Lecture 6: Softening

Similar documents
REMOVAL OF HARDNESS BY PRECIPITATION

Lafayette College Department of Civil and Environmental Engineering

Hard water. Hard and Soft Water. Hard water. Hard water 4/2/2012

Slide 1. Slide 2. Slide 3. Hardness. Concentration is. What s the concentration of red triangles? What s in your pipes? 500 ml

Lecture 1: Introduction

TEAMS Competition 2017 Scenario # 2. Water Treatment. From Potentially Poisonous to Potable through Purification

ENVIRONMENTAL ENGINEERING LECTURE 3: WATER TREATMENT MISS NOR AIDA YUSOFF

2. WATER. Wet Processing I (Pretreatment)

Hardness of Water. (c) Dr. Payal Joshi

Environmental Chemistry - Water HL

FilterSorb SP3 Treatment Method: Part II

WATER CONDITIONING & ENVIRONMENTAL PROTECTION

Chemical Precipitation

Water Technology. 2C 17 H 35 COONa + CaCl 2 (C 17 H 35 COO) 2 Ca (scum) + 2NaCl 2C 17 H 35 COONa + MgSO 4 (C 17 H 35 COO) 2 Mg(scum) + Na 2 SO 4

Department of Civil Engineering, IIT Delhi (India) CVL722 (Sem1, ) (Dr. Arun Kumar;

Sodium Peroxides (Na 2 O 2 ): Preparation: It is formed by heating the metal in excess of air or oxygen at 300, which is free from

Interpreting Irrigation Water Quality Reports

SRI RAMAKRISHNA INSTITUTE OF TECHNOLOGY COIMBATORE First Year BE/B.TECH ( ) Engineering Chemistry- I

CEE 370 Environmental Engineering Principles

Hardness Evidence Search

GEOCHEMICAL MODULE FOR AMDTreat

Q1. The chemical compositions of two samples of hard water, A and B, are shown in the table.

Water Quality Chem Solution Set 7

CEE 370 Environmental Engineering Principles

Process water quality factors

BOILER FEED WATER AND ITS TREATMENTS

Lecture 18. Soil Acidity, Alkalinity, and Socidity

Alkalinity: An Important Parameter in Assessing Water Chemistry

ALKALINITY ADDITION: THEORY AND BEST PRACTICE

Treatment Technologies

UNIT-II: WATER TECHNOLOGY

Chapter six. Precipitate is separated by filtration, washing,drying and finally is accurately weighed.

Evaporative Condenser Passivation. Cameron Klein Strand Associates, Inc.

UNIT-I WATER TECHNOLOGY

By C.F. Chubb Michaud, CWS-VI

We have softening plant for boiler so water treatment chemicals is not require. We used 90 % condensate water so no need of any chemicals treatment

APPLICATION OF REVERSE OSMOSIS IN TREATMENT OF WATER USED IN INDUSTRIAL COOLING CIRCUITS

Revolution. NON-Chemical Treatment. Technology. for Scale Control. 500 different Applications NON TOXIC FOR POLLUTION PREVENTION AND GREEN TECHNOLOGY

to water. You add 1 drop of phenolphthalein and the solution turns pink. This observation tells you Na 2

Irrigation Water Quality for B.C. Greenhouses

A Cost Effective Technique for Chemical Wastes Reduction in Lime Water Softening Process

1. The equation that represents the equilibrium in a saturated solution of Fe 2 (SO 4 ) 3 is.. The precipitate which forms first is

Advanced Water Treatment (DESALINATION) PART 1. Instructors : Dr. Yunes Mogheir Dr. Azzam Abu Habeeb. Page 1

Wastewater Treatment of high total dissolved solids and acidity in Cerro de Pasco mining wastewater

DETERMINATION OF HARDNESS IN A WATER SAMPLE

1. Scaling. H.O.: H-5/21, KRISHNA NAGAR, DELHI Tel.: , Fax:

USING ALUMINUM REFUSE AS A COAGULANT IN THE COAGULATION AND FLIOCCULATION PROCESSES

Solubility Equi librium Ksp. Chapter 17 Sections

Equilibria of Slightly Soluble Ionic Compounds: We lied to you in chem 115

Water. Chapter 2.1 INTRODUCTION 2.2 SOURCES OF WATER 2.3 IMPURITIES IN NATURAL WATER

Undesirable impurities in boilers. Maximum permissible Cycles of concentration (NC)

Water Quality. CE 370 Lecture 1. Global Distribution of Earth s s Water

WINTER 2012 EXAMINATION Subject Code: Model Answer Page No: 1/10

SOLUBILITY STUDY GUIDE- Multiple Choice Section

INDEX FRESH SEMINAR SERIES

UNIT I WATER TECHNOLOGY

5 WATER. (iii) Temporary hard water (iv) Permanent hard water

The Chemistry of Natural Waters

McIlvaine Hot Topic Hour Evaporation and Crystallization of FGD Wastewater. September 3, 2009

A. Yavich, Ph.D., P.E. Optimization Solutions Environmental, LLC Grand Rapids, MI

Unit 4 WATER 4.1 Occurrence and Physical Properties

Recirculating Hot Water Systems

*20GSD5201* Double Award Science: Chemistry. Unit C2 Higher Tier WEDNESDAY 15 JUNE 2016, AFTERNOON [GSD52] *GSD52* *G5802* TIME 1 hour 15 minutes.

ENGINEERING CHEMISTRY

Chapter 9 Systematic Equilibrium

Battling Dragonscale Thomas Coyne Coyne Chemical

UNIT-I WATER TECHNOLOGY

Purpose of this course. Optimization of Water Treatment Plant Operations

Exercise 6a. Balancing equations

PAPER MILL DEPOSIT CONTROL

Understanding Pretreatment. WesTech Engineering, Inc. Salt Lake City, Utah, USA

Produced Water Quality Limits for Irrigated Agriculture. Robert Flynn, Ph.D. Extension Plant Sciences, NMSU

Geology 627, Hydrogeology Review questions for final exam h t 1/ 2

Geological Storage of CO2. Evaluating the Risk of Leakag! Injection & Leakage

Mark the Following Statements as True or False

Quantitive Chemistry Question paper

Evaluation of Alternate Process Chemistries for the Removal of Arsenic and Fluoride from Industrial Wastewater

1. Bugs. Toxic materials Solids and color. 3. Solids and color 4. All above. 1. Water treatment overview:

Topic 2.6 GROUP 2, THE ALKALINE EARTH METALS

TECHNOLOGY OF WATER UNIT II. a) Turbidity

Assessment of Water Quality Parameters of Samalkha

Tutorial 3 Unit 3 - Solubility

Acid Mine Water Reclamation using the ABC Process. Abstract. Introduction

Hardness Removal from Groundwater by Synthetic Resin from Waste Plastics

FACTFILE: GCE CHEMISTRY

Adapted from: An original Creek Connections activity. Creek Connections, Box 10, Allegheny College, Meadville, Pennsylvania

Clear Solutions from your Culligan Man for Complicated Water Problems

Thermal decomposition. Metal carbonates

Chapter 17 Solubility and Complex Ion Equilibria

ANQUE High rate crystallisation processes: Application to softening and removal of scaling compounds for industrial wastewater re-use

DRINKING WATER - LAB EXPERIMENTS LAB EXPERIMENTS. Softening

OC30 Conduct a qualitative experiment to detect the presence of dissolved solids in water samples, and test water for hardness (soap test)

Streamwater Chemistry

# 524 Compare Drinking and Bottle Water Sciencefaircenter.com Study Kit

CEE 370 Fall Homework #8

ENV 4417: WATER QUALITY AND TREATMENT. University of South Florida Civil & Environmental Eng.

WATER THE PROBLEM OF PURITY

Alternative Approaches to Design Evaporator and Crystallizer Systems using OLI Software


was a better adsorbent for NOM than calcium carbonate (CaCO 3 ) (which precipitates at

Transcription:

Islamic University of Gaza Environmental Engineering Department Water Treatment EENV 4331 Lecture 6: Softening Dr. Fahid Rabah 1

6.1 Definition of hardness: A. Hardness is the term often used to characterize a water that : Dose not form a foam or lather well and cause soap scum Ca 2+ + (Soap) Ca(Soap) 2(s) (soap scum) This increase the amount of soap needed for washing cause scaling on pipes and hot boilers. cause valves to stick due to the formation of calcium carbonate crystals leave stains on plumbing fixtures 2

Figure 6.1: Scaling due to calcium and magnesium precipitation 3

6. Hardness and Softing in water Treatment B. Hardness is defined as the sum of the divalent metal cations (in consistent units) existing in water such as : Ca 2+, Mg 2+, Fe 2+, Mn 2+ Practically most hardness is due to Ca 2+, Mg 2+ ions (the predominant minerals in natural waters) C. Total Hardness = Ca 2+ hardness+ Mg 2+ hardness where the concentration of each ion is in consistent units such as mg/l as Ca CO 3, or meq/l. 4

D. Hard water classification Description Hardness range (mg/l as CaCO 3 ) Soft 0-75 Moderately hard 75-100 Hard 100-300 Very hard > 300 5

E. Formation of Hardness Subsoil CO 2 +HO 2 H 2 CO3 Precipitation Topsoil Limestone CaCO 3(s) + H 2 CO 3 Ca(HCO 3 ) 2 M CO H CO M (HCO ) MgCO 3(s) + H 2 CO 3 Mg(HCO 3 ) 2 6

F. Carbonate and non carbonate Hardness Carbonate Hardness ( CH) Ca 2+, Mg 2+ associated with HCO 3, CO 2 3 Often called "temporary hardness" "because heating the water will remove it. When the water is heated, the insoluble carbonates will precipitate and tend to form bottom deposits in water heaters. Non Carbonate Hardness ( NCH) Ca 2+, Mg 2+ associated with other ions, Cl, NO 3, SO 4 2 NCH = TH CH 7

F. Hardness Units Total Hardness = (Ca 2+ + Mg 2+ ) The hardness unit is the same as that consistent unit used for both of the above ions. The most used units are: EW of CaCO 3 mg/l as CaCO 3 mg/l as species EW of species Where, EW = equivalent weight Species = Ion or Rdi Radical or Compound Radical: such as CO 2 3, SO 2 4 Compounds: such as CO 2, CaSO 4 8

MW For radicals and EW Electrical l Charge compounds MW EW For ions Valance MW = molecular weight of the Species Example 3.1 : a) Find the EW of Mg 2+ that has a concentration of 10 mg/l as the ion in water. b) Find the EW of CaCO 3 c) find concentration of Mg 2+ as mg/l CaCO 3. a) Finding the EW for Mg 2+ : g MW 24.3 mole Valance (n) EW mg MW 24.3 mmole 2 eq 2 meq mole MW Vl Valance Valance (n) mmole 24.3 mg 1 EW.[ mmole 2 meq/mmole ] EW 12.15 mg meq 9

b) Finding the EW for CaCO 3 : MW 100 g mole MW 100 mg mmole Electrical charge (n) 2 eq mole Electrical charge 2 meq mmole MW 100 mg 1 EW EW.[ Electrical Charge mmole 2 meq/mmole D) Finding the Mg 2+ concentration as CaCO 3 : ] EW 50 mg meq EW of CaCO 3 mg/l as CCO CaCO 3 mg/l as species EW of species /L 3 2+ Mg 2+ conc. (Mg2 ) in mg/l as CaCO 3 10 mg/l as Mg 2 50 mg/meq 12.1515 mg/meq 41.15 mg/l as CaCO 3 10

Ground Water Rapid Mixing Flocculation Sedimentation Recarbonation Filtration Disinfection Storage Distribution Figure 6.2: Softening Treatment Plant Single stage softening 11

6.2 Relation between Alkalinity and hardness: A. Definition of Alkalinity Alkalinity is a very important parameter in water chemistry and related very closely to hardness and softening process. The following equation is used to measure the alkalinity in water: Alkalinity li it = (HCO 3 ) + (CO 2 3 ) + (OH ) (H + ) Where the concentrations are in meq/l or mg/l as CaCO 3 Usually the (OH ) and (H + ) are negligible. The relation between the alkalinity species is given by the following three equations: 10-10.33 2 [H ][CO 3] 10-14 H OH [HCO3-] ph H 10,, Where the concentrations are moles/ L in these three equations 12

Various Forms of alkalinity and CO 2 relative to ph in water at 25 o C. 13

Example 6.1: A sample of water having a ph of 7.2 has the following concentrations of ions Ca 2+ Mg 2+ Na + K + HCO 3 SO 4 2 Cl 40 mg/l 10 mg/l 11.8 mg/l 7.0 mg/l 110 mg/l 67.2 mg/l 11 mg/l Construct a bar chart of the ions in term of mg/l CaCO 3 Calculate the TH, CH, NCH, Alkalinity 14

Example 6.1: Ion Conc. M.W. n Eq. Wt. Conc. Conc. mg/l mg/mmol mg/meq meq/l mg/l as CaCO 3 Ca 2+ 40.0 40.1 2 20.05 1.995 99.8 Mg 2+ 10.0 24.3 2 12.15.823 41.2 Na + 11.8 23.0 1 23.0.51 25.7 K + 70 7.0 39.1 1 39.1.179 895 8.95 - HCO 3 110.0 61.0 1 61.0 1.80 90.2 2- SO 4 67.2 96.1 2 48.05 140 1.40 69.99 Cl - 11.0 35.5 1 35.5.031 15.5 15

Check The ionic balance: (cations) = (anions) 175.6 = 175.6 mg/l as CaCO 3 O.K 3.51 = 3.23 meq/l OK O.K Note: (error in the range of ± 10% is accepted) Note: one check is enough ( either as {mg/l as CaCO3 } or as {meq/l} ) Total Hardness = (Ca 2+ ) + (Mg 2+ )= 99.8 + 41.2 TH =141 mg/l as CaCO 3 or TH= 1.995 + 0.823 = 2.818 meq/l 16

Alkalinity = (HCO 3 ) + (CO 3 2 ) + (OH ) (H + ) a. Since ph = 7.2 [H + ] = 10 ph = 10 7.2 mole/l = 10 7.2 g/l b. 10 g H eq/l 1g/eq -7.2 /L H 10-7.2 eq/l 72 10-14 H OH -14-7.2 10 10 OH -6.8-6.8 OH 10 mole/l 17*10 g/l = -6.8 68 OH 10 mole/l -6.8 17*10 g OH /L - eq/l OH 17 g/eq C. (HCO 3 ) = 1.80 meq/l = 1.80 *10 3 eq/l from this example calculations as in the table. g/l as HCO = * = * *10 3 = * 3 3 EW eq/l (61 g/eq) 1.80 g/l 109.8 10 g/l [HCO 3 ] = (109.8 * 10 3 g/l)/(61g/mole) = 1.80 *10 3 mole/l 10-6.8 eq/l 17

d. Find thecarbonate concentration: 10-10.33 2 [H ][CO 3] [HCO3-] -7.2-10.33 10 x[co 10-3 1.8 x 10 [CO 2 3 ]= 1.33 x 10 6 mole/l = 79.8 x 10 6 g/l -6 79.8*10 g /L CO 2 = 2.66 x 10 6 eq/l 3 in eq/l 30 g/eq 2 3 ] Alkalinity = (1.80 x 10 3 3) + (2.66 x 10 6 6) + 10 6.8 6 8 10 7.2 7 2 = 1.801 x 10 3 3 eq/l Alkalinity = 1.801 x 10 3 x 1000 x 50 = 90.1 mg/l as CaCO 3 Note: it is clear that the most effective form of alkalinity is bicarbonate, this is always true when the ph is 8.3 or less. 18

Carbonate Hardness the portion of the hardness associated with carbonate or bicarbonate Alkalinity = 90.1 mg/l as CaCO 3 TH = 141 mg/l as CaCO 3 CH = 90.2 mg/l as CaCO 3 Non carbonate Hardness: NCH = TH CH = 141 90.1= 50.9 mg/l as CaCO 3 19

Construct the bar chart of the ions in term of mg/l CaCO 3 TH 0.00 99.8 141 166.7 175.6 Ca 2+ Mg 2+ Na + K + HCO 3 SO 2 4 Cl 0.0 CH 90.2 NCH 160.1 175.6 CaSO 4 MgSO 4 Na 2 SO 4 NaCl KCl Note: the chemicals at the lower line of the bar graph is called the hypothetical combination of positive and negative ions in the water sample 20

6.3 Softening definition: a) Softening is the chemical processes in which hardness causing ions ( Ca 2+, Mg 2+ ) are removed from water ether completely or partially. b) Softening may be a chivied by chemical precipitation using the Lime Soda Ash method or by ion exchange. c) In the chemical precipitation method the objective is to produce CaCO 3 and Mg(OH) 2 : Ca 2+ + CO 2 3 2CaCO 3() 3(s) Mg 2+ + 2OH Mg(OH) 2(s) These tworeactions are achieved by the addition of Lime [Ca(OH) 2 ] and Soda ash [ Na 2 CO 3 ] as will be shown. 21

f) A common water treatment goal is to provide a water with a hardness in the range of 75 to 120 mg/l as CaCO 3 g) To precipitate CaCO 3 and Mg(OH) 2 we need to raise the ph to 10.3 by the addition of Lime [Ca(OH) 2 ]. The addition of the OH will convert HCO 3 to CO 2 3 h) To precipitate Mg(OH) 2 we need to raise the ph to 11 by the addition of Soda ash [ Na 2 2 CO 3 ]. This will add the CO 32 ion needed to react with the remaining Ca 2+ i) Some of the added lime [Ca(OH) 2 ] is consumed to remove CO 2 which is necessary to raise the ph. 22

6.4 Chemistry of Lime Soda Ash Softening softening reactions Neutralization of carbonic acid [To raise the ph we need first to neutralize any acid in the water] CO 2 + Ca(OH) 2 CaCO 3(s) + H 2 O Precipitation of CH due to calcium: [To raise the ph to 10.3 all the HCO 3 is converted to CO 3 2 ] Ca 2+ + 2HCO 3 + Ca(OH) 2 2CaCO 3(s) + 2H 2 O Precipitation of CH due to magnesium [To raise the ph to 11 add more lime] Mg 2+ + 2HCO 3 + Ca(OH) 2 Mg 2+ + CO 2 3 + CaCO 3(s) + 2H 2 O Mg 2+ + CO 2 32 + Ca(OH) 2 MgOH 2(s) + CaCO 3(s) 23

6.4 Chemistry of Lime Soda Ash Softening Removal of NCH due to calcium Ca 2+ + SO 4 2 + Na 2 CO 3 CaCO 3(s) + 2Na + + SO 4 2 Ca 2+ + 2Cl 1 + Na 2 CO 3 CaCO 3(s) + 2Na + + 2Cl 1 Removal of NCH due to magnesium Mg 2+ + Ca(OH) 2() 2+ 2 MgOH 2(s) + Ca Ca 2+ + Na 2 CO 3 CaCO 3(s) + 2Na + 24

6.4 Chemistry of Lime Soda Ash Softening Softening process limitations: 1. Lime Soda softening cannot produce a water completely free of hardness because of the solubility of CaCO 3 and Mg(OH) 2, limitations of mixing and reaction time. 2. Thus, the minimum calcium hardness that can be achieved is 30 mg/l as CaCO 3, the minimum Magnesium hardness that can be achieved is 10 mg/l as CaCO 3, this gives a minimum hardness of 40 mg/l as CaCO 3. 3. However, normally the water is treated to give a hardness in the range of 75 to 120 mg/l as CaCO 3. 4. An Excess lime beyond the stoichiometric amount is usually added to remove Mg 2+ hardness. The minimum excess lime is usually 20 mg/l as CaCO 3, maximum excess lime is 62.5 mg/l as CaCO 3 (1.25 meq/l). 5. Mg 2+ in excess of 40 mg/l as CaCO 3 is not desired as it forms scale in water heaters. Mg 2+ is expensive to remove, so we only remove Mg 2+ in excess of 40 mg/l as CCO CaCO 3. 25

6.4 Chemistry of Lime Soda Ash Softening Chemicals requirements: According to the softening chemical reactions: Lime is added at the ratio of 1:1 for each carbonate hardness compound except for Mg(HCO 3 ) the ratio is 2:1 [i.e. 2 lime for each 1 Mg(HCO 3 ) ]. Lime is also added at the ratio of 1:1 for each Magnesium NCH compound such as MgSO 4 Soda ash is added at the ratio of 1:1 for each Magnesium or Calcium NCH compound such as MgSO 4, and CaSO 4. CO 2 needed is 1:1 ratio with the excess lime added, and 1:1 ratio with CaCO 3 remaining after softening, 2:1 ratio with Mg(OH) 2 remaining after softening. The units of the chemicals are either in meq/l or mg/l CaCO 3 Example 6.2 illustrates the chemical requirements calculations. 26

6.5 Excess Lime Softening example Example: 6.2 A water with ihthe ionic i characteristics i shown below bl is to be softened to the minimum possible hardness by lime soda ash excess lime process. Calculate the required chemical quantities in meq/l. Draw a bar diagram of the softened water. Assume that a residual of CaCO 3 of 0.60 meq/l and a residual of Mg(OH) 2 of 0.20 meq/l will remain in the softened water. 3.4 6.4 7.4 0.6 CO 2 Ca 2+ HCO 3 Mg 2+ Na 2+ SO 2 4 0.00 4.9 7.4 27

Example: 6.2.. continued Solution: Lime = 0.6+3.4+ 2(4.9 3.4)+ 4) (6.4 4.9)+ 4 excess lime = 8.5 +1.25 = 9.75 meq/l Soda Ash = 6.4 4.9 = 1.5 meq/l ( to remove NCH, MgSO 2 4 ) Na + : The addition of soda ash adds to the water an equal amount of Na +. Since we added 1.5 meq/l soda ash, this will add 1.5 meq/l Na + The original concentration existing in the raw water is 1.0 meq/l. Total Na + = 1 + 1.5 = 2.5 meq/l Na +. 28

Example: 6.2.. continued 0.00 0.6 0.8 3.33 Ca 2+ Mg 2+ Na 2+ CO 3 2 HO SO 4 2 0.6 0.8 3.3 Bar graph of the softened water 29