DOI : 10.17577/IJERTV15IS060864
- Open Access

- Authors : Srikanth Reddy Jonnala, Patnala Ranjit Kumar
- Paper ID : IJERTV15IS060864
- Volume & Issue : Volume 15, Issue 06 , June – 2026
- Published (First Online): 20-06-2026
- ISSN (Online) : 2278-0181
- Publisher Name : IJERT
- License:
This work is licensed under a Creative Commons Attribution 4.0 International License
Performance Evaluation of a Scrubber for CO2 Gas Removal – A Case Study from a Pharmaceutical API Manufacturing Plant
A Case Study from a Pharmaceutical API Manufacturing Plant
Srikanth Reddy Jonnala (Author)
Department of Research and Development Lee Pharma Limited, Visakhapatnam, Andhra Pradesh, India
Patnala Ranjit Kumar (Author)
Department of Technical services Lee Pharma Limited, Visakhapatnam, Andhra Pradesh, India
Abstract – Industrial manufacturing process generates gaseous Pollutants that must be Controlled before Discharge into the Atmosphere. For that Industrial Scrubbers Play Critical Role in Controlling gas Emissions. This Study represents a Systemic Approach in to Scrubber Performance Evaluation Through Mole Balance Methodology and focusing on Gas Liberation and Absorption in a Industrial Applications. This Case analysis Demonstrates how Mole Balance Can be applied to Design, Optimize and Troubleshoot the Scrubber. In a Industrial Applications Most of the Chemists and Junior Level People have some Confusion on Gas Liberation and mole Balance but it is a Important Practice For a Industrial Level People. In This paper Represents a Easy and effective Way to practice the Industrial Format to save Our Environmental Surroundings and Useful to all Industrial Formats.
Keywords – Scrubbers, Absorption, Optimize, Mole Balance, Emission
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INTRODUCTION
Industrial processes often generate gaseous by-products that must be controlled to meet environmental and safety standards. Scrubbers are widely employed as gas treatment units, designed to remove pollutants through absorption, chemical reaction, or neutralization. Accurate calculation of scrubber performance is essential for optimizing design, minimizing emissions, and ensuring compliance with regulatory frameworks.
Traditional approaches to scrubber analysis rely on empirical correlations or pilot-scale testing, which may not fully capture the dynamic behaviour of gas liberation and absorption under varying industrial conditions. In contrast, mole balance provides a rigorous theoretical framework for quantifying the rate of gas liberation and pollutant removal efficiency. By applying mole balance equations, engineers can predict scrubber performance, identify limiting factors, and optimize operating parameters with greater precision. This study focuses on integrating mole balance methodology into scrubber calculations for industrial applications. The aim is to bridge the gap between theoretical modelling and practical operation, demonstrating how mole balance can
serve as a robust tool for design, troubleshooting, and performance evaluation. Through case analysis, the paper highlights the relevance of mole balance in improving emission control strategies, reducing operational costs, and advancing sustainable industrial practices.
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LITERARTURE REVIEW
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Scrubber Design Studies:
A venturi scrubber consists of three sections: a converging section, a throat section, and a diverging section. The inlet gas stream enters the converging section and, as the area decreases, gas velocity increases. Liquid is introduced either at the throat or at the entrance to the converging section. The inlet gas, forced to move at extremely high velocities in the small throat section, turbulently mixes with the liquid, producing an enormous number of very tiny droplets. Particle and gas removal occur in the diverging section as the inlet gas stream mixes with the fog of tiny liquid droplets. The inlet stream then exits through the diverging section, where it is forced to slow down
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Wet Scrubber:
The term wet scrubber describes a variety of devices that remove Pollutants from a Furnace Flue Gas or from other gas streams. In a wet scrubber, the polluted gas stream is brought into contact with the scrubbing liquid, by spraying it with the liquid, by forcing it through a pool of liquid, or by some other contact method, so as to remove the pollutants.
Wet scrubbers capture relatively small dust Particles with the wet scrubber’s large liquid droplets. In most wet scrubbing systems, droplets produced are generally larger than 50 micrometres (in the 150 to 500 micrometres range). As a point of reference, human hair ranges in diameter from 50 to 100 micrometres.
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Mole Balance:
While mole balance is a fundamental chemical People tool, its direct application in scrubber calculations is less explored in literature.
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METHODOLOGY
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Applying Mole Balance:
A + B + K2CO3 C + 2 KCL + CO2
LHS
RHS
C:
21
C:
21
O:
4
If we Add 2 Moles in KCL then
O:
3
Cl:
1
Moles is Balanced
Cl:
1
H:
28
H:
27
K:
2
K: 1+1= 2
Here mole Balance applying to Gag Phase to determine the liberation Rate. For that I Got 1 mole of KSM Liberates 1 Mole of Co2.
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Industrial Application Procedure:
12″
12″
Blower Vent
2″
2″
12″ Chilled Out
Chilled Out
6 m2 6m2
12″
Chilled In
Chilled In
6″
12″
2″
12″
6″
1″
1″
2″ 2″
2″ H2O + Lye Solution 2″ H2O + Lye Solution
Blower
6″
Circulation Pump
10 m3/Hr
Circulation Pump
10 m3/Hr
Before Getting Into Calculation Firstly we have to Follow up on Piping & Instrumentation Diagram in Our Plant Wet Scrubber made on Packed Bed with Pall Rings with MOC PP Rings & Typical Size is 25mm & Packing Height is Considered as 2.5 meters. For any Engineers or production side
Chemists Estimate to Calculate the Gas Velocity & Preferable Scrubber Diameter, Liquid Flow Rate & Finding Re- Circulation Capacity. It Helps to Lead troubleshoot at Initial Problems and Helps to Save our Environment. For a Industrial framework I Draw a P&ID Diagram For a Industrial Module.
Fig.1 Piping & Instrumentation Diagram in a Industrial Scale
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CALCULATION WORK:
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Mole Balance:
Initially we have to Balance the Reaction. The Thing is Separate the L.H.S = R.H.S and Equate the Both Values. Here that in my Balance I Got 2 Moles of Potassium Chloride and 1 Moles of CO2 Gas then we have to Conclude the reaction Balance.
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Find No, Of Moles in Reactants:
Moles of (A):
n= WEIGHT/ MOLECULAR WEIGHT
n= 100 Kg/ 225.33 Kg/K. mole n= 0.4437 k. mole.
Moles of (B):
n= WEIGHT/ MOLECULAR WEIGHT n= 62/ 108.57
n= 0.5710 k. mole
Moles of K2Co3:
n= WEIGHT/ MOLECULAR WEIGHT
n= 113 Kg/ 138.21 Kg/K. mole n= 0.8175 k. mole
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Gas Liberation Calculation:
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1 K. mole of C16H19N React 1K. Mole of Co2
Co2 Gas Liberation Quantity:
0.4437 K. mole × 44.01 Kg/K. Mole
Volume (V)= 19.527237 Kgs
N (No, of moles) = 0.4437 k. mole.
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Total Gas Generated:
Total k. mole of Gas:
Moles= 0.4437 mole + 0.4437 K. Mole
Volume (V)= 0.8874 k. mole
at STP 1 k mole = 22.4 Nm3/k mole
Volume (V)= 0.8874 k mole × 22.4 Nm3/k mole
Volume(V)= 19.8901836 Nm3
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NaOH Requirement:
Before Getting into this Findings Firstly we Have to Find After CO2 Gas Inlet into Scrubber the Reaction
Carry Forwarded inside Scrubber is must to be Understand. Here the reaction Inside is NaHCO3
CO2 Neutralization:
Reaction in Scrubber:
Co2 + NaOH NaHCo3
Input Generation of Co2:
Co2= Liberation/ Molecular Weight
n = 0.451946912 k. mole
NaOH Required for Neutralizing of CO2: Volume (V)= 0.4437 K. mol × 40 Kg/K. mole Volume (V)= 17.748 Kg
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Calculation of Gas Emission:
PPM=
Input Data:
Blower Capacity = 3000 m3/Hr. Addition Time = 3 Hours
Finding total Exhaust Gas Volume:
Total Gas Volume = 3000 m3/Hr. x 3 Hours Total Gas Volume = 9000 m3
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Conve t CO2 in Kgs to mg:
19.49 Kgs = 19490000 mg
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C lculate mg/m3:
CO2 Concentration = CO2 Concentration = 2165.55 mg/m3
Now Calculate PPM:
PPM=
= 2165.55 x 24.45 /44.01
= 1203.086 PPM
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Packed Bed Scrubber Design:
Finding Gas Flowrate:
Blower Flowrate = 2500 m3/Hr.
2500 m3/Hr. x 1.2 (20%) = 3000 m3/Hr
*Finding Gas Velocity:
Acid gas Scrubber = 1-2 m/s I have to Take 1.5 m/s Solvent Vapor = 1.5-2.5 m/s
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Calculate Diameter:
Formulae:
Area =
=
Area = 0.556 m2 Now I Find Diameter:
D=
D= 0.84 m
Scrubber Diameter is 850 mm.
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Finding liquid Flowrate & Recirculation pump Capacity
As considered at L/G Ratio CO2 Gas Having Ratio is 5 L/m3 So, we have Gas Flowrate is 3000 m3/Hr. then the Circulation Flowrate is 3000 m3/hr. × 5 L/m3 = 15,000 Liter/ Hour Finally Flowrate is 15 m3/hr.
Recirculation pump Capacity:
Previously we Got Liquid Flowrate is 15 m3/Hr. so, requirement of Pump is Nearly 15-20 m3/Hr. then Total Dynamic Head is H(static)+H(friction)+H(pressure)+H(velocity) Flowrate = 20 m3/Hr.
Static Lift = 6 m
Friction Loss = 4 m Pressure Head = 2 m Velocity Head = 1 m
Formulae: H(static)+H(friction)+H(pressure)+H(velocity)
= 6 m + 4 m + 2 m + 1 m
Head (m) = 13 m
Consideration of Head is Nearly 15 meters.
Parameters
Result
Gas
Co2
Total Moles Generated (k. mole)
0.8874
Total Gas Generated (Kg)
19.890
NaOH Requirement For Neutralize (Kg)
17.48
CO2 Liberation in PPM
1203.086
Scrubber Diameter Required
850 mm
Liquid Flowrate
15 m3/hr.
Requirement of recirculation Pump
20 m3/Hr.
Requirement of Pump Head
15 meters
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RESULTS & DISCUSSION:
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REFERENCES:
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Venturi Scrubber Design and Analysis
Design and Analysis of Venturi Scrubber,© 2019 JETIR April 2019, Volume 6, Issue , Discussion about venturi scrubber design, particulate matter removal and efficiency related to throat velocity and pressure drop.
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Packed Column Scrubber Design, How To Design a Scrubber [Packed Column], Pharma Engineering, 2020, Provides practical design calculations for packed bed scrubbers, including blower sizing, packing selection (Pall rings, saddles), and absorption principles
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EPA Guidelines on Wet Scrubbers
Wet Scrubbers for Acid Gas, U.S. Environmental Protection Agency, Chapter1 Section 5.2. Covers absorption principles in packed towers, venturi scrubbers, and spray chambers, with emphasis on pollution control applications.
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Multiapproach Design Methodology of Downscaled wet Scrubber Study the Collection of Submicronic Particles from Waste Incineration Flue Gas
