BAE 820 Physical Principles of Environmental Systems

Similar documents
Gas transfer rates If either phase concentration can not be predicted by Henry's law then there will be a transfer of mass across the interface until

Theories for Mass Transfer Coefficients

Interphase Mass Transfer see Handout. At equilibrium a species will distribute (or partition ) between two phases.

Mass Transfer Operations I Prof. Bishnupada Mandal Department of Chemical Engineering Indian Institute of Technology, Guwahati

Mass Transfer Fundamentals. Chapter#3

Steady-State Molecular Diffusion

Chapter 2 Mass Transfer Coefficient

Mass Transfer Coefficients (MTC) and Correlations II

AGITATION AND AERATION

Mass Transfer Operations

CHAPTER 3 MODELLING AND ANALYSIS OF THE PACKED COLUMN

PRINCIPLES AND MODERN APPLICATIONS OF MASS TRANSFER OPERATIONS

Chemical Reaction Engineering II Prof. A. K. Suresh Department of Chemical Engineering Indian Institute of Technology, Bombay

MASS TRANSFER COEFFICIENTS DURING AERATION BY A SELF-ASPIRATING IMPELLER

Part I.

MASS TRANSFER AND GAS ABSORPTION EQUIPMENT

Air-Water Gas Exchange of Chemicals

BAE 820 Physical Principles of Environmental Systems

Outline. Definition and mechanism Theory of diffusion Molecular diffusion in gases Molecular diffusion in liquid Mass transfer

In all electrochemical methods, the rate of oxidation & reduction depend on: 1) rate & means by which soluble species reach electrode surface (mass

Mass Transfer II Prof. Nishith Verma Department of Chemical Engineering Indian Institute of Technology, Kanpur. Lecture No. # 9

Mass Transfer-I BIJU PATNAIK UNIVERSITY OF TECHNOLOGY

Mass Transfer Operations I Prof. Bishnupada Mandal Department of Chemical Engineering Indian Institute of Technology, Guwahati

A Mass Transfer Experiment Using Deoxygenation and Aeration of Water

1 Model for gas-liquid reactions Based on film model

Introduction to Mass Transfer

Mass Transfer Operations I Prof. Bishnupada Mandal Department of Chemical Engineering Indian Institute of Technology, Guwahati

SELECTIVE REMOVAL OF CARBON DIOXIDE FROM AQUEOUS AMMONIA SOLUTIONS

Part II: Self Potential Method and Induced Polarization (IP)

ERT 216 HEAT & MASS TRANSFER SEM2, 2013/2014

Application of the penetration theory for gas - Liquid mass transfer without liquid bulk van Elk, E. P.; Knaap, M. C.

Chemical Reaction Engineering

Heat and Mass Transfer Unit-1 Conduction

Exchange of Volatiles between Air and Water, Lecture 5b, Contaminant Fate and Transport in the Environment (Chapter 2)

DEMONSTRATION OF MASS TRANSFER USING AERATION OF WATER

BASIC DESIGN EQUATIONS FOR MULTIPHASE REACTORS

CHEMICAL ENGINEERING

Nirma University Institute of Technology Chemical Engineering Department, Handouts -RRP- CRE-II. Handouts

Unit OperatiOn. Table 1: List of some unit operations

Investigation of Packing Effect on Mass Transfer Coefficient in a Single Drop Liquid Extraction Column

Physical Final Exam

POSITION R & D Officer M.Tech. No. of questions (Each question carries 1 mark) 1 Verbal Ability Quantitative Aptitude Test 34

SEPARATION BY BARRIER

EXPERIMENT 1 DETERMINATION OF GAS DIFFUSION COEFFICIENT

Physicochemical Processes

MASS TRANSFER EFFICIENCY IN SX MIXERS

Removal of Carbon Dioxide from Indoor Air Using a Cross- Flow Rotating Packed Bed

SOFTbank E-Book Center Tehran, Phone: , For Educational Use. Gas/Liquid Oxygen Transfer and Stripping. Transport by Diffusion

e - Galvanic Cell 1. Voltage Sources 1.1 Polymer Electrolyte Membrane (PEM) Fuel Cell

Mechanical Engineering. Postal Correspondence Course HEAT TRANSFER. GATE, IES & PSUs

Absorption of gas by a falling liquid film

AIRLIFT BIOREACTORS. contents

A modication of the lm. model. Heikki Haario. Department of Mathematics. University of Helsinki. Hallituskatu 15, Helsinki.

[Ammonia absorption] Experiment conducted on [13 February 2013]

Recap: Introduction 12/1/2015. EVE 402 Air Pollution Generation and Control. Adsorption

NPTEL. Chemical Reaction Engineering II - Video course. Chemical Engineering. COURSE OUTLINE

Redacted for Privacy Octave Levenspiel

5. Boundary Exchange: Air-Water and Sediment-Water Interfaces

Differential equations of mass transfer

2 THEORY OF TRANSPORT IN MEMBRANES

Processes and Process Variables

Mass Transfer and Separation Processes

NPTEL. Mass Transfer Operations I - Web course. Chemical Engineering. COURSE OUTLINE

Convective Mass Transfer

BAE 820 Physical Principles of Environmental Systems

Chapter 6. Membrane Process (Carrier Mediated Transport)

Measurement Technique in Multiphase Flows Dr. Rajesh Kumar Upadhyay Department of Chemical Engineering Indian Institute of Technology, Guwahati

Application of CFD Techniques for Prediction of NH 3. Transport Through Porous Membranes

Topics in Other Lectures Droplet Groups and Array Instability of Injected Liquid Liquid Fuel-Films

ENGG 199 Reacting Flows Spring Lecture 4 Gas-Liquid Mixing Reactor Selection Agitator Design

CHAPTER 8 ENTROPY. Blank

C. S. R. Prasad, H. Z. Fani, S. B. Menon

Fundamentals of Mass Transfer

Chemical Engineering 140. Chemical Process Analysis C.J. Radke Tentative Schedule Fall 2013

AMRITA VISHWA VIDYAPEETHAM DEPARTMENT OF CHEMICAL ENGINEERING AND MATERIALS SCIENCE. PhD Entrance Examination - Syllabus

Darcy s Law. Darcy s Law

OLI Simulation Conference 2010

Diffusion and Adsorption in porous media. Ali Ahmadpour Chemical Eng. Dept. Ferdowsi University of Mashhad

Chemical Reactions II

Solutions and Their Properties

Sulpher Dioxide Pollution Control by Wet Scrubbing Methods

Name of Course: B.Tech. (Chemical Technology/Leather Technology)

Principles of Convective Heat Transfer

Advanced Transport Phenomena Module 6 - Lecture 28

Physical Pharmacy. Diffusion

Biotransport: Principles

California Standards Test (CST) Practice

Chemical Reaction Engineering - Part 16 - more reactors Richard K. Herz,

THINK FLUID DYNAMIX Mixing, Homogenization & Blend Time. THINK Fluid Dynamix

HIGH FREQUENCY ULTRASONIC ASSISTED MASS-TRANSFER FOR WATER BATCH REACTOR

Convective Heat and Mass Transfer Prof. A.W. Date Department of Mechanical Engineering Indian Institute of Technology, Bombay

EEC 503 Spring 2009 REVIEW 1

Chapter 3. Solution

Prof. Mario L. Ferrari

Analysis of Performance of Packed Columns

University School of Chemical Technology

Biological Process Engineering An Analogical Approach to Fluid Flow, Heat Transfer, and Mass Transfer Applied to Biological Systems

Adsorption (Ch 12) - mass transfer to an interface

University of Groningen

Forced Convection: Inside Pipe HANNA ILYANI ZULHAIMI

Transcription:

BAE 820 Physical Principles of Environmental Systems Inter phase mass transfer Dr. Zifei Liu

Mass transfer between two phases For a two phase system not at equilibrium (concentrations in the two phases are not as predicted by Henry's law), mass transfer will occur to bring it to equilibrium. There must be concentration gradient in the direction of diffusion within each phase. E.g. diffusion of a soluble gas such as ammonia between air and water. 2

A simple conceptualization of the gasliquid transfer process developed by Nernst (1904). Near the interface, there exists a hypothetical stagnant film. In this film, bulk liquid is not moving. Therefore, transport is governed essentially by molecular diffusion. Fick's law describes flux through the film. If the thickness of the stagnant film is given by δ n then the diffusion flux can be approximated by J = -D C x -D(Cb Ci) δ n Film Theory C b and C i are concentrations in the bulk and at the interface, respectively. 3

Two film theory Developed by Lewis-Whitman (1924). Assuming that There are two stagnant layers of film at the interface. The mass transfer across the films is by molecular diffusion. The bulks of gas and liquid are homogeneous with respect to solute. When the mass transfer is in the X direction (from gas phase to liquid phase), there must be a concentration gradient in the direction of mass-transfer within each phase. The bulk gas concentration C g falls to C gi at the interface. In the liquid phase, the concentration falls from C li at the interface to C l in the main body of liquid. C gi and C li are at equilibrium. C g and C l are clearly not the equilibrium values since otherwise the mass transfer would not occur. 4

The two film theory 5

Concentration gradients for the film theory More realistic concentration gradients Gas phase C g Gas film Interface C gi Liquid film Liquid phase Gas phase C g Interface C gi Liquid phase C li C li C l C l Mass transport Mass transport 6

The flux equations Gas phase transport J g = k g (C g -C gi ) Liquid phase transport J l = k l (C li -C l ) Where k l or k g = mass transfer coefficient for either the liquid or gas phase. k l =D l /δ l, k g =D g /δ g C gi =H c C li. At steady state, J = J g = J l The difficulty is finding interface concentrations, C gi or C li, which cannot be measured directly. We want to be able to relate flux to bulk air and water concentrations. Therefore, overall mass transfer coefficients are defined. 7

The overall mass transfer coefficients Define J = K g (C g -C g* ) = K l (C l* -C l ) Where K g is overall mass transfer coefficient based on gas-phase concentration, K l is overall mass transfer coefficient based on liquid-phase concentration. C g* is gas phase concentration that would be in equilibrium with the bulk liquid concentration. C g* =H c C l. C l* is liquid phase concentration that would be in equilibrium with the bulk gas concentration. C l* =C g /H c. 8

1/K g 1/k g 1/k l 1/K l 9

Expand the liquid-phase overall flux equation J = K l (C l -C l* )=K l [(C l -C li )+(C li -C l* )] =K l [(C l -C li )+(C gi -C g )/H c ] = K l [J/k l +J/(k g H c )] Therefore, 1 = 1 + 1 K l k l H c k g In which, 1 represent the overall resistance to mass transfer based on liquid K l phase concentration, and it is the sum of liquid film resistance ( 1 k l )and gas film resistance ( 1 H c k g ). Similarly, 1 K g = 1 k g + H c k l 10

It is possible that one of the films exhibits relatively high resistance and therefore dominates the overall resistance to transfer. This depends on the relative magnitudes of k l, k g and H c. For highly soluble gases such as NH 3 and SO 2 (H c is low), mass transfer is controlled by gas film resistance. 1 1 So, K k l H c k l H c k g g For less soluble gases such as N 2 and O 2 (H c is high), mass transfer is controlled by liquid film resistance. 1 1 So, K k l H c k l k l g 11

Other theoretical models for interphase mass transfer Interphase mass transfer (gas/liquid interface or liquid/liquid interface) are of great interest in separation processes, such as absorption, distillation, extraction, stripping, etc. Theoretical models for interphase mass transfer Film theory (Nernst,1904) Penetration theory (Higbie, 1935) Surface renewal theory (Dankwerts, 1951) Film-penetration theory Boundary layer theory 12

Penetration theory (Higbie, 1935) Eddies move from the bulk to the interface and then leave the interface to mix with the bulk stream. They stay at the interface for a short, fixed period of time during which they remain static so that molecular diffusion takes place. the penetration theory is most useful when mass transfer involves bubbles or droplets or flow over random packing. Mass transfer flux is given by D J=2 (C πt i -C b ) c Where t c is the average contact time of the static eddy at the interface during one cycle (a constant for a given mixing level) 13

Surface renewal theory (Dankwerts, 1951) Danckwerts suggested an improvement to the penetration theory that involves the replacement of the constant eddy contact time with the assumption of a residence-time distribution. Mass transfer flux is given by J= Ds(C i -C b ) Where s is surface renewal rate (again, a function of mixing level in bulk phase). 14

Comparison of the three theories Film theory k= D δ n Penetration theory k=2 D πt c Surface renewal theory k= Ds Boundary layer theory k~d 2/3 In the film theory, k is proportional to D. In penetration theory and surface renewal theory, k is proportional to D 0.5. Most experimental observations show that k is proportional to something in between. The power of D are between 0.5 and 1.0, with higher turbulence being closer to 0.5. In boundary layer theory, the power=2/3. 15

Aeration Transfer of gas across a gas-liquid interface can be accomplished by bubbles or by creating large surfaces (interfaces). Aeration or transfer of air or oxygen to water is a very common process in treatment systems. Bubble injection is a common method to accomplish this transfer. For the case of oxygen transfer to water consider each bubble to consist of completely mixed bulk gas phase (inside the bubble) plus a stagnant liquid film. (the stagnant air film may exist but for oxygen transfer control is usually in the liquid film). 16

The rate of change of gas concentration in the liquid phase dc L = AJ = A K dt V V L (C L *-C L ) = K L a (C L *-C L ) Where, A is the total surface area of the bubbles, V is the volume of the liquid phase. Define K L a= A V K L, is a handy engineering coefficient. It is a lumped parameter takes into account bubble size, temperature (through its effect on diffusion), turbulence ( through its effect on film thickness or surface renewal rate). Integration yields -K L a = ln(cl Ct 1) ln(cl Ct 2 ) t l t 2 K L a can be determined from experiment data though a plot of ln(c L Ct) vs time, which will yield a straight line with slop equal to -K L a. 17

Factors that may affect K L a Factors that affect K L a The concentration of surfactants in the liquid phase. This is of particular concern when we deal with wastewaters. Surfactant effects are often taken into account by K L a (wastewater) = α K L a (clean water) 0.2<α<1 Temperature (K L a) T = (K L a) 20ºC 1.024 (T-20) Factors that affect C L * The solubility of gases in wastewater is affected by solid content. C L * (wastewater) = β C L * (clean water) 0.85<β<1 18

Diffused aeration In diffused aeration systems air is pumped through some sort of diffuser to generate small bubbles. These diffusers are porous ceramics, cloth or plastic. Usually gas ( air or oxygen) is injected into the bottom of the aeration tank and is allowed to rise to the surface in an open tank.

Surface aeration In this case a mixing device is used to agitate the surface so that there is increased interfacial area between liquid and air. There are many different proprietary types of surface aerators.

Problem solving #6-1 Estimate the overall liquid-side mass transfer coefficient at 25ºC for oxygen from water into air. For oxygen in air, the diffusion coefficient is 0.23 cm 2 /sec; for oxygen in water, the diffusion coefficient is 2.1 x 10-5 cm 2 /sec. The Henry s law constant is 769 L atm/mol. Use the two film theory, and assume that the film thickness is 0.01cm for both gas and liquid phase. Which phase has more resistance for the overall mass transfer? 21

Problem solving #6-2 Carbon dioxide is being scrubbed out of a gas using water flowing through a packed bed of 1 cm Berl saddles. The carbon dioxide is absorbed at a rate of 2.3 x 10-6 mol/cm 2 sec. The carbon dioxide is present at a partial pressure of 25 atm, the Henry s law coefficient is 29 L atm/mol, and the diffusion coefficient of carbon dioxide in water is 1.9 x 10-5 cm 2 /sec. Assuming mass transfer is controlled by liquid film resistance, find the film thickness. 22

Problem solving #6-3 The value of K 1 a for a certain industrial waste is 2.46 per hour at 20ºC. What is the value of K 1 a at 25ºC? 23

Problem solution #6-1 δ n =0.01 cm k l = D l = 2.1 10 5 δ n 0.01 k g = D g δ n = 0.23 0.01 = 23cm/s K l = 1 1 + 1 = k l H c k g = 2.1 10 3 cm/s 1 1 2.1 10 3+ 1 23 769/24.4 = 2.1 10 3 cm/s K l k l. Mass transfer is controlled by liquid film resistance

Problem solution #6-2 C l * = p /H c = 25/29 = 0.86 mol/l =0.00086 mol/cm 3 J k l K l = C l Cl 2.3 10 6 = 2.7 0.00086 0 10 3 cm/s δ n = D l k l = 1.9 10 5 2.7 10 3 = 0.007 cm

Problem solution #6-3 (K la ) 25ºC = (K l a) 20ºC 1.024 (T-20) =2.46 1.024 (25-20) =2.77 h -1