories of Mass Transfer
Transport through cell membranes
Convective Heat Transfer
Gas Transfer (Diffusion of O2 and CO2)
Chemical Engineering Department
Movement in and out of cells
Presentation transcript:

Air / Water Gas Exchange The distribution of a chemical across the air-water interface between the atmospheric gas phase and the water dissolved phase Equilibrium transfer of organic chemical between Air and Water K H = P a /  w C w Appropriate for: Exchange between air and falling raindrop (over ~10 m fall) Low MW organic gases exchanging between peat water and bubbles (in wetlands and marshes) Confined headspace over a solution Sheltered systems with more or less constant water and atmospheric conditions Inappropriate for : Large Lakes Flowing rivers Spills in both rivers and lakes Oceans ( sometimes ! ) In these you must consider Mass Transport (absolute and net fluzes)

Processes of Air / Water Exchange Depiction of the physical processes responsible for the movement of chemicals through four zones spanning an intact “air-water” interface (i.e. no bubbles or aerosols). Figure from Schwarzenbach, Gschwend and Imboden, 1993

Processes of Air / Water Exchange “Little” Mixing: Stagnant, 2-film model “More” Mixing: surface renewal model Wave Breaking: intense gas transfer ( breaking bubbles) Figure from Schwarzenbach, Gschwend and Imboden, 1993

Stagnant Boundary Layer Model of Air / Water Exchange – Whitman Two Film Model Figure from Schwarzenbach, Gschwend and Imboden, 1993

Two Film Model Figure from Schwarzenbach, Gschwend and Imboden, 1993 Net Flux = K ol * (C w – C a /H*) resistance to transport * Concentration gradient relative to equilibrium H* is “dimesnionless” Henry’s Law Constant at ambient temperature 1/ K ol = ( 1/ K w + 1/ (K a H*) ) = (1 / D w / z w ) + (1/ D a / z a H*) where D w = diffusivity in water D a = diffusivity in air z w = water film thicknessz a = air film thickness un-measurable parameters: z w, z a

Two Film Model- Continued F w = - D w ( C w/a – C w ) / z w So, at steady state: F w = - D w ( C w/a – C w ) / z w = -D a (C a – C a/w ) / z a = F a Flux total = Fw = Fa since: K H ’ = C a/w / C w/a ( mol / L air / mol / L water ) then:D w (C w -C w/a ) / z w = D a (K H ’ C w/a - C a ) z a C w/a = ( ( D w / z w ) + ( D a / z a ) C a ) / ( ( D w / z w ) + ( D a K H ’ / z a ) ) F overall = 1 / ( z w / D w ) + (z a / D a K H ’) * ( C w - C a / K H ’) mass transfer coefficient (cm/hr) * Conc. gradient F net = (+) then water ====> air b/c (C w > C a / K H ’) F net = (-) then air ====> water b/c (C w < C a / K H ’)

Two Film Model- “Velocities” Flux total = v tot * ( C w – C a / K H ’) mol m -2 sec -1 = m sec -1 * mol m -3 Defining “Partial Transfer Velocities: v w = D w / z w &v a = D a / z a 1 / v tot = 1 / v w + 1 / v a K H ’ Resistance analogy: 1 / R tot = 1 / R w + 1 / R a Transfer dominated by layers: v w v tot ~= v w v w >> v a K H ’ ==> v tot ~= v a K H ’ 1 / v w ~=~ 1 / v a K H ’ ==> Both phases important

Steady State Flux Figure from Schwarzenbach, Gschwend and Imboden, 1993

Two Film Model- Important Factors z a & z w : higher turbulence (wind, flow ===> decreasing thickness) H: Temperature, Ionic Strength ( x 2-3 for every 10 o C) Surface films (surfactants) additional barrier & additional resistance. The time needed for average molecule to cross film / boundary layer:  w ~= z w 2 / D w = z w / v w  a ~= z a 2 / D a = z a / v a if: z w ~ 5x10-3 cm z a ~ 5 x 10-2 cm D w ~10-5 cm s -1 D a ~ 0.1 cm s -1 then, diffusion times ~ seconds  a-w exchange is rapid ( & increased with greater turbulence)

Film Resistance in Whitman Model Flux = v tot (C w – C*) where C* = Ca / K H 1/ v tot = 1 / v w + RT / H v a ( k ol ) ( k w ) ( k a ) Compounds exhibiting liquid phase resistance: O 2, CO 2 k w = 2-10 cm hr -1 Compounds exhibiting gas phase resistance: H 2 0k a = 200 to 2000 cm hr -1 Dominant phases for resistance to transfer: Resistance = ( RT k w ) / ( K H k a ) = * / K H soResistance = / 25 o C K H >~ atm m3 mol-1 ===> resistance is 95 % in water phase K H resistance is primarily in air phase

Air – Water Exchange Mechanisms 4 layers of resistance to transfer in series: Vertical Transport in turbulent air and water is fast (& generally not limiting to gas exchange). Transport is diffusion limited in stagnant films (layers) on both air and water side of the interface Exchange is instantaneous at the air-water interface. In cases where effectively no mixing occurs in boundary layers, Whitman 2 layer (film) model applies In cases of high turbulence on air and water sides, “new” and and water parcels displace “old” air and water parcels, Surface Renewal Model applies. In both models, mixing forces dissipate rapidly below 1mm on air side and 0.1 mm on water side So, Boundary Layer thicknesses are: ~1000  m – air ~  m – water In both models, gas penetration is rapid (high injection velocities) at interface and equilibrium is achieved and assumed (thus we can use K H ) Overall: Limitations to transfer are provided by both boundary layers

Influence of K H on Dominant Process Figure from Schwarzenbach, Gschwend and Imboden, 1993 Large Compounds Small compounds Polar Compounds Non-Polar Compounds

Surface Renewal Model Figure from Schwarzenbach, Gschwend and Imboden, 1993

Surface Renewal Model Eddies Non-renewed Surface Renewed Surface Parcels of Air and water are mixed to interface where exchange occurs (instantaneously).

Surface Renewal Model F = ( 1 / (1/ ( r * D w ) 1/2 ) + (1 / (K H ’ (r * D a ) 1/2 ) ) * ( C w – C a / K H ’ ) Mass transfer coefficientConc. gradient (or, water parcel renewal rate) where r = water parcel renewal rate (t -1 ) D w, D a = molecular diffusion coefficents v tot = [ ( 1 / ( r w D w ) 1/2 ) + 1 / (KH’ (r a D a ) 1/2 ) ] -1 v w = ( r w D w ) 1/2 v a = ( r a D a ) 1/2

Surface Renewal Model: Continued Conceptually, describes turnover of parcels of air and water at interface Dominant exchange process is renewal or exchange of parcels ˆ no diffusive exchange in boundary layers ( diffusive exchange at interface) ˆsize of boundary layer is not important Account for time varying diffusion v w = ( r w D w ) 1/2 v a = ( r a D a ) 1/2 where r w = renewal rate for water parcels (sec -1 ) r a = renewal rate for air parcels (sec -1 ) Conceptually ==> when r , then z  and thus F .

Surface Renewal Model: Continued F = K ol * ( C w – C a H*) resistance to mass transfer * conc. gradient 1 / K ol = ( 1 / ( r w D w ) 1/2 ) + ( 1 / H* ( r a D a ) 1/2 ) 1 / K ol = 1 / k w + 1/ (H* k a ) un-measurable parameters: r w, r a

Where do these two models leave us? F = K ol * ( C w – C a / H) Whitman two film model un-measurable parameters: z w & z a Surface renewal model un-measurable parameters: r w, & r a