Coagulation in Industrial water Treatment

Slides:



Advertisements
Similar presentations
CalARP - Examination of Chemical Processes: Drinking Water Treatment
Advertisements

CE Lab Jar Test.
CE 370 Sedimentation.
Definition and Measurement of Colloids
8.9 Stability and coagulation of colloids
Coagulation and Flocculation in Water Treatment
Coagulation and Flocculation at Water Treatment Plants
Nutrient Removal Project: Chemical Phosphorus Removal Jill Crispell, Stephanie Wedekind, Sarah Rosenbaum.
Iron and Aluminum Compounds for Removing Phosphorus and Turbidity from Pond Waters Claude E. Boyd, Puan Pengseng and Suthira Soongsawang Department of.
Chemical Treatment Processes of Industrial Waste
TREATMENT OF WATER The available raw water has to be treated to make it fit. It should satisfy the physical, chemical and bacteriological standards. The.
Estuarine Chemistry/Physical: Estuaries are where rivers meet the sea - the exact nature of the chemical processes occurring in an estuary generally depends.
Surface Water Treatment Plant
Coagulation CE 547. Overview Turbidity in surface waters is caused by colloidal clay particles. Color in water is caused by colloidal forms of Fe, Mn,
Coagulation and Flocculation
You are from Utah if….. 1. You've never met any celebrities. 2. Your idea of a traffic jam is ten cars waiting to pass a tractor on the highway. 3. "Vacation"
Coagulation and Flocculation
SOIL CHEMISTRY SOIL pH A measure of the degree to which the soil is Acidic or Basic; also known as... Soil Reaction.
E NVIRONMENTAL E NGINEERING 441 Lecture 5: Water Treatment (2) Coagulation and flocculation Philadelphia University Faculty of Engineering Department of.
Particle Settling Velocity Put particle in a still fluid… what happens? Speed at which particle settles depends on: particle properties: D, ρ s, shape.
How nutrients, soil particles and chemistry fit together
Characterization of Al-Humic Complexation and Coagulation Mechanism Removal of natural organic matter (NOM) by coagulation using metal coagulants (aluminium.
Cumulative Final Exam Review Jeopardy Waterworks Operations III WQT 134 Waterworks Operations III WQT 134.
Coagulation Chemistry: Effects on the Acid/Base Balance Via chemical equilibrium reactions, consumption of OH  in the precipitation step has a domino.
Jar Testing Coagulation Dosage Water Treatment Plants
Conventional Surface Water Treatment for Drinking Water.
Monroe L. Weber-Shirk S chool of Civil and Environmental Engineering Water Treatment Plant Reflections alum Flocculation Clear Well Sedimentation.
B. Corrosion, C. Coagulation and flocculation
8.9 Stability and coagulation of colloids
Coagulation: Purpose u Removal of turbidity –historically the reason for coagulation u Removal of natural organic matter –more recently of importance u.
Surface Water Treatment Plant. Fig 4-8: Flow Diagram of conventional surface water treatment plant (“filtration plant”)
Introduction to Environmental Engineering Code No. (PE389) Lec. 5 and 6.
Soil Buffering and Management of Acid Soils. pH pH = - log (H + ) If (H + ) = 1 x mol/L (H + ) = mol/L pH = - log (1 x ) pH = - (-3)
BCE Environmental Engineering Water Treatment Mdm Nur Syazwani binti Noor Rodi.
PHOSPHORUS REMOVAL FOR LAGOON OPERATORS WHY THE CONCERN OVER P.
Coagulation/Flocculation and Jar Testing
IV. Water Chemistry A. pH, hardness, and other ionic compounds and gases affecting water quality.
1 Waste Treatment, Chemical ENVE Why Treat Waste Have a RCRA Waste –TSDS –Treat instead of disposal, landfill –Treat before disposal Or treat in.
Tertiary Filtration.
Water Sources and Quality. Water Sources and Main Characteristics Groundwater (deep/shallow wells) – Not exposed to pollution but once polluted, restoration.
COAGULATION CHEMISTRY Particle sizes and nomenclature How a coagulant works Characteristics of typical coagulants Fitting the right coagulant to a sourcewater.
Spring, 2012 Session 3 – General Chemistry Pt 1.  Definition of terms  Chemical formulas  Chemistry background  Reactions  Equilibrium and law of.
Chapter 15: Water and Aqueous Systems
Jar Testing Machines – Not Just for Making High End Martinis Anymore Robin Lee, P.E.
The Drinking Water Treatment Process
Water Treatment CE 326 Principles of Environmental Engineering
Fractal Characteristics of Al-Humic Flocs A great contribution to the theory of floc structure was made in early 1980s by Mandelbrot who introduced the.
1 Lake water (raw) Flocculation Flash mix Gentle mix Quiescent condition Sedimentation Precipitation Coagulant.
Jar Test Presentation By Douglas Rittmann, Ph.D., P.E. Water/Wastewater Consultant To UTEP Lab Class On March 21, 2006.
ERT 417 Waste Treatment In Bioprocess Industry
Coagulation and Flocculation
CEE 160L – Introduction to Environmental Engineering and Science Lecture 9 Drinking Water.
Soil colloids. CHEMICAL PROPERTIES OF SOIL: Soil Colloids cat ion Exchange organic matter / Organic carbon Carbon –Nitroge ratio Soil fertility Soil reaction.
Engineered systems for wastewater treatment and disposal.
Course TEN-702 Industrial waste management unit-2
Lecture3_water purification, ChemEng, KKU, M.Thabuot MEMBRANE: Microfiltration Simple screening mechanism Pore size 0.01 μm - 10 μm  P  0.01 to 0.5 MPa.
CHEMICAL TREATMENT METHODS DONE BY: MAHASWARI JOGIA WASTE MANAGEMENT TECHNIQUES (HCE 24) SEMINAR ON:
Flocculation Prepared by Dr. Amal A. Aly.
Drinking-water Treatment
SEDIMENTATION 9/11/2018.
Q Chemical Mixers 1. Rapid mixers - for rapid chemical reactions where the reactant needs to be added efficiently 2. Flocculators - when different phases.
Mixing and flocculation
ENVE422: Wastewater Treatment Process Design
Sedimentation.
Flocculation and Coagulation
ENG421 (7c) – Coagulation and Flocculation
Jar Testing of Chemical Dosages
ENG421 (7ab) – Coagulation and Flocculation
Table (5.1): Particle size found in water treatment
5.7 Flocculation   Flocculation is the process of gentle and continuous stirring of coagulated water for the purpose of forming flocs through the aggregation.
Presentation transcript:

Coagulation in Industrial water Treatment J(Hans) van Leeuwen and Samir K Khanal 4/16/2017 water treatment

Why coagulation is needed Various sizes of particles in raw water Particle diameter Type Settling velocity mm 10 Pebble 0.73 m/s 1 Course sand 0.23 m/s 0.1 Fine sand 0.6 m/min 0.01 Silt 8.6 m/d 0.0001 (10 micron) Large colloids 0.3 m/year 0.000001 (1 nano) Small colloids 3 m/million year G r a v i t y s e t t l i n g Colloids – so small, gravity settling not possible Metal precipitates are usually colloidal 4/16/2017 water treatment

COAGULATION Size of colloids - light waves Brownian motion Stability of colloids Removal of colloidal substances from water 4/16/2017 water treatment

- Colloid Stability Colloid Destabilization H2O Colloid Colloids have a net negative surface charge Electrostatic force prevents them from agglomeration Brownian motion keeps the colloids in suspension - Repulsion Colloid - A Colloid - B Impossible to remove colloids by gravity settling Colloid Destabilization Colloids can be destabilized by charge neutralization : Positively charged ions (Na+, Mg2+, Al3+, Fe3+ etc.) neutralize the colloidal negative charges and thus destabilize them. With destabilization, colloids aggregate in size and start to settle 4/16/2017 water treatment

What is Coagulation? Coagulation is the destabilization of colloids by addition of chemicals that reduce the negative charges The chemicals are known as coagulants, usually higher valence cationic salt (Al3+, Fe3+ etc.) - Rapid mixing is required to disperse the coagulant throughout the liquid 4/16/2017 water treatment

FORCES ACTING ON COLLOIDS 4/16/2017 water treatment

Aluminum sulfate: Al2(SO4)3.14 H2O Relative coagulating power of cations Na+ = 1; Mg2+ = 30 Al3+ > 1000; Fe3+ > 1000 Typical coagulants Aluminum sulfate: Al2(SO4)3.14 H2O Polyaluminum Chloride (PAC): Al2(OH)3Cl3 Iron salt- Ferric Sulfate: Fe2(SO4)3 Iron salt- Ferric Chloride: Fe2Cl3 4/16/2017 water treatment

Aluminum Chemistry Al2(SO4)3.14 H2O  2Al(OH)3+ 8H2O + 3H2SO4-2 Al2(SO4)3.14 H2O + 6HCO3-  2Al(OH)3+ 6CO2 + 14H2O + 3SO4-2 With alum addition, what does happen to water pH? (Optimum pH: 5.5 – 6.5) 1 mole of alum consumes 6 moles of bicarbonate (HCO3-) If alkalinity is not enough, pH will reduce greatly due to sulfuric acid formation. Lime or sodium carbonate may be needed to neutralize the acid. 4/16/2017 water treatment

Alkalinity calculation If 200 mg/L of alum to be added to achieve complete coagulation. How much alkalinity is consumed in mg/L as CaCO3? Al2(SO4)3.14 H2O + 6HCO3-  2Al(OH)3+ 6CO2 + 14H2O + 3SO4-2 594 mg 366 mg 594 mg alum consumes 366 mg HCO3- 200 mg alum will consume (366/594) x 200 mg HCO3- = 123 mg HCO3- Alkalinity in mg/L as CaCO3 = 123 x (50/61) = 101 mg/L as CaCO3 4/16/2017 water treatment

Exercise: Alkalinity calculation Iron Chemistry FeCl3+ 3HCO3-  Fe(OH)3+ 3CO2 + 3Cl- With Iron salt addition, what does happen to water pH? (Wider pH range of: 4 – 9; Best pH range of 4.5 – 5.5) 1 mole of FeCl3 consumes 3 moles of bicarbonate (HCO3-) If alkalinity is not enough, pH will reduce greatly due to hydrochloric acid formation. Lime or sodium carbonate may be needed to neutralize the acid. Lime is the cheapest one. Exercise: Alkalinity calculation If 200 mg/L of ferric chloride to be added to achieve complete coagulation. How much alkalinity is consumed in mg/L as CaCO3? 4/16/2017 water treatment

Jar Tests The jar test – a laboratory procedure to determine the optimum pH and the optimum coagulant dose A jar test simulates the coagulation and flocculation processes Determination of optimum pH Fill the jars with raw water sample (500 or 1000 mL) – usually 6 jars Adjust pH of the jars while mixing using H2SO4 or NaOH/lime (pH: 5.0; 5.5; 6.0; 6.5; 7.0; 7.5) Add same dose of the selected coagulant (alum or iron) to each jar (Coagulant dose: 5 or 10 mg/L) Jar Test 4/16/2017 water treatment

Rapid mix each jar at 100 to 150 rpm for 1 minute. The rapid mix helps to disperse the coagulant throughout each container Reduce the stirring speed to 25 to 30 rpm and continue mixing for 15 to 20 mins This slower mixing speed helps promote floc formation by enhancing particle collisions which lead to larger flocs Turn off the mixers and allow flocs to settle for 30 to 45 mins Measure the final residual turbidity in each jar Plot residual turbidity against pH 4/16/2017 water treatment Jar Test set-up

The pH with the lowest residual turbidity will be the optimum pH Residual turbidity Versus pH Optimum pH: 6.3 4/16/2017 water treatment

Determination of optimum coagulant dose Fill jars Adjust pH of all jars at optimum (6.3 found from first test) while mixing using H2SO4 or NaOH/lime Add different doses of the selected coagulant (alum or iron) to each jar (Coagulant dose: 5; 7; 10; 12; 15; 20 mg/L) Rapid mix each jar at 100 to 150 rpm for 1 minute. The rapid mix helps to disperse the coagulant throughout each container Reduce the stirring speed to 25 to 30 rpm and continue mixing for 15 to 20 mins 4/16/2017 water treatment

This slower mixing speed helps promote floc formation by enhancing particle collisions which lead to larger flocs Turn off the mixers and allow flocs to settle for 30 to 45 mins Measure the final residual turbidity in each jar Plot residual turbidity against coagulant dose Coagulant Dose mg/L Optimum coagulant dose: 12.5 mg/L The coagulant dose with the lowest residual turbidity will be the optimum coagulant dose 4/16/2017 water treatment

Rapid Mixing (Coagulation) To uniformly mix the coagulant with colloidal matters present in raw water so as to bring about colloidal destabilization 4/16/2017 water treatment

How to achieve rapid mixing Horizontal baffled tank The water flows in a horizontal direction. The baffle walls help to create turbulence when the water hits the surface and thus facilitate mixing L W Plan view (horizontal flow) Vertical baffled tank The water flows in a vertical direction. The baffle walls help to create turbulence when the water hits the surface and thus facilitate mixing H L Isometric View (vertical flow) 4/16/2017 water treatment

Hydraulic Jump: Hydraulic Jump creates turbulence and thus help better mixing. Coagulant In-line flash mixing Mechanical mixing Back mix impeller flat-blade impeller Inflow Chemical feeding Chemical feeding Inflow 4/16/2017 water treatment

4/16/2017 water treatment

4/16/2017 water treatment

4/16/2017 water treatment

4/16/2017 water treatment

4/16/2017 water treatment

4/16/2017 water treatment

COAGULANT AIDS Other substances than coagulants used: - Clay minerals - Silicates Polymers Polymers are often either anionic or cationic to aid coagulation. Polymers also reinforce flocs 4/16/2017 water treatment

Typical layout of a water treatment plant Flocculation and its applications in water treatment                                                                                                                                                                                                                                                                                                                                               Typical layout of a water treatment plant 4/16/2017 water treatment