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COOLING WATER TREATMENT
ByPrem Baboo
National Fertilizers Ltd.India.Fellow of Institution of Engineers, India
INTRODUCTION• Location- At Vijaipur, Dist-Guna
Around 850km from Mumbai.• Plant details
Unit Vijipur I Vijaypur II
Ammonia Plant MTPD 1520 1520Urea Plant MTPD 2620 2620CPP MW 3 x 17.5 3 x 17.5Raw Material NG NG/NaphthaCommisioning 1987 1998
Details of Cooling Tower.
Ammonia I Urea I Ammonia II Urea IIType Induced
draftCross flow
Induced draft
Cross flow
Induced draft
Cross flow
Induced draft
Cross flow No. Of Cells
6 5 6 5
Delta T 10 10 10 10CR m3/hr 17000 16000 18000 17000System Hold Up
7500 7000 7500 7000
Make up Water QualityParameter UNITS Typical RangepH 7.5 – 8.2Total Hardness Ppm 75 – 120Ca-Hardness Ppm 50 – 80Mg-Hardness Ppm 25 – 40
Silica Ppm 10 – 25Chlorides Ppm 10 – 25M-Alkalinity Ppm 60 – 150Sulphates Ppm 10 – 50TDS Ppm 150 – 200
Re-circulating Water Parameters. Parameter Units Normal Operating
RangepH NTU 6.8 – 7.5Turbidity Ppm 5Total Hardness Ppm 700 – 800TDS Ppm 2200maxSilica Ppm 100maxChlorides Ppm 150 – 250Iron Ppm 1.5maxZinc Ppm 1.0maxTotal PO4 Ppm 4 – 8COC 6-8TBC Counts/ml 1 x 105
SRB Counts/100ml
100
Monitoring Tools1. Corrosion Coupons2. Deposit monitor3. Bio-fouling monitors4. Test heat exchanger5. Microbial counts6. ORP meter7. Inspection of cooler during shut
down
Cooling Systems
• Once-through systems• Closed recirculating systems• Open evaporative recirculating
Simple Cooling Water Diagram
Simple cooling water diagram.
Cooling tower
Blow down
[evaporation]
Return water Coolers
Heat exchangers
Cooling Water Terminology• Cooling water - water used to cool process
fluid, condense steam, cool oil, air, etc• Make-up water - fresh water added to
make-up for loss water• Evaporation - droplets of hot return water
that evaporate taking heat with them cooling the remaining water
• Blow-down or bleed-off - water that is being drained or loss beyond control
Terminology• Cycle of concentration - how many
times concentrated the cooling water is compared to the make up water (dissolved solid concentration)
• Drift loss - loss of water through windage
• Circulation Rate - total circulation pump flow rate
Terminology• Supply temperature - temperature of
the supply water• Return temperature - temperature of
the return water• Delta T (temperature different) - the
difference between return and supply temperature (T return - T supply)
Relationship of various parameters• Cycles Of Concentration C = Concentration in Recirculation Concentration In Make-up
• Evaporation Loss E = 0.0018 x deltaT x R x TF (Tower
Factor)* ( T expressed in oC)
* Tower factor is based on humidity/% contribution of evaporation to delta T
Relationship of various parameters• Windage Loss
W = 0.05 to 0.2 x R / 100
• Blow Down B = E / ( C – 1 ) • Make-up M = E + W + B
Cooling Water Chemistry• pH• Conductivity or Total Dissolved Solid• Turbidity or Total Suspended Solid• Total hardness• Calcium hardness• Alkalinity (p and m)• Chloride• Sulfate• Silica
More Parameters
• Total Iron• Inhibitor residuals (i.e. o-phosphate,
phosphonate, zinc, molybdate, etc.)• Bacteria counts (TBC , SRB, Nitrifying )• Chlorine i.e FRC• ORP• CLO2 levels
pH• Low pH means more hydrogen
ions• Hydrogen ions depolarizes
corrosion cells accelerating corrosion
• High pH means more hydroxyl ions
• Environment for scales formation• Environment for microbiological
activities
Conductivity or TDS
• High values mean more dissolved minerals
• Higher ions movement improves electrical conduction
• Increase the rate of electrochemical corrosion.
Turbidity and Total Suspended Solid
• The content of suspended solid in the water - silt, debris, air-borne materials
• Higher values indicate potential fouling due to deposition of the solid
• The deposition might be combined with microbiological activities - microbiological sludge and MIC
Total Hardness• The contents of permanent hardness -
calcium, magnesium, barium, strontium• Generally indicates the total content of
calcium and magnesium as CaCO3
• Read as CaCO3 due to the molecular weight - 100
• High values indicate potential scales formation when there is a presence of complexing anions
Calcium Hardness• The content of calcium in water
read as CaCO3
• The most common component of scales in water system
• May form calcium carbonate, calcium phosphate and calcium sulfate scales
• High values may also indicate less corrosive (electrochemically) water
Alkalinity• Acid neutralizing ability
• Free mineral acidity - CO2 at pH < 4.2
• M-alkalinity consisting of HCO3- and
CO32- beginning from methyl-orange
point pH >4.2
• P-alkalinity consisting of CO32- and OH-
beginning from phenolpthalien point pH >8.2
Chloride and Sulfate• Corrosive ions - form metal
chloride and sulfate then mineral acids
• Cause pitting corrosion• Chloride - environment for SCC -
stainless steel• Sulfate - required element for SRB
Total Iron
• High values may indicate corrosion activities
• Potential deposition of corrosion products - fouling and under-deposit corrosion
Inhibitor Residuals• Depending of inhibitors used and
control ranges• Inhibitors - phosphate (ortho or total),
phosphonate, zinc, molybdate, toly-triazole
• Low level - insufficient protection• High level - potential scales formation
(precipitative chemistry) and non economical
Why do we treat cooling water?• Corrosion of ferrous and non-ferrous
metals - electrochemical• Precipitation and deposition of
mineral scales• Deposition of suspended solid• Microbiological sludge deposit • Biofilm or microbiological slime• Microbiologically influenced corrosion
Corrosion Scaling
PROBLEMS
Fouling
General Fouling Microbial Fouling
Algae,
Fungi,
CORROSION• Corrosion is an electrochemical
process by which metals return to their native state
• Mild Steel reverts back to Iron Oxide
• This is also true for copper alloys, Zinc, Aluminum etc.
Localised corrosion• c
+ Cathode +
Fe(OH)3
Fe2O3
Fe(OH)2
Fe++
- Anode -
Fe
Metal
e-
e-e-
e-
+ Cathode +OH-
02+H2O
Corrosion Cell 2Fe + O2 + 2H2O ---> 2Fe (OH )2 Ferrous
Hydroxide
2Fe(OH)2+H2O+1/2O2 ->2Fe(OH )3
Hydrated Ferric
Oxide
Prevention Of Corrosion• Condition the metal
– coating (Zinc,Epoxy Resin) .
– Alloy the metal (Stainless Steel)
• Condition the environment Remove Oxygen
• Use corrosion inhibitors
Corrosion Inhibition Mechanisms
• Oxidation• Oxidation with film strengthening• Cathodic polarization• Cathodic precipitants
Anodic InhibitorsAn anodic Inhibitor interferes with the
Anodic process
• Chromate• Molybdate• Phosphate• Nitrite• Phosphonates
Oxidation (With complexation)• .
Fe++
2e--
PO4PO4
Fe3(PO4)2 FePO4
Cathodic Inhibitors A Cathodic inhibitor interferes with the
cathodic process by precipitating an insoluble species onto the cathodic site.
• Zinc• Calcium Carbonate• Polyphosphate• Phosphate• Phosphonates
Cathodic Precipitants• .
Zn
e-
e-
e-
e-
e-
O2
O2
O2
O2
O2
OH-OH-OH-
ZnCa
HCO3HCO3
HCO3HCO3
HCO3
HCO3CaCa
Ca Zn
ZnZn
Zn
Zn(OH)2
HCO3 + OH H2O +CO3
CO3CO3Zn CaCO3
Zinc• Forms zinc hydroxide and zinc
carbonate complexes at cathode• Good for soft water• Above pH 8 will begin to precipitate
in bulk water• Zn is stabilised by phosphonates and
polymers• Levels from 0.25-3.0 ppm used
Poly and Ortho-phosphate• Form complexes with Ca at cathode• Need to formulate stabilizing polymer
with package• Also reacts at anode to form iron
phosphate complex• Levels of 2-15ppm typically used
depending on program
Scaling Caused by crystalline growth of salts on
the system surfaces• CaCO3 (Calcite) : Major Scale • Silica :Amorphous silica precipitates,when
*SiO2 > 150 ppm at pH < 8.0 . > 180 ppm at pH > 8.0
• MgSiO2 :Adsorption of silica on precipitated Mg(OH)2 (Brucite)
• Ca5(PO4)3OH (Hydroxyapatite)• CaF2 (Fluorite) : Potential foulant
Solubilities (20 / 100 deg C)
• Sodium Chloride• Sodium Sulphate• Sodium Carbonate• Sodium Bicarbonate• Sodium Phosphate• Calcium Chloride• Calcium Sulphate• Calcium Carbonate• Calcium Bicarbonate• Calcium phosphate
36% / 39% 16% / 30% 32% / 31% 8% / Dec 11% / Dec 43% / 61% 0.3% / 0.06% 0.005% /0.002% 0.08% / Dec 0.0003%/ 0.0002%
Solubilities ( 20 deg C )
• Silica• Ferrous
Hydroxide• Ferric
Hydroxide
• 0.005%• 0.0007%• 0.0001%
Formation of Hardness scale• Calcium Carbonate has inverse
solubility
• Ca(HCO3)2-------> CaCO3 + H2O + CO2
• Mg(HCO3 )2------> MgCO3 + H2O + CO2
• MgCO3+ H2O-----> Mg(OH)2 + CO2
Scale Formation• CaCO3 precipitates at Saturation pHs
and depends primarily upon:– Level Of calcium hardness– Level Of Bicarbonate alkalinity– pH– TDS– Temperature– Water velocity
Scale Inhibition• Remove hardness salts.
• pH control with Acid
• Dose scale inhibitor
Acid Dosing• Used to limit pH in hard water systems.• Helps in inhibitor selection• Potential for water and treatment savings by
allowing an increase in COC• Each 1ppm M Alkalinity will require:
• 1.0 ppm sulphuric acid• 2.0 ppm Hydrochloric acid• 1.8 ppm Nitric acid
Scale Inhibitors• Added to extend Induction time beyond Retention
time • Induction time decreases with increase in
Saturation level ( Driving force)• Effectiveness of Inhibitor depends on the extent
to which it increases Induction time at lesser dosage
• Inhibitor dosage is increased with increase in Induction time
• If retention time is less than induction time there is very little need of scale inhibitors
Dispersion• A process by which charged particles are
prevented from agglomerating into larger particles rendering them less settleable.
• Most cooling water particulates have a net negative charge. Acrylate dispersants also have a net negative charge. Addition of dispersant increases charge inhibiting agglomeration.
Dispersants• Polyacrylate• Acrylate /Acrylamide• Acrylate terpolymers• Sulfonated styrene• Maleic Acid Homopolymer• Maleic acid co and terpolymers
Bio Fouling• Caused by the excessive growth of
microorganisms.
• Cooling water system-ideal incubator for growth
Problems• Pitting corrosion-depolarising action
of O2 released during their metabolic process.
• Shield metal surfaces from the action of inhibitors
• cause legionella pneumophila disease
Chemical Control• Microbiocides e.g.
Bacteriacides,Fungicides,Algaecides
• Microbiostats e.g.
Bacteriastats,Fungistats,Algaestats
• Surfactants
Microorganisms
• Viruses
– Consists of protein & DNA/RNA (Nucleic acids)
– Survive by multiplying in other host cells - plant or Animals
Cooling Water as a MediumIdeal temperature (200C-600C)pH 6 to 8Often exposed to sunlightSome made of woodNitrogen and phosphorous based
inhibitorsSuspended and airborne debrisGood aerationPresence of process fluids like
ammonia, urea, other organics and sunlight
.• Algae
– Photosynthesis– Uni/Multicellular– Diverse Forms
Filamentous Colonial Plantlike
• Diatoms– A Group of Algae– Organic walls impregnated with silica
.• Blue Green Algae
– Photosynthetic bacteria
• Fungi – Aerobic growth above the waterline– Do not contain chlorophyll
.• Mould
– Fungus which forms visible layer on the surfaces - Wood/Walls/Foods
• Yeast– Unicellular Fungi
• Protozoa– Diverse group of unicellular Microorganisms
Bacteria• Unicellular• Cells may grow attached to each other in
clusters , chains , rods or filaments• Require carbon source for growth• Different shapes
– Rods Bacillus– Spherical Coccus– Spiral Spirill
• Protected by slime• Multiply by cell division
Bacteria (Classification )
• Aerobic Requires O2 & CO2• Anaerobic Grow in O2 free atmosphere• Facultative Grow in both conditions• Autotrophes Inorganic nutrients• Heterotrophes Organic nutrients• Psychrophiles < 22 0c• Mesophiles 22 ~ 45 0 C• Thermophiles > 45 0 C • Planktonic Free floating organisms in .
Water• Sessile Surface attached growing in .
Biofilm
Methods Of Control• Physical
– Nutrient Removal - Remove food or energy source .
e.g. Sunlight , Dead Leaves.Process Contamination.
– Temperature Control - Increase temperature
Not really practical on a Cooling System
Methods Of Control• Chemical
– pH Adjustment• With the help of Acid / Caustic (pH’s Over 10.0 Required)
– Microbiocide Control• Kill Organisms by use of toxic materiale.g. Algaecides,Fungicides, Bacteriacides
Chemical Control• Microbiocides e.g.
Bacteriacides,Fungicides,Algaecides
• Microbiostats e.g.
Bacteriastats,Fungistats,Algaestats
• Surfactants
Biocide Classification• Oxidising Materials
– Have the ability to oxidise organic matter– Irreversibly oxidise protein groups
• Non-Oxidising Materials– Destroy or inhibit normal cell metabolism by
any of the following ways:-• Altering permeability of cell wall• Destroying protein groups• Precipitating protein• Blocking metabolite reaction
Sulphate Reducing Bacteria• Anaerobic and convert dissolved sulphur
compounds to H2S 10 H++ SO4
-2+ 4Fe --> 4Fe+2+H2S +4H2O H2S + Fe+2 --> FeS + H+
• H2S released corrodes Carbon steel and Copper based alloys.
• Localised pH depressions cause further attack
• Exist mainly below deposits devoid of oxygen
• Corrosion rate as high as 100 mpy occurs
Nitrifying / Iron Bacteria• Nitrifying Bacteria :
– Oxidation of Ammonia . NH3 + 2O2 ---> HNO3 + H2O
– Nitrosomonas , Nitrobacter
• Iron Bacteria : – Oxidation of ferrous ions
. ++ .
– Fe + O2 ----> Fe2O3 – Crenothrex
Limitations Of Chlorination• Not effective in alkaline water
Cl + H2O = HOCl + HCl HOCl -> OCl- + H+
OCl- is 1/80 th time as effective as HOCl
Deactivated by the reducing agents H2S ,SO2,,NH3,polyacrylamide, Monoethnolamine,etc.
• Deactivates some Organo phosphonates, Does not penetrate slimes
• Extremely corrosive to many metals-maintenance of chlorinator is difficult.
• Environmental limitations - 0.1 ppm. Free Cl2 can kill fish
• When not effective use bromine compounds,chlorine dioxide,ozone
Chlorine A strong smelling, greenish-
yellow gas with pungent odor which is extremely irritating to mucous membranes.
Chlorine Gas• Hazardous• Heavier than air• Strong oxidizer• Low capital requirements• Produces chlorinated by-
products• Efficacy - pH dependent
Chemistry Chlorination
Chlorine gas dissolves in water and hydrolyses as:
Cl2 + H2O HCl + HOCl (hypoclorous acid)
HOCl ↔ H+ + OCl- – (hypo chlorite ion)
The percentage distribution of hypochlorite ion and undissociated hypochlorous acid can be calculated for various pH values.
The amount of hypochlorite ion becomes appreciable above pH 6 while molecular chlorine is non-existent.
HOCl is about 80 times more effective than OCl- as a biocide
Microbicidal Efficiency• HOCl – the microbicidal efficiency is due to
the relative ease with which it can penetrate cell walls. The penetration is quite comparable to water.
• OCl- - Poor disinfectant (about 1/80%
efficiency of HOCl). It is unable to diffuse cell wall of microorganisms due to negative electrical charge.
Chlorine EffectivenessAt Various pH
0102030405060708090
100 01020304050607080901004 5 6 7 8 9 10
Percentage HOCl
pH Value
Percentage OCl -
Microbiological Action
• Diffusion of active agent through cell wall and attack the enzymes group whose destruction results in death to the organism. Hence microorganisms are not immune to chlorine
Factors affecting chlorine efficiency:1.Concentration of Free Chlorine2.Contact time3.Temperature4.Types and concentration of organisms5.pH6.Contaminants
Chlorine Di-Oxide• Draw backs of chlorine can be over
come with help of Clo2 mainly in NH3 contaminated water.
• It can be produced on site as• 2NaClO2 + Cl2 2 ClO2 + 2NaCl• ClO2 does not react with ammonia
thus gets effective in controlling microorganisms.
Limitation of Chlorine• Chlorine reacts with organics, hence
exerts a chlorine demand leading to higher chlorine consumption and non-maintenance of residual
• Difficult to handle and dose• Efficacy of chlorine is pH dependent• Chlorine is highly corrosive
Chlorine Reactivity1. With Ammonia- HOCl + NH3 NH2Cl (mono chloramines) +
H2O
- NH2Cl + HOCl NHCl2 (dichloramine) + H2O
- NHCl2 + HOCl NCl3 (trichloramine) + H2OIt means one ppm of ammonia can react with 3 ppm of chlorine, hence will increase chlorine demand
Chlorine Reactivity2. With Organic Nitrogen• Proteins hydrolyzes to amino
acids.• Chlorination chemistry of these
are extremely complex• Because of various hydrolysis
products.• Finally the products are mono/di-
chloramines.
Chlorine Reactivity3. With Urea• Urea hydrolyzes with nitrogen breaking down to
ammonia in presence of urease enzyme. • If the hydrolysis lacks this enzyme, the
formation of NH3 is greatly inhibited. • If significant quantity of urea-N is present and
hydrolysis proceeds at slow rate, unstable residue could result.
• Urea-N would then be reservoir for the production of ammonia.
Chlorine Reactivity4. Inorganic Carbon:C + Cl2 + 2H2O 4 HCl + CO2
This takes place in dechlorination with granular activated carbon.
5. Cyanide:At alkaline pH 8.5 or higher,2Cl2 + 4NaOH + 2NaCN 2NaCNO +
4NaCl + 2H2O
Chlorine Reactivity6. Hydrogen sulphide:H2S + 4Cl2 + 4H2O H2SO4 + 8HCl Here 8.3 ppm of chlorine is required
to oxidize 1 ppm of H2S.
Chlorine Reactivity
9. Hydrocarbons:
Hydrocarbons create high chlorine demand due to high oxidisable organics.
Chlorine Dioxide Application Technology
Chlorine DioxideIntroduction• Strong oxidizer• Not a halogen• Selective reactivity• Generated on site• pH independent• Low capital requirements
Chlorine Dioxide (Contd.)• Rapid acting. Lower contact time for micobiological kill compared to chlorine
• Less corrosive compared to chlorine• Does not hydrolyse to form acid• Does not react to form chloramines• Does not form trihalomethanes with
organic matter like chlorine• Does not produce any chlorinated
compounds
Chlorine Dioxide Mechanism of Kill
Disruption of protein synthesis or lysing of cell
No resistivity by organisms
Chlorine Dioxide Effectiveness at Various
pHs
0102030405060708090
100
4 5 6 7 8 9 10
% Active
pHLb./Equal Performance 1
Chlorine DioxideSafety Considerations
Not handled as a gas Typical use is < 0.3% solutions On-site generator is required
Selection criteria of suitable oxidant• Efficacy • Safety handling• Regulatory reporting• Process contamination• pH dependence
Safety
Sodium Hypochlorite
Sodium BromideChlorine DioxideOzoneBCDMHChlorine Gas
Best
Worst
Reporting Requirements
Chlorine DioxideHypochloriteBromine CompoundOzoneChlorine Gas
Least
Greatest
Performance in Contaminated Systems
Chlorine DioxideOzoneBromine
CompoundsChlorine GasSodium
Hypochlorite
Best
Worst
Performance at Elevated pH
OzoneChlorine DioxideBromine
CompoundSodium
HypochloriteChlorine Gas
Best
Worst
Best Alternative• CHLORINE is still a widely used oxidant
* Inexpensive, historically established, being phased out• HYPOCHLORITE is cheapest alternative
* Similar performance to chlorine, degradation is problem• BROMINE CHEMISTRY, halogen alternative
* Better performance, can be costly, pH dependent• CHLORINE DIOXIDE, non-halogen alternative Cost-effective
broad spectrum, safely fed, pH independent, non-chlorinating agent
• OZONE, New Approach* Capital intensive, strong oxidant, no chemicals
Chlorine Dioxide Generation
Chlorine DioxideAdvantages/Benefits• Gas dissolved in
water• Strong oxidizer• Not a halogen• Selective reactivity
Chlorine DioxideAdvantages/Benefits• Generated on-site• Rapid acting• pH independent• Low capital requirements
Physical Characteristics
Color : Yellow-green
State : Gas
Odor : Similar to chlorine
Solubility: 2.9 gr/L
ClO2 GeneratorGeneration Methods
Chlorine Gas Method Three Pump Method
Precursor Source
WaterInlet
Chlorine
1
2 3
456
7
8
9
10
11
12
13
48"H x 42"W x 17"D
14
ClO2
15
1. Electric Control Box2. Flow Indicator (GPM)3. Hand/Off/Auto Switch4. Ball Valve5. Solenoid Valve6. Pressure Gauge7. In-line Flowmeter8. Ball Check Valve9. Chlorine Eduction10. Chlorine Solenoid Valve11. Chlorine Rotameter12. Precursor Pump13. ClO2 Generator14. Emergency Shutdown Switch15. Loss Of Chlorine Switch
ClO2 GeneratorChlorine Gas Method
ClO2 GenerationGaseous Chlorine Method
2NaClO2 + Cl2 2ClO2 + 2NaCl Sodium Chlorine Chlorine Sodium Chlorite Dioxide Chloride
ClO2 GenerationThree Pump Method
2NaClO2 + NaOCl + 2HCl Sodium Sodium Hydrochloric Chlorite Hypochlorite Acid
2ClO2 + 3NaCl + H2O Chlorine Sodium Water Dioxide Chloride
Hydrochloric Acid SourceSodium Hypochlorite Source
Precursor Source
1
2 3
456
7
8
9
10
48"H x 42"W x 17"D
11
ClO2
9 9WaterInlet
1. Electric Control Box2. Flow Indicator (GPM)3. Hand/Off/Auto Switch4. Ball Valve5. Solenoid Valve6. Pressure Gauge7. In-line Flowmeter8. Ball Check Valve9. Chemical Pumps10. ClO2 Generator11. Emergency Shutdown Switch
ClO2 GeneratorThree Pump Method
ClO2 GeneratorGeneration MethodThree Pump Method
Advantages• Higher
Capacity• High Back-
Pressure Capacities
• Higher Turndown
• No Chlorine Gas Necessary
Disadvantages• Slightly Higher
Cost• Additional
Chemical Storage
• Incompatible Chemicals
Typical ClO2 DosagesRendering Odor Control :2-10 ppmCooling Water Treatment : 0.1-0.5
ppmFood Processing : 2-10 ppmPaper Mill Slime Control :0.25-0.45 lb
ClO2/ton paper
Sodium Chlorite PrecautionsDO NOT allow solution to dry.
DO NOT mix with any other chemicals.
DO NOT use wooden pallets or paddles.
DO NOT wear leather or cloth external clothing.
Normal Shutdown Procedure• Turn operating switch to “Off”• Water flush occurs briefly• Drain unit• If chlorine used, close valve• Drain and flush all chemical
systems
Equipment SiteSurvey Location• Well-ventilated area• Eyewash/shower near generator• Eyewash/shower near bulk
storage• Washdown water source available• Approved drain• Well lighted
Monitoring Tools• Corrosion coupons • Deposit monitor - visual indication of deposit
formation • Biofouling monitor - indicate loss of pressure
due to biofilm • TBC and SRB dip slides• Test heat exchangers• ORP meters • Site Management • Daily reporting
Corrosion Monitoring by Coupons Method
• Corrosion Rate (MPY) = coupons wt loss in gms*365*1000/ Area of coupon in cm2*density of coupon in (gm/cm3)*Exposure period in days*2.54
Also we know that 1 Miles = 0.001 inch =0.0254 mm
Means if corrosion rate is 3 MPY will cause the metal loss (tube thickness reduction) by 0.0762 mm per year.
THANK YOUfor any types of queries
please contact toPrem Baboo
Sr. Manager(Prod)National Fertilizers Ltd, India
Designer for Plant & equipment'[email protected]@nfl.co.in
+919425735974