Alkalinity of water is essential parameter to be found before its consumption. Following is a self explanatory presentation of why it is important and how to find the same in any sample of water.
There are three sources of alkalinity in water samples: hydroxide, carbonate, and bicarbonate alkalinity. The alkalinity method involves titrating a water sample from its original pH down to pH 8.3 to determine hydroxide and carbonate alkalinity. The sample is then titrated down to pH 4.5 to determine total alkalinity. Calculations are performed based on the volumes of acid added and normality to quantify each alkalinity type in units of mg/L as CaCO3. The source and amount of each alkalinity present depends on the initial pH and volume of acid needed to reach pH 8.3 versus the total volume to pH 4.
Alkalinity in water is measured by titrating a water sample with sulfuric acid and monitoring the pH. Alkalinity is caused by hydroxides, carbonates, and bicarbonates and is expressed in units of mg/L of calcium carbonate. The amount of acid needed to reduce the pH to 8.3 measures phenolphthalein alkalinity, while the amount to reduce to 4.5 measures total alkalinity. Different combinations of hydroxides, carbonates, and bicarbonates can be present depending on the initial pH. Alkalinity data provides information useful for water treatment processes like coagulation, softening, and corrosion control.
This document describes an experiment to determine the alkalinity of a water sample through titration with sulfuric acid. Alkalinity is measured by titrating a water sample with acid until the pH reaches 4.5, neutralizing hydroxyl, carbonate, and bicarbonate ions. The titration is performed twice - first with phenolphthalein to measure phenolphthalein alkalinity from hydroxyl ions, then with a mixed indicator to measure total alkalinity from additional carbonate and bicarbonate ions. The alkalinity of the tested sample was found to be 83 mg/L, within acceptable limits for drinking water.
This document provides instructions for determining the alkalinity of a water sample using a double-endpoint titration. Alkalinity is caused by carbonate, bicarbonate, and hydroxide ions and refers to a water sample's ability to neutralize acids. A titration with sulfuric acid is conducted, with two endpoints detected using different pH indicators. The volumes of acid needed at each endpoint can identify which ions are present and be used to calculate the sample's total, phenolphthalein, carbonate, bicarbonate, and hydroxide alkalinities in mg/L CaCO3. Tables are provided to match titration results to ion combinations and determine which acid volumes to use
Lecture notes of Environmental Engineering-II as per Solapur university syllabus of TE CIVIL.
Prepared by
Prof S S Jahagirdar,
Associate Professor,
N K Orchid college of Engg and Technology,
Solapur
Analysis BOD is an important parameter in identifying the extend of pollution in a water body. This presentation explains the various methods of BOD analysis as per the APHA manual
This document provides a procedure for determining the alkalinity of water samples. Alkalinity is measured through acid-base titration and is important as it indicates a water sample's ability to resist changes in pH. The procedure involves titrating the sample with sulfuric acid using phenolphthalein and methyl orange indicators. The titrations are used to determine the phenolphthalein alkalinity and total alkalinity in mg/L of calcium carbonate. For the given water sample, the phenolphthalein alkalinity was found to be 0 while the total alkalinity was determined to be 65 mg/L, within the recommended limit of less than 200 mg/L.
The document discusses biochemical oxygen demand (BOD), which measures the amount of oxygen used by microorganisms to break down organic waste in water. When organic waste is present, bacteria consume dissolved oxygen to decompose the waste. BOD tests how much oxygen is absorbed over 5 days at 20°C. A high BOD level indicates more organic waste requiring decomposition, lowering available oxygen for aquatic life. BOD is used to measure water pollution and assess treatment plant performance by comparing raw sewage and treated effluent BOD levels. Proper BOD testing follows steps including sample collection, dilution, seeding with bacteria, initial and final oxygen readings, and calculations to determine BOD in mg/L.
The document discusses coagulation and flocculation processes used in water treatment. It begins by explaining that coagulation uses chemicals like aluminum and iron salts to neutralize the negative charges on small particles and colloids in water. This destabilizes the particles so they can agglomerate during flocculation. Flocculation is the process where the destabilized particles collide and form larger flocs that are easier to remove by sedimentation. Jar tests are used to determine the optimal pH and coagulant dose. Different types of flocculators including mechanical mixers and hydraulic designs that utilize baffles or differential settling are also described.
This Presentation Clarifying about potable Water analysis and their methods which i gave training on operation and maintenance team for Oman Al Ghubrah Independence Water Project (SWRO Desalination 42 MIGD)
This document describes a procedure to determine the acidity of a water sample through titration with sodium hydroxide solution. The acidity is measured as both mineral acidity at pH 3.7 using methyl orange indicator and total acidity at pH 8.3 using phenolphthalein indicator. Dissolved carbon dioxide is usually the major contributor to acidity in surface waters. The titration results are used to calculate and report the acidity levels in the sample as mg/L of calcium carbonate equivalent. High acidity can interfere with water treatment and affect aquatic life.
The document outlines various methods for determining types of solids in wastewater samples, including total solids, total suspended solids, volatile solids, fixed solids, total dissolved solids, and their significance for classifying wastewater and designing wastewater treatment processes. Gravimetric analysis methods are described for evaporating and igniting samples to separate organic and inorganic fractions. Standards for discharge of treated wastewater are also provided.
This document discusses coagulation and flocculation processes used in water treatment. It explains that coagulation uses chemicals like aluminum and iron salts to destabilize colloidal particles in water by neutralizing their negative charges. This allows the particles to agglomerate into larger flocs during flocculation. Flocculation is the process where these destabilized particles come together through gentle mixing. Jar tests are used to determine the optimum pH and coagulant dose needed for effective coagulation and flocculation in water treatment.
This document describes an experiment to determine the acidity of a water sample. The experiment involves titrating the water sample with a standard sodium hydroxide (NaOH) solution using two different acid-base indicators - methyl orange and phenolphthalein. The titration with methyl orange determines the mineral acidity as mg/L of calcium carbonate (CaCO3), while titration with phenolphthalein determines the total acidity, including carbonic acid, as mg/L of CaCO3. The procedure, observations, and calculations for determining the mineral and total acidity are provided.
The document discusses sedimentation in water treatment. It defines sedimentation as the gravitational accumulation of solids at the bottom of water. It then discusses factors that affect sedimentation rates such as particle size and shape, water viscosity, and temperature. Stokes' formula and other equations for calculating particle settling velocity are provided. The main types of sedimentation tanks - quiescent/fill and draw, horizontal flow rectangular and circular, and vertical flow - are described. Key design considerations like surface overflow rate and detention period are also summarized. Finally, the need for periodic sludge removal from sedimentation tanks is mentioned.
The acidity of water is a measure of the quantitative capacity to react with a mineral base. The measured value usually varies with the pH indicator used in the experiment. The solution of phenolphthalein is colourless in acidic or mild basic medium (pH<8.0), while in basic medium (pH<9.6) solution is pink. The solution of methyl orange is generally red at pH lower than 3.1 and above pH 4.4 the solutions are yellow.
The dissolved strong mineral acids, weak organic acids, dissolved carbon dioxide and hydrolyzed mineral salts may contribute to the measured acidity of natural water. The acidity of water is a significant parameter of water as the presence of acids in natural water contributes to corrosiveness and influences chemical reaction rates. The biological processes are dependent on the acidity of water. The quantitative acidity measurement also reflects the quality of the source of water. The acidity of water is usually expressed in terms of CaCO3.
Estimation of types of alkalinity in waste water samplesRudradityo Saha
?
This document describes an experiment to determine the alkalinity of various water samples. It defines alkalinity as the amount of bases in a solution and lists the main components that contribute to alkalinity in water as carbonates, bicarbonates and hydroxides. The document outlines the procedure to titrate water samples with hydrochloric acid using phenolphthalein and methyl orange indicators. The results show that a sample of dirty water after washing clothes had the highest alkalinity at 750ppm, while water dripping from an air conditioner had the lowest alkalinity at 50ppm. Based on these alkalinity levels, the water dripping from the air conditioner was determined to be the most pure
chemical oxygen demand -analysis using APHA manualSHERIN RAHMAN
?
This document provides details on methods for analyzing chemical oxygen demand (COD) using standards from the American Public Health Association (APHA) manual. It describes three common COD analysis methods: the open reflux method, closed reflux titrimetric method, and closed reflux colorimetric method. For each method, it outlines the key steps, including refluxing samples with dichromate and sulfuric acid, and then titrating or measuring color change to determine the amount of dichromate consumed and calculate the COD level. The document also discusses interferences, limitations, sampling, and analysis of COD values both above and below 50 mg O2/L.
Estimation of total solids, total suspended solids and total dissolved solids...anju bala
?
The term solid refers to the matter either filtrable or non-filtrable that remains as residue upon evaporation and subsequent drying at a defined temperature.
In effluent, the total solids, total dissolved solids and total suspended solids are mainly composed of carbonates bicarbonates, chlorides, sulphates, nitrates, Ca, Mg, Na, K, Mn, organic matter, silts and other particles.
wholesomeness, Requirements for Domestic Use. Impurities in Water. Objects & purpose of Water Analysis.Collection of Samples. Classification of Analysis of Water: Physical,
Chemical & Biological Examination of Water.
Coagulation and flocculation are important water treatment processes used to remove small particles from water. Coagulation involves adding chemicals like aluminum sulfate or ferric chloride to destabilize colloidal particles and reduce charges. This allows particles to agglomerate into larger flocs during flocculation. Jar tests are used to determine the optimum pH and coagulant dose. Mechanical and hydraulic flocculators are then used to slowly mix water and form flocs, which are removed by sedimentation. Proper design of coagulant chambers, flocculators, and clarifiers is needed for effective treatment.
The document describes an experiment to determine the conductivity of a water sample. Conductivity is measured using a conductivity meter, which applies a voltage between electrodes in a probe immersed in the sample. This allows calculation of conductivity based on the resistance and current. The experiment involves calibrating the meter using a standard potassium chloride solution before measuring the conductivity of three water samples. The conductivity values obtained are then interpreted based on how conductivity relates to the concentration of dissolved ions in the water.
Lab 4 alkalinity –acidity and determination of alkalinity in waterAnas Maghayreh
?
Environmental lab
Lab 4 alkalinity –acidity and determination of alkalinity in water
experiment at JORDAN UNIVERSITY OF SCIENCE AND TECHNOLOGY
by: ANAS MAGHAYREH
This document discusses determining the alkalinity of a water sample through titration with dilute sulfuric acid using phenolphthalein and methyl orange indicators. Alkalinity is a measure of a water's capacity to neutralize acids and is primarily due to carbonate, bicarbonate, and hydroxide ions. The procedure involves adding sodium carbonate and an indicator to a water sample, then titrating with acid and recording the endpoint color changes to calculate alkalinity concentration.
This document discusses different types of solids found in water samples:
- Total Suspended Solids (TSS) are solids that can be filtered from water. Samples are filtered and weighed to determine TSS concentration.
- Total Dissolved Solids (TDS) pass through filters and remain dissolved in water. Samples are filtered, dried, and weighed to measure TDS.
- Volatile Suspended Solids (VSS) are organic solids that are lost upon ignition. Heating samples provides a rough estimate of organic matter.
- Total Solids (TS) is the total of all solids, including TSS, TDS, and VSS. Proced
Analysis of Alkalinity Acidity and TDS in water samplessuser074a2a1
?
This document discusses methods for analyzing the alkalinity, acidity, and total dissolved solids (TDS) in water samples. It describes how alkalinity is determined by titrating a sample with acid until the color change of an indicator is reached. Acidity is determined similarly using a base. TDS is measured by evaporating a water sample in an oven and weighing the residue. Alkalinity, acidity, and TDS are important water quality parameters.
The document discusses biochemical oxygen demand (BOD), which measures the amount of oxygen used by microorganisms to break down organic waste in water. When organic waste is present, bacteria consume dissolved oxygen to decompose the waste. BOD tests how much oxygen is absorbed over 5 days at 20°C. A high BOD level indicates more organic waste requiring decomposition, lowering available oxygen for aquatic life. BOD is used to measure water pollution and assess treatment plant performance by comparing raw sewage and treated effluent BOD levels. Proper BOD testing follows steps including sample collection, dilution, seeding with bacteria, initial and final oxygen readings, and calculations to determine BOD in mg/L.
The document discusses coagulation and flocculation processes used in water treatment. It begins by explaining that coagulation uses chemicals like aluminum and iron salts to neutralize the negative charges on small particles and colloids in water. This destabilizes the particles so they can agglomerate during flocculation. Flocculation is the process where the destabilized particles collide and form larger flocs that are easier to remove by sedimentation. Jar tests are used to determine the optimal pH and coagulant dose. Different types of flocculators including mechanical mixers and hydraulic designs that utilize baffles or differential settling are also described.
This Presentation Clarifying about potable Water analysis and their methods which i gave training on operation and maintenance team for Oman Al Ghubrah Independence Water Project (SWRO Desalination 42 MIGD)
This document describes a procedure to determine the acidity of a water sample through titration with sodium hydroxide solution. The acidity is measured as both mineral acidity at pH 3.7 using methyl orange indicator and total acidity at pH 8.3 using phenolphthalein indicator. Dissolved carbon dioxide is usually the major contributor to acidity in surface waters. The titration results are used to calculate and report the acidity levels in the sample as mg/L of calcium carbonate equivalent. High acidity can interfere with water treatment and affect aquatic life.
The document outlines various methods for determining types of solids in wastewater samples, including total solids, total suspended solids, volatile solids, fixed solids, total dissolved solids, and their significance for classifying wastewater and designing wastewater treatment processes. Gravimetric analysis methods are described for evaporating and igniting samples to separate organic and inorganic fractions. Standards for discharge of treated wastewater are also provided.
This document discusses coagulation and flocculation processes used in water treatment. It explains that coagulation uses chemicals like aluminum and iron salts to destabilize colloidal particles in water by neutralizing their negative charges. This allows the particles to agglomerate into larger flocs during flocculation. Flocculation is the process where these destabilized particles come together through gentle mixing. Jar tests are used to determine the optimum pH and coagulant dose needed for effective coagulation and flocculation in water treatment.
This document describes an experiment to determine the acidity of a water sample. The experiment involves titrating the water sample with a standard sodium hydroxide (NaOH) solution using two different acid-base indicators - methyl orange and phenolphthalein. The titration with methyl orange determines the mineral acidity as mg/L of calcium carbonate (CaCO3), while titration with phenolphthalein determines the total acidity, including carbonic acid, as mg/L of CaCO3. The procedure, observations, and calculations for determining the mineral and total acidity are provided.
The document discusses sedimentation in water treatment. It defines sedimentation as the gravitational accumulation of solids at the bottom of water. It then discusses factors that affect sedimentation rates such as particle size and shape, water viscosity, and temperature. Stokes' formula and other equations for calculating particle settling velocity are provided. The main types of sedimentation tanks - quiescent/fill and draw, horizontal flow rectangular and circular, and vertical flow - are described. Key design considerations like surface overflow rate and detention period are also summarized. Finally, the need for periodic sludge removal from sedimentation tanks is mentioned.
The acidity of water is a measure of the quantitative capacity to react with a mineral base. The measured value usually varies with the pH indicator used in the experiment. The solution of phenolphthalein is colourless in acidic or mild basic medium (pH<8.0), while in basic medium (pH<9.6) solution is pink. The solution of methyl orange is generally red at pH lower than 3.1 and above pH 4.4 the solutions are yellow.
The dissolved strong mineral acids, weak organic acids, dissolved carbon dioxide and hydrolyzed mineral salts may contribute to the measured acidity of natural water. The acidity of water is a significant parameter of water as the presence of acids in natural water contributes to corrosiveness and influences chemical reaction rates. The biological processes are dependent on the acidity of water. The quantitative acidity measurement also reflects the quality of the source of water. The acidity of water is usually expressed in terms of CaCO3.
Estimation of types of alkalinity in waste water samplesRudradityo Saha
?
This document describes an experiment to determine the alkalinity of various water samples. It defines alkalinity as the amount of bases in a solution and lists the main components that contribute to alkalinity in water as carbonates, bicarbonates and hydroxides. The document outlines the procedure to titrate water samples with hydrochloric acid using phenolphthalein and methyl orange indicators. The results show that a sample of dirty water after washing clothes had the highest alkalinity at 750ppm, while water dripping from an air conditioner had the lowest alkalinity at 50ppm. Based on these alkalinity levels, the water dripping from the air conditioner was determined to be the most pure
chemical oxygen demand -analysis using APHA manualSHERIN RAHMAN
?
This document provides details on methods for analyzing chemical oxygen demand (COD) using standards from the American Public Health Association (APHA) manual. It describes three common COD analysis methods: the open reflux method, closed reflux titrimetric method, and closed reflux colorimetric method. For each method, it outlines the key steps, including refluxing samples with dichromate and sulfuric acid, and then titrating or measuring color change to determine the amount of dichromate consumed and calculate the COD level. The document also discusses interferences, limitations, sampling, and analysis of COD values both above and below 50 mg O2/L.
Estimation of total solids, total suspended solids and total dissolved solids...anju bala
?
The term solid refers to the matter either filtrable or non-filtrable that remains as residue upon evaporation and subsequent drying at a defined temperature.
In effluent, the total solids, total dissolved solids and total suspended solids are mainly composed of carbonates bicarbonates, chlorides, sulphates, nitrates, Ca, Mg, Na, K, Mn, organic matter, silts and other particles.
wholesomeness, Requirements for Domestic Use. Impurities in Water. Objects & purpose of Water Analysis.Collection of Samples. Classification of Analysis of Water: Physical,
Chemical & Biological Examination of Water.
Coagulation and flocculation are important water treatment processes used to remove small particles from water. Coagulation involves adding chemicals like aluminum sulfate or ferric chloride to destabilize colloidal particles and reduce charges. This allows particles to agglomerate into larger flocs during flocculation. Jar tests are used to determine the optimum pH and coagulant dose. Mechanical and hydraulic flocculators are then used to slowly mix water and form flocs, which are removed by sedimentation. Proper design of coagulant chambers, flocculators, and clarifiers is needed for effective treatment.
The document describes an experiment to determine the conductivity of a water sample. Conductivity is measured using a conductivity meter, which applies a voltage between electrodes in a probe immersed in the sample. This allows calculation of conductivity based on the resistance and current. The experiment involves calibrating the meter using a standard potassium chloride solution before measuring the conductivity of three water samples. The conductivity values obtained are then interpreted based on how conductivity relates to the concentration of dissolved ions in the water.
Lab 4 alkalinity –acidity and determination of alkalinity in waterAnas Maghayreh
?
Environmental lab
Lab 4 alkalinity –acidity and determination of alkalinity in water
experiment at JORDAN UNIVERSITY OF SCIENCE AND TECHNOLOGY
by: ANAS MAGHAYREH
This document discusses determining the alkalinity of a water sample through titration with dilute sulfuric acid using phenolphthalein and methyl orange indicators. Alkalinity is a measure of a water's capacity to neutralize acids and is primarily due to carbonate, bicarbonate, and hydroxide ions. The procedure involves adding sodium carbonate and an indicator to a water sample, then titrating with acid and recording the endpoint color changes to calculate alkalinity concentration.
This document discusses different types of solids found in water samples:
- Total Suspended Solids (TSS) are solids that can be filtered from water. Samples are filtered and weighed to determine TSS concentration.
- Total Dissolved Solids (TDS) pass through filters and remain dissolved in water. Samples are filtered, dried, and weighed to measure TDS.
- Volatile Suspended Solids (VSS) are organic solids that are lost upon ignition. Heating samples provides a rough estimate of organic matter.
- Total Solids (TS) is the total of all solids, including TSS, TDS, and VSS. Proced
Analysis of Alkalinity Acidity and TDS in water samplessuser074a2a1
?
This document discusses methods for analyzing the alkalinity, acidity, and total dissolved solids (TDS) in water samples. It describes how alkalinity is determined by titrating a sample with acid until the color change of an indicator is reached. Acidity is determined similarly using a base. TDS is measured by evaporating a water sample in an oven and weighing the residue. Alkalinity, acidity, and TDS are important water quality parameters.
This document discusses soil pH and factors that influence it. It begins by explaining that soil pH is determined by the concentration of hydrogen ions (H+) and hydroxide ions (OH-) in the soil solution. It then discusses typical pH ranges for agricultural soils and different types of acidic and alkaline soils. The rest of the document covers measurement of soil pH using colorimetric indicators or a pH meter, factors that affect soil pH readings such as temperature and soil-water ratio, and precautions for using a glass pH electrode.
The document discusses body buffers and acid-base balance. It covers several key points in 3 sentences:
The human body maintains acid-base balance through various buffer systems, including bicarbonate, phosphate, and proteins, which help resist changes in pH. Respiratory mechanisms like breathing and renal mechanisms like kidney function also help regulate pH levels over different time periods. The Henderson-Hasselbalch equation relates the pH of a solution containing a weak acid and its conjugate base to their concentration ratio and defines acid-base properties crucial for cellular functions.
The document defines pH and describes how it is measured. It begins by explaining that pH was introduced in 1909 by Sorensen to express the concentration of hydrogen ions (H+) in a solution. It then defines pH mathematically as the negative logarithm of the H+ concentration. The rest of the document discusses:
- How pH is measured using indicators and pH meters
- How the pH scale was developed based on experimental measurements of H+ concentrations
- Examples of calculating pH from H+ concentration and calculating H- concentration from pH
- Applications of pH including in nature, soil, and acid rain
Introduction
History
Acid & Base
Ionization of water
Definitions of pH
(1) Mathematical Definition
(2) pH
(3) pOH
Buffer solution
(1) Types
(2) Buffer action
(3) Biological buffer systems
Henderson – Hasselbalch Equation
Measurement of pH
(1) pH Scale
(2) pH indicators
(3) pH meter
pH in human body and nature
Importance
Conclusion
Reference
The document provides information about acid-base titrations including Bronsted-Lowry and Lewis acid-base theories, the self-ionization of water, and examples of water acting as an acid or base. It also discusses acid-base indicators and how they can be used to detect the equivalence point during titrations. Examples are given for titrations involving strong acid-strong base, weak acid-strong base, and weak base-strong acid. The dependence of the titration curve on concentration is illustrated and factors that can affect the choice of indicator are described.
This experiment determines the strength of sodium hydroxide (NaOH) and sodium carbonate (Na2CO3) in a water sample. Standard hydrochloric acid (HCl) is titrated against sodium carbonate to determine its normality. The water sample is then titrated with HCl using phenolphthalein and methyl orange indicators. The volume of HCl used corresponds to the amount of NaOH and Na2CO3 present. Calculations are done to determine the normality and strength of NaOH and Na2CO3 in the water sample based on the titration results.
Discuss the carbonate conditioning and phosphate conditioning with respect to...SamiaSalman1
?
Discuss the carbonate conditioning and phosphate conditioning with respect to principles involved, advantages and limitations.numericals on total acidity and alkalinity
pH is a measure of acidity or alkalinity on a scale of 0 to 14. A pH below 7 is acidic, above 7 is alkaline, and 7 is neutral. pH is defined as the negative logarithm of hydrogen ion concentration and represents the ratio of hydrogen and hydroxide ions in solution. pH is measured using a pH meter which consists of electrodes, a meter, and buffers for calibration and provides a quantitative measurement of acidity or alkalinity. Temperature affects pH measurements so compensation is required for accurate readings.
The document summarizes an experiment on acid-base titrations. Sodium hydroxide was standardized and used to titrate hydrochloric acid, phosphoric acid, and an unknown acid. Titrations of hydrochloric acid showed the equivalence point was pH 7. Phosphoric acid titration showed two equivalence points, determining its two pKa values. Titration of the unknown acid found its molecular weight to be 76.09 g/mol, identifying it as tartaric acid. A final potassium hydrogen phthalate titration found the experimental curve nearly identical to the theoretical curve.
The document summarizes an experiment on acid-base titrations. Sodium hydroxide was standardized and used to titrate hydrochloric acid, phosphoric acid, and an unknown acid. Titrations of hydrochloric acid showed the equivalence point was pH 7. Phosphoric acid titration showed two equivalence points, determining its two pKa values. Titration of the unknown acid found its molecular weight to be 76.09 g/mol, identifying it as tartaric acid. A final potassium hydrogen phthalate titration found the experimental and theoretical titration curves nearly identical.
The document describes the Kjeldahl method for determining total nitrogen in a sample. It involves three main steps: digestion, distillation, and titration. In digestion, the sample is broken down in sulfuric acid to convert nitrogen into ammonium ions. Distillation transforms ammonium ions into ammonia gas, which is captured in an absorbing solution. Finally, titration uses sulfuric acid to determine the amount of ammonia in the solution, allowing calculation of the nitrogen content in the original sample. The Kjeldahl method is commonly used to indirectly estimate protein content through nitrogen levels and provides important information about water quality and soil fertility.
This document discusses pH measurement and provides details on:
- The definition and scale of pH as a measure of acidity or alkalinity.
- Why pH is measured in various industries and applications.
- The principles of pH measurement using a glass electrode and pH meter.
- Factors that affect pH measurement accuracy such as temperature, ionic strength, and electrode calibration.
- The process of calibrating pH electrodes using buffer solutions and adjusting for the Nernstian slope.
The document discusses acid-base balance and buffers. It provides:
1. The syllabus for MBBS and BDS programs which covers topics like pH, Henderson-Hasselbach equation, acid-base regulation in the human body, and importance of selectively permeable membranes.
2. Information on water functions in the body, its role in thermal regulation, and water movement via osmosis.
3. Definitions of acids, bases, pH, and how buffers work to resist pH changes when acids or bases are added. Common buffer systems in the body like bicarbonate are discussed.
4. Applications of the Henderson-Hasselbach equation to calculate pH changes, abundance of ion
Carbonate and bicarbonate ions in the sample can be determined by titrating it with against standard sulphuric acid (H2SO4) using phenolphthalein and methyl orange as indicators.
The document discusses pH electrodes and how pH meters work. It contains the following key points:
1. pH meters measure the voltage generated by a solution, which indicates the concentration of hydrogen ions and allows the measurement of pH.
2. A pH meter contains a glass electrode that interacts with hydrogen ions in the solution and a reference electrode to provide a baseline measurement.
3. The voltage measured corresponds to pH - a higher voltage means more hydrogen ions and lower pH, while a lower voltage means fewer hydrogen ions and higher pH.
4. Factors like the calibration standards used, junction potentials, temperature, and contaminants on the probe can introduce errors in pH measurements. Regular calibration and cleaning of electrodes
Breakout session Tuesday, February 11 at 1:30 p.m.
Precision Farming with Smart Soil Insights: How Advanced Soil Profiling Enhances Farm Economics and Ecology
Traditional soil analysis is limited in scope and insight. Breakthroughs with in-field sensors and in-lab analytics provide a complete soil profile to help maximize yield and minimize impact.
Speaker: Kiana Sinner, Thurston Conservation District
Water pollution occurs when harmful substances contaminate a body of water, making it toxic to humans and the environment.
Causes
Point source pollution: Pollution from specific sources like sewage treatment plants or factories
Diffuse pollution: Pollution from widespread sources like farming and power plants
Oil spills: Accidental spills, transportation, runoff, and intentional dumping
Industrial wastewater: Heavy metals, dyes, and other pollutants released into water bodies
Agricultural runoff: Fertilizers, pesticides, and salt
Kamil Pyciak, A Name Making Waves in the Digital Worldkamilpyciakinfo1
?
Kamil Pyciak, based in the USA, is a passionate explorer and nature lover who connects with a Polish audience through an international platform. Surrounded by America’s breathtaking landscapes, he ventures into national parks, capturing the essence of the wilderness through his lens. Despite being miles away from Poland, Kamil’s digital presence transcends borders, uniting a global community of outdoor enthusiasts. Through striking photography and engaging storytelling, he fosters a shared admiration for nature, proving that the love for the great outdoors is a universal language that brings people together across continents.
Day 2 Seminar Local Government Reorganisation and Planning Seminar_web.pptxmhutttch
?
Prepare for the impact of devolution and local government reorganisation! This workshop explores how these changes will affect planning and how local authorities can adapt smoothly. Hear insights from those in newly formed and combined authorities
Breakout session Tuesday, February 11 at 1:30 p.m.
Explore the value of STAR's adaptable framework in aligning state partners & amplifying conservation efforts using a locally led, science-based approach to evaluating & guiding practice adoption.
Speaker: Jake Deutmeyer, STAR: Saving Tomorrow's Agriculture Resources
This presentation explores the role of recalcitrant halocarbons in environmental microbiology, focusing on their persistence in ecosystems and the challenges they pose to microbial degradation. It covers the mechanisms by which certain halocarbons resist breakdown, their impact on soil and water quality, and the strategies employed by microbes to metabolize these stubborn compounds. The presentation also highlights current research, environmental concerns, and potential solutions for managing halocarbon contamination in various ecosystems. Ideal for students, researchers, and environmental professionals.
Governance of seabed integrity in the Baltic Seapermagoveu
?
Seabed integrity depends on the health and wellbeing of benthic habitats found on the seafloor. These habitats include geological and biological components that are constantly pressured by human activities e.g. dredging, bottom trawling.
PERMAGOV analysis of governance arrangements shows that the availability of knowledge is an essential enabler for seabed governance. Missing knowledge about the locations and extent of benthic habitat types, impacts of bottom trawling, cumulative impacts of activities, and the recovery potential of habitats hamper seabed governance.
Setting threshold values can support seabed governance by providing concrete quantified targets for seabed protection and legal depth for the enforcement of the MSFD.
Hear from experts on how well new NDCs are stacking up – both to curb emissions and protect communities from increasingly severe climate impacts – and what to look out for next. Speakers assess the plans submitted thus far and also share what to expect from key forthcoming submissions, such as those from China and the European Union, as well as consider the next steps in driving progress toward a net-zero future.
Presentación de Maria Tarrés, responsable de Estrategia de Sostenibilidad de SEAT, en el marco del XIII Simposio Empresarial Internacional, organizado por Funseam el pasado 3 de febrero de 2025, en Barcelona.
Más información en: https://funseam.com/xiii-simposio-empresarial-internacional-funseam-2025/
Environmental Engineering Practical Series - Alkalinity Test of Water
1. ALKALINITY TEST OF WATER
? It is the Acid Neutralizing property of water
?Caused due to presence of OH, CO3 & HCO3 ions
?Is analyzed by volumetric method by,
?Using Phenolphthalien & Methyl Orange indicators
?The principle behind this is mere chemical reaction,
?Between H+ and OH– ions
? It is to be noted that this is independent of pH
Theory / Principle
2. ? The presence of OH ions occurs at pH 8.5 or
above whereas CO3 ions occur at pH ranges
between 6.5 to 8.5 and lastly bicarbonate ions
ie. HCO3 occur when the pH falls down to 4.5
from 6.5.
? The reaction of acid and a base always result
in neutralizing pH to a scale of 7 and thus in
order to determine the Alkalinity of any water
body an acid is used for neutralizing OH, CO3
& HCO3 ions to H2O and CO2 respectively
3. Procedure
? Take 100mL sample in a 250mL capacity conical
flask
? In a burette take N/50 H2SO4 solution
? To the sample containing flask add 4-5 drops of
Phenolphthalien indicator
? Pink color indicating presence of OH and CO3
ions will appear
4. ? Now titrate the sample against H2SO4 till the
pink color disappears (colorless) (in this OH
combines with H and gets converted to H2O
and CO3 gets converted to HCO3)
? Note the value of N/50 H2SO4 consumed for
the color change of the sample as “P” or the
phenolphthalien end point.
? Now to the same sample add 1 drop of Methyl
Orange indicator
5. ? Pale yellow color indicating the presence of
HCO3 ions will appear
? Now without filling the burette again start the
titration from the same end point “P” till the
color changes to light orange (in this the HCO3
ions gets converted to H2O and CO2 by
reacting with H+ ions of the acid)
? Note down the final value of N/50 H2SO4
consumed to complete the analysis of
alkalinity as “T”
6. ? Repeat the whole experiment for finding the
concordant value of the acid consumed for
neutralizing the sample of water
? Using the equation –
N1V1 = N2V2
We have to find out the amount of Alkalinity causing
ions present in water either in mg/L or in p p m
(parts per million)
Calculations
7. 1. Phenolphthalien end point –
Vol. of H2SO4 used is “P” and is said to be V2 where
its normality is known as to be N2 ie. 1/50
By this the value of N1 or the concentration of
alkalinity causing ions can be found by implying the
formula –
N1 = N2V2/V1 = 1 X P = OH + CO3 alkalinity
50 X 100
In simpler way it can be taken as –
OH + CO3 Alkalinity = P X 1000 or P X 10 mg/L
100
8. 2. Methyl orange / Total end point –
Vol. of H2SO4 used is “T” and is said to be V2 where
its normality is known as to be N2 ie. 1/50
By this the value of N1 or the concentration of
alkalinity causing ions can be found by implying the
formula –
N1 = N2V2/V1 = 1 X T = HCO3 alkalinity in mg/L
50 X 100
In simpler way it can be taken as –
OH + CO3 Alkalinity = T X 1000 or T X 10 mg/L
100
9. ? Results are further interpreted by using the
below table
Values of P& T OH CO3 HCO3
P = T T 0 0
P = T / 2 0 2 P 0
P < T / 2 0 2 P T – 2 P
P > T / 2 2 P - T 2 (T – P) 0
P = 0 0 0 T
10. VIVA QUESTIONS
? Q. (1) why a given water sample can not be alkaline due to
the simultaneous presence of OH- and HCO3
-?
? Q. (2) What do you mean by the alkalinity of the water
sample?
? Q. (3) What are the drawbacks of the high alkalinity of the
water ?
? Q. (4) How you will conclude that the given water sample is
alkaline due to simultaneous presence of OH- and HCO3
-?
? Q.(5) How the alkalinity data are useful in environmental
engineering Practice?
? Q.(6) Why the pH of pond water is high? What type of
alkalinity would be present?