This document provides instructions for an experiment to determine water hardness using EDTA titration. Students will titrate a water sample and a blank with EDTA to find the endpoint color change. They will then use the titration data and molar concentrations to calculate the concentration of calcium and magnesium ions in the sample in units of mg/L calcium carbonate, which is a measure of water hardness. Safety precautions are outlined for handling the pH 10 buffer and indicator.
The student determined the total hardness of drinking water samples from the hostel, cafe, and laboratory at Elizade University using complexometric titration with EDTA. The total hardness was calculated to be 82 mg/L for the hostel sample, 84 mg/L for the cafe sample, and 80 mg/L for the laboratory sample, indicating the water sources were moderately hard. As the differences between samples were small, the water sources were likely the same without additional filtration.
The document describes an experiment to determine the total hardness of drinking water samples from three locations in Punjab, India. Water samples were collected from Ludhiana, Kharar, and Samrala and titrated against EDTA using an indicator. The total hardness was calculated and found to be 82 mg/L, 84 mg/L, and 80 mg/L, respectively, indicating moderately hard water. The difference in hardness between the three samples was not significant.
Generally hardness of water is defined as the measure of capacity of water to precipitate soap i.e., the capacity of the water to form lather with soap.
Hard water contains dissolved minerals such as Ca2+, Mg2+, Fe3+, SO4 2- ,etc.,
The degree of hardness is measured in Parts Per Million(ppm) or Grams per Gallon(GPG).
Hard water is better for drinking because it contains minerals.
Soft water is better for cleaning because it doesn’t form scum with soap.
Hardness of water is a measure of the total concentration of the calcium and magnesium ions expressed as calcium carbonate.
There are two types of hardness
1. Temporary hardness
Temporary Hardness is due to the presence of bicarbonates of calcium and magnesium. It can be easily removed by boiling.
Ca (HCO3 ) CaCO3 +CO2 +H2O
2. Permanent hardness
Permanent Hardness is due to the presence of chlorides and sulphates of calcium and magnesium. This type of hardness cannot be removed by boiling.
This document provides information about determining the total hardness of a water sample using EDTA titration. It defines hardness as the concentration of calcium and magnesium ions in water. The document outlines the theory behind using EDTA to chelate calcium and magnesium ions, describes the chemicals and apparatus needed, and provides step-by-step instructions for performing an EDTA titration to quantify total water hardness.
This document presents information on the hardness of water, including its constituents, occurrence, structure, types (temporary and permanent), methods of determination (soap solution and EDTA methods), units of measurement in terms of calcium carbonate, and effects. Hardness is caused by calcium and magnesium ions which reduce the lathering ability of soap. There are two types - temporary (removed by boiling) and permanent. Methods to determine hardness involve titrating water samples against soap or EDTA solutions.
The document discusses various topics related to water treatment for textile processing including:
1. Classification and properties of water used for textiles. Hard water can cause issues so standards for textile supply water are outlined.
2. Causes and scales of water hardness. Methods for estimating total, temporary, and permanent hardness are described.
3. Problems hardness causes in wet processing like precipitation and efficiency reductions. Methods to soften water like lime-soda, ion exchange, and demineralization are summarized.
Theory and measurement of hardness ppt version 1VELINSHAH
The document discusses water hardness, including what causes it and different types. It defines hardness as the capacity of water to form soap lather. Hardness is caused by calcium, magnesium, bicarbonates, and sulfates. There are two types: temporary (removed by boiling) and permanent (requires water softening). Methods to measure and remove hardness are also described. Hard water can cause scaling in pipes and appliances.
This document provides instructions for an experiment to determine water hardness using EDTA titration. Students will titrate a water sample and a blank with EDTA to find the endpoint color change. They will then use the titration data and molar concentrations to calculate the concentration of calcium and magnesium ions in the sample in units of mg/L calcium carbonate, which is a measure of water hardness. Safety precautions are outlined for handling the pH 10 buffer and indicator.
The student determined the total hardness of drinking water samples from the hostel, cafe, and laboratory at Elizade University using complexometric titration with EDTA. The total hardness was calculated to be 82 mg/L for the hostel sample, 84 mg/L for the cafe sample, and 80 mg/L for the laboratory sample, indicating the water sources were moderately hard. As the differences between samples were small, the water sources were likely the same without additional filtration.
The document describes an experiment to determine the total hardness of drinking water samples from three locations in Punjab, India. Water samples were collected from Ludhiana, Kharar, and Samrala and titrated against EDTA using an indicator. The total hardness was calculated and found to be 82 mg/L, 84 mg/L, and 80 mg/L, respectively, indicating moderately hard water. The difference in hardness between the three samples was not significant.
Generally hardness of water is defined as the measure of capacity of water to precipitate soap i.e., the capacity of the water to form lather with soap.
Hard water contains dissolved minerals such as Ca2+, Mg2+, Fe3+, SO4 2- ,etc.,
The degree of hardness is measured in Parts Per Million(ppm) or Grams per Gallon(GPG).
Hard water is better for drinking because it contains minerals.
Soft water is better for cleaning because it doesn’t form scum with soap.
Hardness of water is a measure of the total concentration of the calcium and magnesium ions expressed as calcium carbonate.
There are two types of hardness
1. Temporary hardness
Temporary Hardness is due to the presence of bicarbonates of calcium and magnesium. It can be easily removed by boiling.
Ca (HCO3 ) CaCO3 +CO2 +H2O
2. Permanent hardness
Permanent Hardness is due to the presence of chlorides and sulphates of calcium and magnesium. This type of hardness cannot be removed by boiling.
This document provides information about determining the total hardness of a water sample using EDTA titration. It defines hardness as the concentration of calcium and magnesium ions in water. The document outlines the theory behind using EDTA to chelate calcium and magnesium ions, describes the chemicals and apparatus needed, and provides step-by-step instructions for performing an EDTA titration to quantify total water hardness.
This document presents information on the hardness of water, including its constituents, occurrence, structure, types (temporary and permanent), methods of determination (soap solution and EDTA methods), units of measurement in terms of calcium carbonate, and effects. Hardness is caused by calcium and magnesium ions which reduce the lathering ability of soap. There are two types - temporary (removed by boiling) and permanent. Methods to determine hardness involve titrating water samples against soap or EDTA solutions.
The document discusses various topics related to water treatment for textile processing including:
1. Classification and properties of water used for textiles. Hard water can cause issues so standards for textile supply water are outlined.
2. Causes and scales of water hardness. Methods for estimating total, temporary, and permanent hardness are described.
3. Problems hardness causes in wet processing like precipitation and efficiency reductions. Methods to soften water like lime-soda, ion exchange, and demineralization are summarized.
Theory and measurement of hardness ppt version 1VELINSHAH
The document discusses water hardness, including what causes it and different types. It defines hardness as the capacity of water to form soap lather. Hardness is caused by calcium, magnesium, bicarbonates, and sulfates. There are two types: temporary (removed by boiling) and permanent (requires water softening). Methods to measure and remove hardness are also described. Hard water can cause scaling in pipes and appliances.
This document discusses various methods for water softening including:
1. Removal of temporary hardness can be done by boiling or adding lime to precipitate calcium carbonate.
2. Permanent hardness can be removed through chemical precipitation using lime soda ash or ion exchange which replaces calcium and magnesium ions with sodium ions.
3. Demineralization passes water through cation then anion exchange resins to remove all minerals including hardness.
The document describes the lime soda process, an obsolete method for softening hard water. It works by precipitating calcium and magnesium ions through the addition of lime (Ca(OH)2) and soda ash (Na2CO3). The process can be done hot or cold and involves a series of chemical reactions to remove carbonate, sulfate, and magnesium hardness. While once widely used to treat large volumes of water, the lime soda process has limitations and cannot produce completely soft water.
This document outlines a procedure for determining biochemical oxygen demand (BOD5) in water and wastewater samples over a 5 day incubation period. Various reagents are prepared, including a phosphate buffer, magnesium sulfate, calcium chloride, and ferric chloride solutions. A wastewater sample is diluted with dilution water and its initial and final dissolved oxygen concentrations are measured. BOD5 is then calculated based on the oxygen consumed. Results are discussed by comparing to water quality standards and factors affecting BOD5 degradation are addressed.
This document summarizes a student's laboratory experiment to test total solid matter in a water sample. The student measured total solids by drying a water sample and calculating the difference in weight. The total solids in the sample were 33.73 mg/l, which is within the required limit of 500 mg/l for domestic water use according to USPHS standards. Solid analyses are important for controlling water treatment processes and ensuring water quality standards are met.
IRJET- Hardness Removal of Groundwater by using Optimum Lime-Soda ProcessIRJET Journal
The document summarizes a study on removing hardness from groundwater in Surat, India using a lime-soda process. Water samples were collected from four zones in Surat with average hardness of 500 mg/L as CaCO3. Jar tests were conducted with varying dosages of lime and soda ash to determine the optimal dosage. Results showed that increasing lime dosage decreased total hardness concentrations. The pH also increased with higher lime and soda ash dosages. The lime-soda process successfully reduced hardness in the groundwater samples.
Anilisis Kadar DO dan BOD Pada PerairanRajaYustisia
Tujuan dari dilakukannya percobaan ini yaitu untuk mengetahui kadar DO dan BOD pada perairan yang akan dibandingkan dengan baku mutu menurut peraturan pemerintah dan baku mutu lainnya.
Water supply and sewerage engineering laboratoryTaufique Hasan
The document discusses water quality testing performed on samples from the First Ladies Hall of Shahjalal University of Science and Technology, Sylhet. Water samples were tested for various parameters under water supply engineering (drinking water) and sewerage engineering (sewage). For drinking water, tests found the pH, carbon dioxide, turbidity, alkalinity, iron, and manganese levels were all within acceptable limits for drinking water. For sewage, tests were conducted to determine total solids, biochemical oxygen demand, chemical oxygen demand, and chloride. The hardness of the water sample was also found to be within acceptable limits.
coagulation and flocculation Processes for waste water treatmentDeep Kotak
After the coagulation and flocculation process, the wastewater is treated up to that parameter (COD, BOD, etc.) which are acceptable as per government criteria to dump into water bodies instead of directly dumping and also to overcome problems like toxicity and health hazard posed by inorganic coagulants, production of large amount of toxic sludge, ineffectiveness in removing heavy metals and emerging contaminants, increase in effluent color, inefficient pollutant removal using natural coagulants, and complexity of scaling up procedure are presented
This document describes a procedure for determining water hardness through titration with EDTA. Water hardness is defined as the calcium and magnesium ion content and is reported in parts per million (ppm) of calcium carbonate. The titration uses EDTA to chelate calcium and magnesium ions until the indicator Eriochrome Black T changes color, signaling the endpoint. Standard solutions of calcium carbonate and EDTA are prepared and used to determine the concentration of EDTA and calculate water hardness based on the volume of EDTA needed to reach the endpoint in a sample.
Department of biochemistry cell ad molecular biology (1)Samuel Baffoe
1) This experiment aimed to determine the statistical errors associated with diluting a 10M NaOH solution to 0.05M using seven different dilution pathways, including both direct and serial dilutions.
2) The results showed that all dilution pathways produced solutions with concentrations between 0.024M to 0.031M, indicating errors of 0.02-0.03 compared to the theoretical concentration of 0.05M. The serial dilution pathways had higher errors than the direct dilution.
3) Sources of error included inaccuracies in measuring and transferring small volumes, inefficiencies in mixing during serial dilutions, and analyte absorption to container surfaces during transfers. The highest number of dilution steps corresponded to the largest
Unit 03 Photosynthesis Lab Non Inquiry Version General BiologySUNY Oswego
This document describes an experiment to test whether the amount of light an aquatic plant receives affects the level of carbon dioxide in the surrounding water. The experiment uses bromothymol blue solution, which changes color in the presence of carbon dioxide, and Elodea plant pieces. Test tubes containing the solution and plant pieces were placed in light or dark conditions. Over time, the solution in the light test tubes was expected to change color as the plant photosynthesizes, while the solution in the dark test tubes was expected to remain the same color. Observations of color changes in the solutions would indicate whether the level of carbon dioxide differed between the light and dark conditions.
Assessment of the leachability and mechanical stability of mud from a zinc pl...eSAT Publishing House
This document summarizes a study that examined immobilizing mud from a zinc plating plant and waste zeolite materials with Portland cement. Samples with different proportions of mud and zeolite-mud mixtures were prepared and tested. Leachability was assessed using a modified leaching test, where zinc concentrations in eluates were measured after different time periods. A diffusion model was used to assess zinc diffusion speeds and leaching mechanisms. Mechanical strength tests were also conducted. The study aimed to determine the effectiveness of immobilizing zinc-containing wastes with cement and understand the chemical and physical processes involved.
RoHs report of am labels from jizosecurityCathy Zhu
This document is a test report from SGS-CSTC Standards Technical Services (Shanghai) Co., Ltd. analyzing samples submitted by SHANGHAI JIZO TRADING CO.,LTD. for lead, mercury, cadmium, and hexavalent chromium content. Testing was performed from June 27 to June 30, 2017 according to specified standards. The results indicated that the sample identified as AM Label, a silvery metal, complied with limits for lead, mercury, cadmium, and hexavalent chromium as defined by the RoHS Directive. The report provides test methods used and details of sample preparation and testing procedures.
This document describes 9 qualitative tests for carbohydrates: 1) Molish test detects carbohydrates using alpha-naphthol which produces a purple color. 2) Anthrone test uses anthrone reagent to detect sugars and produces a blue-green color. 3) Benedict's test detects reducing sugars using a copper sulfate solution that forms a red precipitate. 4) Picric acid test also detects reducing sugars, forming a red color. 5) Bial's test detects carbohydrates using orcinol and ferric chloride, producing a blue color. 6) Iodine test detects carbohydrates, changing color when mixed with iodine. 7) Borfoed's test detects reducing
Effect of hardness of water on fixation and total wash off percentage of reac...Elias Khalil (ইলিয়াস খলিল)
Dye-house water quality is the most important parameter to be confirmed before dyeing; precisely the presence of metal content i.e. Hardness. This research will investigate & analyses the impact of separate hardness (i.e. Calcium, Magnesium & Iron) on particular „Turquoise‟ (C.I. Reactive Blue 21) & a „High Exhaustion‟ class (C.I. HE Red 120, C.I. HE Yellow 84) of Reactive dye on cotton knitted-fabric. From evaluation of dyed fabric the range of metal content is sorted out where the quality starts to fluctuate as distinctive visible & spectral change of shade & fixation rate of the dye molecules has been found. The result of the work will help for further projection about water quality degradation in upcoming years & its effect on dyeing behavior, also the sustainability of present dyeing process to cope with the ever degrading quality of water.
This document contains information about the densities of various substances including:
- Calcium, neon, carbon monoxide, ethyl alcohol, coke, and Gatorade.
- The densities of gold, silver, benzene, and other unlabeled substances are provided in g/mL.
- Steps are provided for calculating density using mass and volume measurements.
- The document also discusses physical states of matter and properties of select elements and compounds.
This document discusses the principles and methods of gravimetric analysis. Gravimetric analysis involves quantitatively estimating an element or compound based on weighing it after isolation. The key steps are: 1) converting the analyte into an insoluble precipitate of known composition, 2) purifying it by washing, 3) weighing the dried residue to calculate the amount of analyte based on its composition. Common gravimetric methods include precipitation, volatilization, electrogravimetry, and particulate methods. Considerations for choosing appropriate precipitates and weighed forms include solubility, structure, and composition.
The document summarizes research on the phase transformation of sol-gel titania containing silica. Key findings include:
1) The addition of 5-10% silica to titania increases the specific surface area of the material from 89 m2/g to over 200 m2/g. Using ethanol as the solvent medium achieved the highest surface area of 232 m2/g.
2) The addition of silica increases the anatase-rutile phase transformation temperature of titania from around 800°C to higher temperatures.
3) The phase transformation was studied using X-ray diffraction and impedance spectroscopy. The addition of methanol or ethanol was found to enhance the formation of the rutile
This document discusses complexation titration and the use of EDTA titration. Complexation titration involves the titration of a metal ion with a ligand like EDTA to form a colored complex. EDTA is a common chelating agent used due to its high stability constants. It can bind metal ions through multiple atoms. EDTA titrations can be direct, indirect, back, or displacement titrations depending on the method used. Metal ion indicators are also used to detect the color change at the endpoint of the titration.
This document discusses complexometric titration using EDTA. It describes the requirements for complexometric titration including that the formation constant (Kf) must be high and the reaction rate must be fast. It explains that EDTA fulfills these requirements and can be used for direct, indirect, substitution and back titration. It also discusses the selectivity of EDTA through controlling pH, masking/demasking techniques, and precipitation or redox reactions to selectively analyze mixtures.
Here are the steps to solve this problem:
1) Volume of Ag+ solution = 25 mL
Moles of Ag+ = (0.0100 M) * (0.025 L) = 2.5 x 10-5 moles
2) Volume of EDTA solution = 15 mL
Moles of EDTA = (0.0200 M) * (0.015 L) = 3.0 x 10-5 moles
3) Ratio of Ag+ to EDTA is 1:1
Moles of AgEDTA formed = Minimum(Moles Ag+, Moles EDTA) = 2.5 x 10-5 moles
4) Kf' = α * Kf
This document discusses various methods for water softening including:
1. Removal of temporary hardness can be done by boiling or adding lime to precipitate calcium carbonate.
2. Permanent hardness can be removed through chemical precipitation using lime soda ash or ion exchange which replaces calcium and magnesium ions with sodium ions.
3. Demineralization passes water through cation then anion exchange resins to remove all minerals including hardness.
The document describes the lime soda process, an obsolete method for softening hard water. It works by precipitating calcium and magnesium ions through the addition of lime (Ca(OH)2) and soda ash (Na2CO3). The process can be done hot or cold and involves a series of chemical reactions to remove carbonate, sulfate, and magnesium hardness. While once widely used to treat large volumes of water, the lime soda process has limitations and cannot produce completely soft water.
This document outlines a procedure for determining biochemical oxygen demand (BOD5) in water and wastewater samples over a 5 day incubation period. Various reagents are prepared, including a phosphate buffer, magnesium sulfate, calcium chloride, and ferric chloride solutions. A wastewater sample is diluted with dilution water and its initial and final dissolved oxygen concentrations are measured. BOD5 is then calculated based on the oxygen consumed. Results are discussed by comparing to water quality standards and factors affecting BOD5 degradation are addressed.
This document summarizes a student's laboratory experiment to test total solid matter in a water sample. The student measured total solids by drying a water sample and calculating the difference in weight. The total solids in the sample were 33.73 mg/l, which is within the required limit of 500 mg/l for domestic water use according to USPHS standards. Solid analyses are important for controlling water treatment processes and ensuring water quality standards are met.
IRJET- Hardness Removal of Groundwater by using Optimum Lime-Soda ProcessIRJET Journal
The document summarizes a study on removing hardness from groundwater in Surat, India using a lime-soda process. Water samples were collected from four zones in Surat with average hardness of 500 mg/L as CaCO3. Jar tests were conducted with varying dosages of lime and soda ash to determine the optimal dosage. Results showed that increasing lime dosage decreased total hardness concentrations. The pH also increased with higher lime and soda ash dosages. The lime-soda process successfully reduced hardness in the groundwater samples.
Anilisis Kadar DO dan BOD Pada PerairanRajaYustisia
Tujuan dari dilakukannya percobaan ini yaitu untuk mengetahui kadar DO dan BOD pada perairan yang akan dibandingkan dengan baku mutu menurut peraturan pemerintah dan baku mutu lainnya.
Water supply and sewerage engineering laboratoryTaufique Hasan
The document discusses water quality testing performed on samples from the First Ladies Hall of Shahjalal University of Science and Technology, Sylhet. Water samples were tested for various parameters under water supply engineering (drinking water) and sewerage engineering (sewage). For drinking water, tests found the pH, carbon dioxide, turbidity, alkalinity, iron, and manganese levels were all within acceptable limits for drinking water. For sewage, tests were conducted to determine total solids, biochemical oxygen demand, chemical oxygen demand, and chloride. The hardness of the water sample was also found to be within acceptable limits.
coagulation and flocculation Processes for waste water treatmentDeep Kotak
After the coagulation and flocculation process, the wastewater is treated up to that parameter (COD, BOD, etc.) which are acceptable as per government criteria to dump into water bodies instead of directly dumping and also to overcome problems like toxicity and health hazard posed by inorganic coagulants, production of large amount of toxic sludge, ineffectiveness in removing heavy metals and emerging contaminants, increase in effluent color, inefficient pollutant removal using natural coagulants, and complexity of scaling up procedure are presented
This document describes a procedure for determining water hardness through titration with EDTA. Water hardness is defined as the calcium and magnesium ion content and is reported in parts per million (ppm) of calcium carbonate. The titration uses EDTA to chelate calcium and magnesium ions until the indicator Eriochrome Black T changes color, signaling the endpoint. Standard solutions of calcium carbonate and EDTA are prepared and used to determine the concentration of EDTA and calculate water hardness based on the volume of EDTA needed to reach the endpoint in a sample.
Department of biochemistry cell ad molecular biology (1)Samuel Baffoe
1) This experiment aimed to determine the statistical errors associated with diluting a 10M NaOH solution to 0.05M using seven different dilution pathways, including both direct and serial dilutions.
2) The results showed that all dilution pathways produced solutions with concentrations between 0.024M to 0.031M, indicating errors of 0.02-0.03 compared to the theoretical concentration of 0.05M. The serial dilution pathways had higher errors than the direct dilution.
3) Sources of error included inaccuracies in measuring and transferring small volumes, inefficiencies in mixing during serial dilutions, and analyte absorption to container surfaces during transfers. The highest number of dilution steps corresponded to the largest
Unit 03 Photosynthesis Lab Non Inquiry Version General BiologySUNY Oswego
This document describes an experiment to test whether the amount of light an aquatic plant receives affects the level of carbon dioxide in the surrounding water. The experiment uses bromothymol blue solution, which changes color in the presence of carbon dioxide, and Elodea plant pieces. Test tubes containing the solution and plant pieces were placed in light or dark conditions. Over time, the solution in the light test tubes was expected to change color as the plant photosynthesizes, while the solution in the dark test tubes was expected to remain the same color. Observations of color changes in the solutions would indicate whether the level of carbon dioxide differed between the light and dark conditions.
Assessment of the leachability and mechanical stability of mud from a zinc pl...eSAT Publishing House
This document summarizes a study that examined immobilizing mud from a zinc plating plant and waste zeolite materials with Portland cement. Samples with different proportions of mud and zeolite-mud mixtures were prepared and tested. Leachability was assessed using a modified leaching test, where zinc concentrations in eluates were measured after different time periods. A diffusion model was used to assess zinc diffusion speeds and leaching mechanisms. Mechanical strength tests were also conducted. The study aimed to determine the effectiveness of immobilizing zinc-containing wastes with cement and understand the chemical and physical processes involved.
RoHs report of am labels from jizosecurityCathy Zhu
This document is a test report from SGS-CSTC Standards Technical Services (Shanghai) Co., Ltd. analyzing samples submitted by SHANGHAI JIZO TRADING CO.,LTD. for lead, mercury, cadmium, and hexavalent chromium content. Testing was performed from June 27 to June 30, 2017 according to specified standards. The results indicated that the sample identified as AM Label, a silvery metal, complied with limits for lead, mercury, cadmium, and hexavalent chromium as defined by the RoHS Directive. The report provides test methods used and details of sample preparation and testing procedures.
This document describes 9 qualitative tests for carbohydrates: 1) Molish test detects carbohydrates using alpha-naphthol which produces a purple color. 2) Anthrone test uses anthrone reagent to detect sugars and produces a blue-green color. 3) Benedict's test detects reducing sugars using a copper sulfate solution that forms a red precipitate. 4) Picric acid test also detects reducing sugars, forming a red color. 5) Bial's test detects carbohydrates using orcinol and ferric chloride, producing a blue color. 6) Iodine test detects carbohydrates, changing color when mixed with iodine. 7) Borfoed's test detects reducing
Effect of hardness of water on fixation and total wash off percentage of reac...Elias Khalil (ইলিয়াস খলিল)
Dye-house water quality is the most important parameter to be confirmed before dyeing; precisely the presence of metal content i.e. Hardness. This research will investigate & analyses the impact of separate hardness (i.e. Calcium, Magnesium & Iron) on particular „Turquoise‟ (C.I. Reactive Blue 21) & a „High Exhaustion‟ class (C.I. HE Red 120, C.I. HE Yellow 84) of Reactive dye on cotton knitted-fabric. From evaluation of dyed fabric the range of metal content is sorted out where the quality starts to fluctuate as distinctive visible & spectral change of shade & fixation rate of the dye molecules has been found. The result of the work will help for further projection about water quality degradation in upcoming years & its effect on dyeing behavior, also the sustainability of present dyeing process to cope with the ever degrading quality of water.
This document contains information about the densities of various substances including:
- Calcium, neon, carbon monoxide, ethyl alcohol, coke, and Gatorade.
- The densities of gold, silver, benzene, and other unlabeled substances are provided in g/mL.
- Steps are provided for calculating density using mass and volume measurements.
- The document also discusses physical states of matter and properties of select elements and compounds.
This document discusses the principles and methods of gravimetric analysis. Gravimetric analysis involves quantitatively estimating an element or compound based on weighing it after isolation. The key steps are: 1) converting the analyte into an insoluble precipitate of known composition, 2) purifying it by washing, 3) weighing the dried residue to calculate the amount of analyte based on its composition. Common gravimetric methods include precipitation, volatilization, electrogravimetry, and particulate methods. Considerations for choosing appropriate precipitates and weighed forms include solubility, structure, and composition.
The document summarizes research on the phase transformation of sol-gel titania containing silica. Key findings include:
1) The addition of 5-10% silica to titania increases the specific surface area of the material from 89 m2/g to over 200 m2/g. Using ethanol as the solvent medium achieved the highest surface area of 232 m2/g.
2) The addition of silica increases the anatase-rutile phase transformation temperature of titania from around 800°C to higher temperatures.
3) The phase transformation was studied using X-ray diffraction and impedance spectroscopy. The addition of methanol or ethanol was found to enhance the formation of the rutile
This document discusses complexation titration and the use of EDTA titration. Complexation titration involves the titration of a metal ion with a ligand like EDTA to form a colored complex. EDTA is a common chelating agent used due to its high stability constants. It can bind metal ions through multiple atoms. EDTA titrations can be direct, indirect, back, or displacement titrations depending on the method used. Metal ion indicators are also used to detect the color change at the endpoint of the titration.
This document discusses complexometric titration using EDTA. It describes the requirements for complexometric titration including that the formation constant (Kf) must be high and the reaction rate must be fast. It explains that EDTA fulfills these requirements and can be used for direct, indirect, substitution and back titration. It also discusses the selectivity of EDTA through controlling pH, masking/demasking techniques, and precipitation or redox reactions to selectively analyze mixtures.
Here are the steps to solve this problem:
1) Volume of Ag+ solution = 25 mL
Moles of Ag+ = (0.0100 M) * (0.025 L) = 2.5 x 10-5 moles
2) Volume of EDTA solution = 15 mL
Moles of EDTA = (0.0200 M) * (0.015 L) = 3.0 x 10-5 moles
3) Ratio of Ag+ to EDTA is 1:1
Moles of AgEDTA formed = Minimum(Moles Ag+, Moles EDTA) = 2.5 x 10-5 moles
4) Kf' = α * Kf
This document discusses complexometric titrations using ethylenediaminetetraacetic acid (EDTA) as the titrant. It describes how EDTA forms stable 1:1 complexes with metal ions and can be used to titrate metals in various ways, including direct titration, back-titration, and replacement titration. It also explains the importance of pH and discusses indicators used for different metal-EDTA complexes. Calcium titrations are discussed as an example, noting how magnesium ions improve the sharpness of the endpoint when using solochrome black indicator.
this eperiment was done by
Anet Mengesha Dube
at addis ababa university
addis ababa institute of tecnology
school of bio &chemichal_engineering
2nd year student
This document discusses different types of titrations used in analytical chemistry. It describes four main types: acid-base titrations, complexometric titrations, precipitation titrations, and redox titrations. It provides examples of each type, including EDTA titrations used for complexometric titrations to determine hardness, Mohr's method for precipitation titration of chloride ions, and titration of iron using potassium dichromate for redox titrations. The document also covers topics like concentration systems, including definitions and calculations involving molarity, molality, formality, and normality.
Determination of hardness in water .pdfMausumi Adhya
1. The document describes the determination of hardness in water samples by complexometric titration using EDTA. Total hardness is defined as the sum of calcium and magnesium ions and is expressed in parts per million of calcium carbonate.
2. EDTA forms stable complexes with Ca2+ and Mg2+ ions at pH 9-10, allowing for their quantification via titration. The endpoint is indicated by a color change of the indicator Eriochrome Black T from grape/wine red to blue.
3. A sample water is titrated with standardized EDTA solution and the total hardness is calculated based on the volume used and concentration of EDTA. Calcium hardness is also determined by titrating at pH 12,
The document discusses water treatment and hardness for textile processing. It defines hardness as the condition where soap is less effective at forming foam due to the presence of calcium and magnesium ions. Hard water can cause issues like precipitates, poor dyeing and finishing results. Methods for determining total, temporary and permanent hardness are presented. Total hardness is measured by titrating with EDTA, while temporary hardness can be removed by boiling and titrating the residual with HCl. Common methods for softening hard water include lime-soda processing, ion exchange, demineralization, and use of sequestering agents.
• A chelate is formed when a metal ion coordinates with two (or more) donor groups of a single ligand. Tertiary amine compounds such as ethylenadiaminetetraacetic acid (EDTA) are widely used for the formation of chelates.
• Complexometric titrations with EDTA have been reported for the analysis of nearly all metal ions The endpoint of the titration is determined by the addition of Eriochrome Black T, which forms a colored chelate with Mg 2+ and undergoes a color change when the Mg 2+ is released to form a chelate with EDTA
This document provides instructions for estimating the amount of calcium and magnesium in food samples using complexometric titration with EDTA. It describes titrating a standard hard water sample against a standardized EDTA solution to determine the EDTA concentration. This standardized EDTA is then used to titrate sample hard water and determine total, calcium, and magnesium hardness levels present. The document lists the materials, procedure, and questions to ask during the experiment. The results will provide the concentration of total hardness, calcium hardness, and magnesium hardness in the sample water in ppm units.
This document discusses water hardness, its determination using EDTA titration, and methods for water softening. It provides details on:
- Temporary and permanent hardness, and their sources
- Calculating hardness from ion concentrations using equivalents of CaCO3
- The EDTA titration process for determining total hardness
- Examples of calculations for total, temporary and permanent hardness
The key points are that hardness is caused by calcium, magnesium, and other ions, and is classified as temporary (removable by boiling) or permanent. Total hardness can be determined by titrating a water sample with EDTA and calculating concentration in terms of CaCO3 equivalents. Temporary hardness is the difference between total and permanent hardness
This document discusses water technology and the analysis of water hardness. It outlines various sources of water including rainwater, surface water, groundwater, and seawater. Water can become impure through dissolving gases, minerals, and organic matter. Hardness in water is caused by calcium, magnesium, and other ions and prevents soap from lathering. Hardness can be temporary (removed by boiling) or permanent. The document describes methods for measuring hardness using EDTA titration and calculating hardness levels in terms of calcium carbonate equivalents and other units.
The document provides instructions for performing an assay of calcium gluconate by complexometry, including preparing standard EDTA and magnesium sulfate solutions, titrating calcium gluconate against EDTA while using magnesium and an indicator to identify the endpoint, and calculating the percentage purity of calcium gluconate based on the titration results. The titration is a replacement complexometric titration that uses the stable magnesium-indicator complex to indirectly determine the endpoint of the calcium-EDTA reaction.
This document provides a syllabus for an engineering chemistry course that covers 7 units related to water analysis, treatment, and industrial applications. The first unit discusses various water sources and types of impurities found in different water sources. It also explains water treatment methods and uses of water in industry. The document includes details on determining water hardness using EDTA titration, including the chemical reactions, procedure, calculations, and an example problem.
This document provides instructions for determining the concentration of magnesium (Mg) in an unknown sample by titrating with ethylenediaminetetraacetic acid (EDTA). The EDTA solution is standardized against a zinc standard solution. Magnesium in the unknown sample forms a complex with Eriochrome Black T indicator, changing color. When all the magnesium has been chelated by EDTA, the indicator changes to a clear blue, signaling the titration endpoint. Students will titrate the unknown sample with standardized EDTA and calculate the percentage of magnesium in the prepared unknown sample diluted to 100 mL.
Module 5 Chemistry notes and assignment notesmuhammedhasinnk
Hard water is water that does not lather easily with soap due to dissolved calcium and magnesium ions. There are two types of hardness: temporary hardness caused by bicarbonates of calcium and magnesium that can be removed by boiling, and permanent hardness caused by chlorides and sulfates of calcium and magnesium that cannot be removed by boiling. Hardness of water is quantified using calcium carbonate equivalent units, where the mass of hardness-causing substances is multiplied by 100 and divided by the molecular mass of calcium carbonate.
This document provides information about water technology and the hardness of water. It discusses how water is essential for life and its various uses. Water exists in different forms on Earth, including as freshwater and saltwater. Sources of freshwater include surface water and groundwater. The document also describes the unique properties of water and the water cycle. It defines different types of water based on purity levels and intended uses. The document explains what causes water hardness and how to measure and calculate hardness in terms of calcium carbonate equivalents and various scale units. Common ions that contribute to water hardness, like calcium and magnesium, are also discussed.
Water is essential for humans, animals and plants. It is used for drinking, cooking, bathing and washing. Water also plays an important role in industries. Hardness in water is caused by dissolved salts of calcium, magnesium and other metals. This prevents soap from lathering easily. Hardness can be classified as temporary, caused by bicarbonates, or permanent, caused by chlorides and sulfates. The EDTA method is commonly used to determine water hardness by forming complexes with calcium and magnesium ions. Scale and sludge formation in boilers occurs when salt concentrations exceed solubility limits during steam production, potentially weakening boiler walls.
This document outlines the topics covered in the Engineering Chemistry course including water and its treatment, electrochemistry and batteries, polymers, fuels and combustion, cement, refractories, lubricants and composites. The course aims to provide understanding of water properties and treatment, electrochemical cells and batteries, polymer engineering applications, fuel combustion and properties of basic construction materials. Key concepts covered include water hardness, its causes and types, water treatment methods, electrochemistry principles, polymer classifications and applications.
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5. Determination of Hardness
Standardization of EDTA :
10ml SHW + 3ml Buffer + 2 drop EBT
wine red colour
+EDTA
Blue colour
(End Point)
6. Determination of Total Hardness :
10ml Water Sample +3ml Buffer + 2 drop EBT
wine red colour
+EDTA
Blue colour
(End Point)
7. Determination of Permanent Hardness :
250ml Water Sample boil 50 ml filter Filtrate
make up to 1 lt. by D.W.(Boil Water)
10ml boil water sample + 3ml Buffer + 2 drop EBT
Blue colour +EDTA wine red colour
(End Point)
8. Calculation
Standardization of EDTA :
10 ml of SHW = 10mg of CaCO3 eq.
10 ml of SHW = V1 ml of EDTA
10 mg of CaCO3 eq. = V1 ml of EDTA
1 ml of EDTA = 10/ V1 mg of CaCO3 eq.
9. Total Hardness :
10 ml H2O sample = V2 ml of EDTA
10 ml H2O sample = V2×10/V1 mg of CaCO3 eq.
1000 ml of H2O sample = (V2/V1)×1000 ppm
10. Permanent Hardness :
10 ml boil H2O sample = V3 ml of EDTA
10 ml boil H2O sample = V3×10 mg of CaCO3 eq.
1000ml of boil H2O sample = (V3/V1)×1000 ppm
11. Temporary Hardness :
Total Hardness = Temp. H. + Per. H.
Temp. H. = Total H.-Per. H.
=> Temp. H. = {(V2-V3)/V1}×1000 ppm