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5. EXPERIMENT ON DETERMINATION OF ALKALINITY OF WATER
AIM
To determine the alkalinity of given water sample
INTRODUCTION
Alkalinity is primarily a way of measuring the acid neutralizing capacity of water. In
other words, its ability to maintain a relatively constant pH.
The possibility to maintain constant pH is due to the hydroxyl, carbonate and
bicarbonate ions present in water.
The ability of natural water to act as a buffer is controlled in part by the amount of calcium
and carbonate ions in solution.
Carbonate ion and calcium ion both come from calcium carbonate or limestone.
So water that comes in contact with limestone will contain high levels of both2-
Ca++ and CO3 ions and have elevated hardness and alkalinity.
PRINCIPLE
The alkalinity of water can be determined by titrating the water sample with Sulphuric
acid of known values of pH, volume and concentrations. Based on stoichiometry of the
reaction and number of moles of Sulphuric acid needed to reach the end point, the
concentration of alkalinity in water is calculated.
When a water sample that has a pH of greater than 4.5 is titrated with acid to a pH 4.5
end point, all OH-, CO3 , and HCO32- will be neutralized.
For the pH more than 8.3, add phenolphthalein indicator, the colour changes to pink
colour. This pink colour is due to presence of hydroxyl ions.
If sulphuric acid is added to it, the pink colour disappears i.e. OH- ions are neutralized.
Then add mixed indicator, the presence of CO3
2- and HCO3
- ions in the solution
changes the colour to blue. While adding sulphuric acid, the color changes to red, this
color change indicates that all the CO3
2- and HCO3
- ions has been neutralized. This is
the end point.
MATERIALS REQUIRED
APPARATUS REQUIRED
1. Burette with Burette stand and porcelain title
2. Pipettes with elongated tips
3. Pipette bulb
4. Conical flask (Erlenmeyer Flask)
5. 250 mL Measuring cylinders
6. Standard flask
7. Wash Bottle
8. Beakers
CHEMICALS REQUIRED
1. Standard sulphuric acid
2. Phenolphthalein
3. Mixed Indicator
4. Bromocresol Green
5. Methyl Red
6. Ethyl alcohol
7. Distilled Water
-
2-
PRECAUTIONS
The following precautions should be observed while performing the
experiment:
1. Do not keep the indicator solution open since it contains the alcohol which tends
to evaporate.
2. The mixed indicator solution is containing dye in it; care should be taken so that it
is not spilled to your skin.
3. If it spills on your skin, the scar will remain at least for two to three days.
PROCEDURE
TESTING OF WATER SAMPLE
 Rinse the burette with 0.02N Sulphuric acid and discard the solution.
 Fill the burette with 0.02N sulphuric acid and adjust it to zero.
 Fix the burette in the stand.
 Using a measuring cylinder exactly measure 100 mL of sample and pour it into a
250 mL of conical flask.
 Add few drops of phenolphthalein indicator to the contents of conical flask. The
colour of the solution will turn to pink. This colour change is due to alkalinity of
hydroxyl ions in the water sample.
 Titrate it against 0.02N sulphuric acid till the pink color disappears. This indicates
that all the hydroxyl ions are removed from the water sample. Note down the titter
value (V1). The value of titration is mL .This value is used in calculating the
phenolphthalein alkalinity.
 To the same solution in the conical flask add few drops of mixed indicator. The
colour of the solution turns to blue. This colour change is due to CO3 & HCO3
ions in water sample.
 Continue the titration from the point where stopped for the phenolphthalein
alkalinity. Titrate till the solution becomes red. The entire volume (V2) of
sulphuric acid is noted down and it is accountable in calculating the total
alkalinity.
 The value of titration is mL.
 Repeat the titration for concordant values.
CALCULATION
TABLE
Table -1 Phenolphthalein Alkalinity:
Sl.No.
Volume of
Sample (mL)
Burette Reading (mL) Volume of
Sulphuric acid
(mL)
Initial Final
1.
2.
3.
Burette solution: Sulphuric Acid Solution
Pipette solution: Sample.
Indicator: Phenolphthalein Indicator.
End point: Disappearance of pink color.
Table - 2 Total Alkalinity:
Sl.No.
Volume of
Sample (mL)
Burette Reading (mL) Volume of
Sulphuric acid
(mL)
Initial Final
1.
2.
3.
Burette solution: Sulphuric Acid Solution
Pipette solution: Sample.
Indicator: Mixed Indicator.
End point: Appearance of Red color.
Specimen Calculation:
Volume of Sulphuric Acid = mL
Normality of Sulphuric Acid =
N Volume of Sample = mL
Equivalent weight of CaCO3 =
Phenolphthalein Alkalinity = (volume of H22SO4(V1)* Normality * 50 * 1000)
Volume of sample taken
To convert the sample size from mL to L, multiply the result by 1,000 mL/L to
convert the sample size from mL to L
Alkalinity as CaCO3 equivalent (mg/L) = X mg/L as CaCO3 equivalent
Total Alkalinity also came calculations
INTERPRETATION OF RESULTS
INFERENCE
Alkalinity is a measure of the capacity of water to neutralize acids. The
predominant chemical system present in natural waters is one where carbonates,
bicarbonates and hydroxides are present. The bicarbonate ion is usually
prevalent. However, the ratio of these ions is a function of pH, mineral
composition, temperature and ionic strength. Water may have a low alkalinity
rating but a relatively high pH or vice versa, so alkalinity alone is not of major
importance as a measure of water quality. Alkalinity is not considered detrimental
to humans but is generally associated with high pH values, hardness and excess
dissolved solids. High alkalinity waters may also have a distinctly flat, unpleasant
taste. Based on the testing, it is found that the alkalinity of the sample is 83 mg/L.
As per the provisional code, alkalinity should not exceed 200 mg/L for potable
water. For the fresh water alkalinity ranges between 20 – 100 mg/L. Alkalinity of
tested sample is within the limits specified in the standards. Hence the water
sample is fit for drinking.
EVALUATION
1. Alkalinity of water is an indication of
a) Base neutralizing capacity
b) Acid neutralizing capacity
c) Quantity of base present
d) Quality of base present
2. Mixed indicator is a combination of
a) Bromcresol Blue and Methyl Orange
b) Bromcresol Green and Methyl Red
c) Bromcresol Blue and Methyl Red
d) Bromcresol Green and Methyl Orange
3. Alkalinity is present due to all except .
a) Bromates
b) Phosphates
c) Silicates
d) Chlorides
4. Alkalinity is not caused by
a) Carbonates ions
b) Bicarbonates ions
c) Hydroxyl ions
d) Chloride ions
5. The phenolphthalein alkalinity is present then the pH of that water will be More than
a) 8.3
b) 9.3
c) 7.3
d) 6.3
6. Alkalinity of natural water is mainly due to the presence of .
a) Bicarbonates
b) Bromates
c) Phosphates
d) Silicates
7. The bicarbonate equivalence point normally occur at pH a)
a) 2.5
b) 3.5
c) 4.5
d) 5.5
8. What is ppm?
a) Parts per meter square
b) Parts per meter
c) Parts per million
d) Parts per millimeter
9. The normality of the acid used in the titration is .
a) 0.2 N
b) 0.02 N
c) 0.002 N
d) 2.0 N
10. A standard solution is a
a) Solution of accurately known strength
b) Solution of accurately known pH
c) Coloured solution
d) Colourless solution
ENVIRONMENTAL SIGNIFICANCE
Alkalinity is important for fish and aquatic life because it protects or buffers against
rapid pH changes. Higher alkalinity levels in surface waters will buffer acid rain and
other acid wastes and prevent pH changes that are harmful to aquatic life.
Large amount of alkalinity imparts bitter taste in water.
The principal objection of alkaline water is the reactions that can occur between
alkalinity and certain cations in waters. The resultant precipitate can corrode pipes
and other accessories of water distribution systems.
Wastewaters containing excess caustic (hydroxide) alkalinity are not to be
discharged into natural water bodies or sewers.
Alkalinity as carbonate and bicarbonate of saline water is very important in tertiary
recovery processes for recovering petroleum. Alkaline water offers better wetting to
the formation rock and improve oil release. As an additional benefit, ions that provide
alkalinity absorb on rock surfaces occupying adsorption sites and decrease the loss
of recovery chemical by adsorption.
The alkalinity value is necessary in the calculation of carbonate scaling tendencies of
saline waters.
The alkalinity acts as a pH buffer in coagulation and lime-soda softening of water.
In wastewater treatment, alkalinity is an important parameter in determining the
amenability of wastes to the treatment process and control of processes such as
anaerobic digestion, where bicarbonate alkalinity, total alkalinity, and any fraction
contributed by volatile acid salts become considerations.

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Exp 5

  • 1. 2- - 5. EXPERIMENT ON DETERMINATION OF ALKALINITY OF WATER AIM To determine the alkalinity of given water sample INTRODUCTION Alkalinity is primarily a way of measuring the acid neutralizing capacity of water. In other words, its ability to maintain a relatively constant pH. The possibility to maintain constant pH is due to the hydroxyl, carbonate and bicarbonate ions present in water. The ability of natural water to act as a buffer is controlled in part by the amount of calcium and carbonate ions in solution. Carbonate ion and calcium ion both come from calcium carbonate or limestone. So water that comes in contact with limestone will contain high levels of both2- Ca++ and CO3 ions and have elevated hardness and alkalinity. PRINCIPLE The alkalinity of water can be determined by titrating the water sample with Sulphuric acid of known values of pH, volume and concentrations. Based on stoichiometry of the reaction and number of moles of Sulphuric acid needed to reach the end point, the concentration of alkalinity in water is calculated. When a water sample that has a pH of greater than 4.5 is titrated with acid to a pH 4.5 end point, all OH-, CO3 , and HCO32- will be neutralized. For the pH more than 8.3, add phenolphthalein indicator, the colour changes to pink colour. This pink colour is due to presence of hydroxyl ions. If sulphuric acid is added to it, the pink colour disappears i.e. OH- ions are neutralized. Then add mixed indicator, the presence of CO3 2- and HCO3 - ions in the solution changes the colour to blue. While adding sulphuric acid, the color changes to red, this color change indicates that all the CO3 2- and HCO3 - ions has been neutralized. This is the end point.
  • 2. MATERIALS REQUIRED APPARATUS REQUIRED 1. Burette with Burette stand and porcelain title 2. Pipettes with elongated tips 3. Pipette bulb 4. Conical flask (Erlenmeyer Flask) 5. 250 mL Measuring cylinders 6. Standard flask 7. Wash Bottle 8. Beakers CHEMICALS REQUIRED 1. Standard sulphuric acid 2. Phenolphthalein 3. Mixed Indicator 4. Bromocresol Green 5. Methyl Red 6. Ethyl alcohol 7. Distilled Water
  • 3.
  • 4. - 2- PRECAUTIONS The following precautions should be observed while performing the experiment: 1. Do not keep the indicator solution open since it contains the alcohol which tends to evaporate. 2. The mixed indicator solution is containing dye in it; care should be taken so that it is not spilled to your skin. 3. If it spills on your skin, the scar will remain at least for two to three days. PROCEDURE TESTING OF WATER SAMPLE  Rinse the burette with 0.02N Sulphuric acid and discard the solution.  Fill the burette with 0.02N sulphuric acid and adjust it to zero.  Fix the burette in the stand.  Using a measuring cylinder exactly measure 100 mL of sample and pour it into a 250 mL of conical flask.  Add few drops of phenolphthalein indicator to the contents of conical flask. The colour of the solution will turn to pink. This colour change is due to alkalinity of hydroxyl ions in the water sample.  Titrate it against 0.02N sulphuric acid till the pink color disappears. This indicates that all the hydroxyl ions are removed from the water sample. Note down the titter value (V1). The value of titration is mL .This value is used in calculating the phenolphthalein alkalinity.  To the same solution in the conical flask add few drops of mixed indicator. The colour of the solution turns to blue. This colour change is due to CO3 & HCO3 ions in water sample.  Continue the titration from the point where stopped for the phenolphthalein alkalinity. Titrate till the solution becomes red. The entire volume (V2) of sulphuric acid is noted down and it is accountable in calculating the total alkalinity.  The value of titration is mL.  Repeat the titration for concordant values.
  • 5. CALCULATION TABLE Table -1 Phenolphthalein Alkalinity: Sl.No. Volume of Sample (mL) Burette Reading (mL) Volume of Sulphuric acid (mL) Initial Final 1. 2. 3. Burette solution: Sulphuric Acid Solution Pipette solution: Sample. Indicator: Phenolphthalein Indicator. End point: Disappearance of pink color. Table - 2 Total Alkalinity: Sl.No. Volume of Sample (mL) Burette Reading (mL) Volume of Sulphuric acid (mL) Initial Final 1. 2. 3. Burette solution: Sulphuric Acid Solution Pipette solution: Sample. Indicator: Mixed Indicator. End point: Appearance of Red color.
  • 6. Specimen Calculation: Volume of Sulphuric Acid = mL Normality of Sulphuric Acid = N Volume of Sample = mL Equivalent weight of CaCO3 = Phenolphthalein Alkalinity = (volume of H22SO4(V1)* Normality * 50 * 1000) Volume of sample taken To convert the sample size from mL to L, multiply the result by 1,000 mL/L to convert the sample size from mL to L Alkalinity as CaCO3 equivalent (mg/L) = X mg/L as CaCO3 equivalent Total Alkalinity also came calculations INTERPRETATION OF RESULTS INFERENCE Alkalinity is a measure of the capacity of water to neutralize acids. The predominant chemical system present in natural waters is one where carbonates, bicarbonates and hydroxides are present. The bicarbonate ion is usually prevalent. However, the ratio of these ions is a function of pH, mineral composition, temperature and ionic strength. Water may have a low alkalinity rating but a relatively high pH or vice versa, so alkalinity alone is not of major importance as a measure of water quality. Alkalinity is not considered detrimental to humans but is generally associated with high pH values, hardness and excess dissolved solids. High alkalinity waters may also have a distinctly flat, unpleasant taste. Based on the testing, it is found that the alkalinity of the sample is 83 mg/L. As per the provisional code, alkalinity should not exceed 200 mg/L for potable water. For the fresh water alkalinity ranges between 20 – 100 mg/L. Alkalinity of tested sample is within the limits specified in the standards. Hence the water sample is fit for drinking.
  • 7. EVALUATION 1. Alkalinity of water is an indication of a) Base neutralizing capacity b) Acid neutralizing capacity c) Quantity of base present d) Quality of base present 2. Mixed indicator is a combination of a) Bromcresol Blue and Methyl Orange b) Bromcresol Green and Methyl Red c) Bromcresol Blue and Methyl Red d) Bromcresol Green and Methyl Orange 3. Alkalinity is present due to all except . a) Bromates b) Phosphates c) Silicates d) Chlorides 4. Alkalinity is not caused by a) Carbonates ions b) Bicarbonates ions c) Hydroxyl ions d) Chloride ions
  • 8. 5. The phenolphthalein alkalinity is present then the pH of that water will be More than a) 8.3 b) 9.3 c) 7.3 d) 6.3 6. Alkalinity of natural water is mainly due to the presence of . a) Bicarbonates b) Bromates c) Phosphates d) Silicates 7. The bicarbonate equivalence point normally occur at pH a) a) 2.5 b) 3.5 c) 4.5 d) 5.5 8. What is ppm? a) Parts per meter square b) Parts per meter c) Parts per million d) Parts per millimeter 9. The normality of the acid used in the titration is . a) 0.2 N b) 0.02 N c) 0.002 N d) 2.0 N 10. A standard solution is a a) Solution of accurately known strength b) Solution of accurately known pH c) Coloured solution d) Colourless solution
  • 9. ENVIRONMENTAL SIGNIFICANCE Alkalinity is important for fish and aquatic life because it protects or buffers against rapid pH changes. Higher alkalinity levels in surface waters will buffer acid rain and other acid wastes and prevent pH changes that are harmful to aquatic life. Large amount of alkalinity imparts bitter taste in water. The principal objection of alkaline water is the reactions that can occur between alkalinity and certain cations in waters. The resultant precipitate can corrode pipes and other accessories of water distribution systems. Wastewaters containing excess caustic (hydroxide) alkalinity are not to be discharged into natural water bodies or sewers. Alkalinity as carbonate and bicarbonate of saline water is very important in tertiary recovery processes for recovering petroleum. Alkaline water offers better wetting to the formation rock and improve oil release. As an additional benefit, ions that provide alkalinity absorb on rock surfaces occupying adsorption sites and decrease the loss of recovery chemical by adsorption. The alkalinity value is necessary in the calculation of carbonate scaling tendencies of saline waters. The alkalinity acts as a pH buffer in coagulation and lime-soda softening of water. In wastewater treatment, alkalinity is an important parameter in determining the amenability of wastes to the treatment process and control of processes such as anaerobic digestion, where bicarbonate alkalinity, total alkalinity, and any fraction contributed by volatile acid salts become considerations.