Experiment Details:
Date:
Department of Chemistry
Name:
Branch:
Registration Number:
Duration: 90 min
Objective: Standardization of EDTA by titrating against standard hard water.
Requirements:
Reagents and Solutions:
Standard hard water (0.01M or 1000ppm)
EDTA solution
EBT indicator
NH3-NH4Cl buffer solution
Apparatus:
Burette
Pipette
Conical flask
Standard flask
Burette stand
Procedure:
Prepare EDTA solution:
Add distilled water to 100 mL in a volumetric flask.
Titration Setup:
Pipette 20 mL of standard hard water into a conical flask.
Add 2 mL of NH4OH-NH4Cl buffer (to maintain pH ~10).
Add 1-2 drops of EBT indicator.
Titration:
Titrate against the EDTA solution until color changes from wine red to steel blue.
Record volume of EDTA used as 'V1'.
Replicate: Repeat for concordant readings.
Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V1, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
Calculation:
( 1 \text{ mL of EDTA} = \left( \frac{20}{V1} \right) \text{ mg of CaCO3 eq.} )
(Expression of Concentration):
Given M1V1 = M2V2, with M1 for EDTA, M2 for CaCO3.
Calculations:
( M1 = \frac{M2 \times V2}{V1} = \frac{0.01 \times 20}{V1} ) (Molarity of CaCO3)
Equivalence Data:
1L of 1M EDTA = 100g eqvt. of CaCO3
1L of 0.01 x 20/ V1 EDTA = ( \frac{20}{V1} \text{ gm eq. of CaCO3} )
Result Evaluation:
Sample water: 50mL of tap water required 15mL of EDTA.
After boiling, 10mL of EDTA consumed for same sample.
50mL of 0.02M standard CaCO3 consumed 20mL of EDTA.
Calculate hardness (temporary, permanent, total) in ppm.
Aim: To determine total hardness of water using EDTA complexometric titration.
Principle: Hardness arises from Ca2+ and Mg2+ salts in the water.
Reaction:
EDTA forms complexes with cations, quantitatively at pH 10.
General reaction: ( M + H2Y2- \rightarrow MY2- + 2H+ ) wherein M = Ca2+, Mg2+.
EBT forms a wine-red complex with M2+, less stable than metal-EDTA.
Requirements:
Reagents/Solutions:
Standard hard water (0.01M), EDTA, EBT indicator, NH3-NH4Cl buffer
Apparatus: Same as previous.
Procedure for Titration I (Standardization of EDTA):
Prepare a 100 mL EDTA solution for titration.
Pipette 20 mL of standard calcium ion solution into a conical flask.
Add 2-3 mL NH4OH-NH4Cl buffer and 3 drops of EBT.
Titrate with EDTA until the color changes from red to blue: record as 'V1'.
Procedure for Titration II (Total Hardness Estimation):
Pipette 20 mL of the water sample into a conical flask.
Follow steps 2-4 from Titration I, recording as 'V2'.
Observation and Calculation:
Titration I Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V1, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
Calculate hardness from V1 and V2.
Burette: Standard EDTA solution
Conical Flask: 20 mL of hard water + buffer + 2 drops of EBT
Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V2, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
From this measurement, define total hardness in ppm.
Aim: Determine types and extent of alkalinity in a water sample.
Principle: Alkalinity from OH-, CO32-, HCO3- ions neutralized by standard HCl.
Detection Metrics:
Titrate until pH 8.3 (Phenolphthalein indicator) = neutralizes OH- and half CO32-.
Titrate until 4.4 (Methyl Orange indicator) = total alkalinity measured.
Reagents/Solutions:
Hydrochloric acid (0.1N)
Methyl orange & phenolphthalein indicators
Procedure:
Mix water sample in a 100 mL volumetric flask and add HCl till the endpoint records [P] and [T].
Record readings for subsequent calculations.
Calculation Table:
S.No | Water Sample (mL) | Burette Reading at [P] (mL) | Burette Reading at [T] (mL) |
---|
Results: Determine the concentrations of each ion as well as total alkalinity.
Titration Observation Table:
S.No | Volume of Water Sample (mL) | Burette Reading (mL) | Concordant Value (mL) |
---|---|---|---|
1 |
Phenolphthalein Alkalinity and Calculations:
( ext{Phenolphthalein Alkalinity (mg/L as CaCO3)} = \text{mL of HCl} \times \text{Normality of HCl} \times 50 \times 1000 )
Methyl Orange Alkalinity Calculations: ( ext{Methyl Orange Alkalinity (mg/L as CaCO3)} = \text{mL of HCl} \times \text{Normality of HCl} \times 50 \times 1000 )
Data Regarding OH-, CO32-, HCO3- Alkalinity Types:
Results Evaluation:
Total alkalinity and data to be filled:
Sample number, experimental values, actual values, % error, marks, and space for calculations.
Aim: To estimate copper content in a sample solution.
Principle: Reaction of iodine and sodium thiosulphate and subsequent titration.
Reagents/Solutions:
0.01 N copper sulphate, KI, 0.01N sodium thiosulphate.
Procedure Titration I (Standardization):
Pipette 20ml of copper sulphate into a conical flask.
Add ammonium hydroxide till precipitate forms, then clear it with acetic acid.
Add KI and titrate iodine against thiosulphate until blue disappears.
Data Table for Titration Analysis:| S.No | Volume of Std CuSO4 (ml) | Final Burette Reading | Volume of Sodium Thiosulphate (ml) |
Titration II:
Make alloy to 100 mL solution, and process as above.
Measure readings.
Data for Analysis:| S.No | Volume of Unknown CuSO4 (ml) | Volume of Sodium Thiosulphate (ml) |
Calculate copper using: ( ext{Cu (present in the solution)} = \frac{ ext{Normality} \times ext{Equivalent Weight}}{10} )
Calculations
Detailed observation values across experiments, results, and marks analysis.
Equivalence and final outcomes in standard measurements.
Aim: Estimate dissolved oxygen in water samples via Winkler’s method.
Principle: Oxygen oxidation of potassium iodide, measured via thiosulphate titration.
Procedure:
Mix sample with reagents, precipitate settling, then titrate.
Record and calculate dissolved oxygen (ppm).
Formula Usage: ( ext{ppm} = N \times ext{equivalent weight} \times 1000 mg/L ) where N is normality.
Principle: Conductometric method evaluates the ion presence through conductivity variations during titration.
Procedure:
Calibrate TDS meter with KCl.
Follow through with BaCl2 to monitor conductance.
Data Recording and Graphing:
Result interpretation from graphs reflecting BaCl2 additions related to sulphate levels.
Concise tabulated data reflecting volumetric analysis results.
Principle: Potassium permanganate oxidizes ferrous ions under controlled conditions.
Procedure: Measure EMF changes corresponding to titration volume; determine iron concentration from graphs.
Calculation equations for assessing Fe(II) concentration, aimed around titration endpoints with proper data layout for observations.
Principle and Procedures:
Apply Beer's law to colorimetric analysis for Cu concentrations.
Prepare standard solutions and measure absorbances, graph results.
Final Results: Reports for concentration outputs, comparative calculations.
chem lab manual
Experiment Details:
Date:
Department of Chemistry
Name:
Branch:
Registration Number:
Duration: 90 min
Objective: Standardization of EDTA by titrating against standard hard water.
Requirements:
Reagents and Solutions:
Standard hard water (0.01M or 1000ppm)
EDTA solution
EBT indicator
NH3-NH4Cl buffer solution
Apparatus:
Burette
Pipette
Conical flask
Standard flask
Burette stand
Procedure:
Prepare EDTA solution:
Add distilled water to 100 mL in a volumetric flask.
Titration Setup:
Pipette 20 mL of standard hard water into a conical flask.
Add 2 mL of NH4OH-NH4Cl buffer (to maintain pH ~10).
Add 1-2 drops of EBT indicator.
Titration:
Titrate against the EDTA solution until color changes from wine red to steel blue.
Record volume of EDTA used as 'V1'.
Replicate: Repeat for concordant readings.
Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V1, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
Calculation:
( 1 \text{ mL of EDTA} = \left( \frac{20}{V1} \right) \text{ mg of CaCO3 eq.} )
(Expression of Concentration):
Given M1V1 = M2V2, with M1 for EDTA, M2 for CaCO3.
Calculations:
( M1 = \frac{M2 \times V2}{V1} = \frac{0.01 \times 20}{V1} ) (Molarity of CaCO3)
Equivalence Data:
1L of 1M EDTA = 100g eqvt. of CaCO3
1L of 0.01 x 20/ V1 EDTA = ( \frac{20}{V1} \text{ gm eq. of CaCO3} )
Result Evaluation:
Sample water: 50mL of tap water required 15mL of EDTA.
After boiling, 10mL of EDTA consumed for same sample.
50mL of 0.02M standard CaCO3 consumed 20mL of EDTA.
Calculate hardness (temporary, permanent, total) in ppm.
Aim: To determine total hardness of water using EDTA complexometric titration.
Principle: Hardness arises from Ca2+ and Mg2+ salts in the water.
Reaction:
EDTA forms complexes with cations, quantitatively at pH 10.
General reaction: ( M + H2Y2- \rightarrow MY2- + 2H+ ) wherein M = Ca2+, Mg2+.
EBT forms a wine-red complex with M2+, less stable than metal-EDTA.
Requirements:
Reagents/Solutions:
Standard hard water (0.01M), EDTA, EBT indicator, NH3-NH4Cl buffer
Apparatus: Same as previous.
Procedure for Titration I (Standardization of EDTA):
Prepare a 100 mL EDTA solution for titration.
Pipette 20 mL of standard calcium ion solution into a conical flask.
Add 2-3 mL NH4OH-NH4Cl buffer and 3 drops of EBT.
Titrate with EDTA until the color changes from red to blue: record as 'V1'.
Procedure for Titration II (Total Hardness Estimation):
Pipette 20 mL of the water sample into a conical flask.
Follow steps 2-4 from Titration I, recording as 'V2'.
Observation and Calculation:
Titration I Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V1, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
Calculate hardness from V1 and V2.
Burette: Standard EDTA solution
Conical Flask: 20 mL of hard water + buffer + 2 drops of EBT
Data Table:
S.No | Volume of standard hard water (mL) | Burette reading (mL) | Volume of EDTA (V2, mL) |
---|---|---|---|
1 | |||
2 | |||
3 |
From this measurement, define total hardness in ppm.
Aim: Determine types and extent of alkalinity in a water sample.
Principle: Alkalinity from OH-, CO32-, HCO3- ions neutralized by standard HCl.
Detection Metrics:
Titrate until pH 8.3 (Phenolphthalein indicator) = neutralizes OH- and half CO32-.
Titrate until 4.4 (Methyl Orange indicator) = total alkalinity measured.
Reagents/Solutions:
Hydrochloric acid (0.1N)
Methyl orange & phenolphthalein indicators
Procedure:
Mix water sample in a 100 mL volumetric flask and add HCl till the endpoint records [P] and [T].
Record readings for subsequent calculations.
Calculation Table:
S.No | Water Sample (mL) | Burette Reading at [P] (mL) | Burette Reading at [T] (mL) |
---|
Results: Determine the concentrations of each ion as well as total alkalinity.
Titration Observation Table:
S.No | Volume of Water Sample (mL) | Burette Reading (mL) | Concordant Value (mL) |
---|---|---|---|
1 |
Phenolphthalein Alkalinity and Calculations:
( ext{Phenolphthalein Alkalinity (mg/L as CaCO3)} = \text{mL of HCl} \times \text{Normality of HCl} \times 50 \times 1000 )
Methyl Orange Alkalinity Calculations: ( ext{Methyl Orange Alkalinity (mg/L as CaCO3)} = \text{mL of HCl} \times \text{Normality of HCl} \times 50 \times 1000 )
Data Regarding OH-, CO32-, HCO3- Alkalinity Types:
Results Evaluation:
Total alkalinity and data to be filled:
Sample number, experimental values, actual values, % error, marks, and space for calculations.
Aim: To estimate copper content in a sample solution.
Principle: Reaction of iodine and sodium thiosulphate and subsequent titration.
Reagents/Solutions:
0.01 N copper sulphate, KI, 0.01N sodium thiosulphate.
Procedure Titration I (Standardization):
Pipette 20ml of copper sulphate into a conical flask.
Add ammonium hydroxide till precipitate forms, then clear it with acetic acid.
Add KI and titrate iodine against thiosulphate until blue disappears.
Data Table for Titration Analysis:| S.No | Volume of Std CuSO4 (ml) | Final Burette Reading | Volume of Sodium Thiosulphate (ml) |
Titration II:
Make alloy to 100 mL solution, and process as above.
Measure readings.
Data for Analysis:| S.No | Volume of Unknown CuSO4 (ml) | Volume of Sodium Thiosulphate (ml) |
Calculate copper using: ( ext{Cu (present in the solution)} = \frac{ ext{Normality} \times ext{Equivalent Weight}}{10} )
Calculations
Detailed observation values across experiments, results, and marks analysis.
Equivalence and final outcomes in standard measurements.
Aim: Estimate dissolved oxygen in water samples via Winkler’s method.
Principle: Oxygen oxidation of potassium iodide, measured via thiosulphate titration.
Procedure:
Mix sample with reagents, precipitate settling, then titrate.
Record and calculate dissolved oxygen (ppm).
Formula Usage: ( ext{ppm} = N \times ext{equivalent weight} \times 1000 mg/L ) where N is normality.
Principle: Conductometric method evaluates the ion presence through conductivity variations during titration.
Procedure:
Calibrate TDS meter with KCl.
Follow through with BaCl2 to monitor conductance.
Data Recording and Graphing:
Result interpretation from graphs reflecting BaCl2 additions related to sulphate levels.
Concise tabulated data reflecting volumetric analysis results.
Principle: Potassium permanganate oxidizes ferrous ions under controlled conditions.
Procedure: Measure EMF changes corresponding to titration volume; determine iron concentration from graphs.
Calculation equations for assessing Fe(II) concentration, aimed around titration endpoints with proper data layout for observations.
Principle and Procedures:
Apply Beer's law to colorimetric analysis for Cu concentrations.
Prepare standard solutions and measure absorbances, graph results.
Final Results: Reports for concentration outputs, comparative calculations.