The varying temperatures and salinities of ocean water from around the world might play a role in the amount of CO2 that can be absorbed by that part of the ocean. If patterns could be found to those amounts and the carbon dioxide dissolution limit, then one could create a diagram of the world’s oceans and display where the most carbon dioxide could be absorbed, which also leads to where the most damage will be caused because of the maximum amount of ocean acidification. To test this question, solutions with various salinities (28, 34 and 38 ppt) were prepared. Dry ice was added to the solutions to find the maximum CO2 dissolution by identifying or measuring the pH using the pH indicator. Then the acidic solution was neutralized using baking soda and weighed to quantify the amount of baking soda dissolved. Then those steps are repeated at these temperatures (40, 57, 70 and 80 F) for each salinity to understand the dependency of temperature. Then using the data, plots are made to locate the maximum acidification by carbon dioxide in the oceans of the world. In general, the results stated that as salinity rises, the amount of carbon dioxide that can be absorbed by the ocean rises. As the temperature reaches a medium temperature at around 60 degrees Fahrenheit, the ocean water reaches its highest absorption potential. As temperatures get farther away from about 60 degrees Fahrenheit, the carbon dioxide absorption potential decreases.
International Journal of Engineering Research and Applications (IJERA) is an open access online peer reviewed international journal that publishes research and review articles in the fields of Computer Science, Neural Networks, Electrical Engineering, Software Engineering, Information Technology, Mechanical Engineering, Chemical Engineering, Plastic Engineering, Food Technology, Textile Engineering, Nano Technology & science, Power Electronics, Electronics & Communication Engineering, Computational mathematics, Image processing, Civil Engineering, Structural Engineering, Environmental Engineering, VLSI Testing & Low Power VLSI Design etc.
This document discusses various organic and inorganic compounds found in water. It covers topics like biochemical oxygen demand (BOD), chemical oxygen demand (COD), and suspended solids. For BOD and COD, it explains the test procedures and calculations used to measure levels of each compound. It also discusses how temperature affects BOD reaction rates. Inorganic compounds are classified as metals or non-metals. The document provides details on measuring parameters that indicate levels of organic pollution in water samples.
ESTIMATION OF DO, BOD AND COD IN CANAL WATER SAMPLESadia Rahat
The document discusses the estimation of dissolved oxygen (DO), biological oxygen demand (BOD), and chemical oxygen demand (COD) in a canal water sample. DO was found to be 3.20 ppm, BOD was 54.24 ppm, and COD was 220 ppm in the sample. BOD measures the amount of oxygen consumed by microorganisms to break down organic matter over 5 days. COD uses a strong chemical oxidant to measure total organic compounds and some inorganic compounds. While related, BOD and COD measure oxygen demand slightly differently. BOD is more relevant for organic-rich waters, while COD provides a faster test that is not affected by toxins.
Dissolved Oxygen Demand (DO) AND Chemical Oxygen Demand (COD) PDFchetansingh999
Dissolved oxygen (DO) refers to the level of oxygen present in water or other liquids. It is important for assessing water quality and supporting aquatic life. Chemical oxygen demand (COD) measures the amount of oxygen required to chemically break down pollutants in water. DO enters water through diffusion from air and as a byproduct of photosynthesis. It can be measured using electrochemical, optical, or colorimetric methods. COD is determined by using potassium dichromate as an oxidizing agent under acidic conditions, then measuring the amount of chromium formed.
Biochemical Oxygen Demand and its Industrial SignificanceAdnan Murad Bhayo
BOD is the amount of dissolved oxygen needed by aerobic biological organism in a body of water to breakdown organic material present in a given water sample at certain temperature over a specific time period .
Most of Bacteria in the aquatic columns are aerobic. Escherichia coli, Bacillus subtilis, Vibrio cholera.
Atmosphere contains 21% oxygen (210000 mg/dm3)
Higher the temperature of water higher will be the rate of respiration. So, concentration of oxygen decreases.
Many Animal species can grow and reproduce normally when dissolved oxygen level is ~ 5.0 mg/L.
HYPOXIA: When dissolve oxygen content below 3.0 mg/L. Many Species move elsewhere and immobile species may die
ANOXIA: When dissolve oxygen content below 0.5 mg/L. All aerobic species will die
Fertilizer contains Nitrate contributes to high BOD
Phosphate present in Soap and detergent that enhances the growth of algal blooms. As a result depletion of oxygen occur.
In a body of water with large amount of decaying organic material , the dissolved oxygen level may drop by 90 %, this would represent High BOD
In a body of water with small amount of decaying organic material , the dissolved oxygen level may drop by 10 %, this would represent Low BOD
ANALYSIS OF BOD OF WATER
Use glass bottles having 60 mL or greater capacity. Take samples of water.
Turn on the constant temperature chamber to allow the
controlled temperature to stabilize at 20°C ±1°C.
Record the DO level (ppm) of one immediately.
Place water sample in an incubator in complete darkness at 20 C for 5 days. Exclude all light to prevent possibility of photosynthetic production of DO
If don't have an incubator, wrap the water sample bottle in aluminum foil or black electrical tape and store in a dark place at room temperature (20o C or 68 °F).
DILUTION OF SAMPLE
Most relatively unpolluted streams have a BOD5 that ranges from 1 to 8 mg/L
Dilution is necessary when the amount of DO consumed by microorganisms is greater than the amount of DO available in the air-saturated.
If the BOD5 value of a sample is less than 7 mg/L, sample dilution is not needed.
The DO concentration after 5 days must be at least 1 mg/L and at least 2 mg/L lower in concentration than the initial DO
(American Public Health Association and others, 1995).
BOD of the dilution water is less than 0.2 mg/L.
Discard dilution water if there is any sign of biological growth.
pH of the dilution water needs to be maintained in a range suitable for bacterial growth
Bacterial growth is very good between 6.5 to 7.5
Sulfuric acid or sodium hydroxide may need to be added to the dilution water to lower or raise the pH, respectively.
CALCULATION:
The general equation for the determination of a BOD5 value is:
BOD = D1-D2/P
Where
D1 = initial DO of the sample,
D2 = final DO of the sample after 5 days, and
P = decimal volumetric fraction of sample used.
If 100 mL of sample a
pollution monitoring and control methods, COD lethovik
This document discusses pollution monitoring and control methods. It introduces different types of pollutants like nitrate, sulfate, and phosphate that come from sources such as fertilizers, industrial effluents, and sewage. These pollutants can cause eutrophication of water bodies and acid rain. The document then explains methods used to monitor waste water treatment like chemical oxygen demand, biochemical oxygen demand, and total organic carbon. It concludes by emphasizing the importance of preventing pollution to protect the environment and emphasizes reducing, reusing, and recycling to control pollution.
Distillery Wastewater Decontamination by the Fenton Advanced Oxidation MethodIJRES Journal
This study evaluated the effect of Fenton advanced oxidation process on the treatment of an industrial wastewater (distillery). The comparison of the effects of Fe2+ loadings, H2O2 dosages (2%(v/v)and 4%(v/v)), reaction temperature and reaction time, established optimum efficiency in terms of BOD and COD reductions. The best operating conditions for the treatment of the distillery wastewater containing 43.85 mg/L BOD concentration and 274.28 mg/L COD concentration in the raw effluent was 2% H2O2 dosage at constant loadings of Fe2+ (1.5 g), 80 oC pretreatment temperature, and 1 h reaction time. At this optimized condition, the BOD content reduced to about 35 mg/L (about 21% removal) and COD content reduced to about 53 mg/L (about 81% removal). There was a complete removal of the initial colour present in the wastewater after the treatment process. The process proved the ability to effectively reduce the COD content which when high in industrial wastewaters can lead to serious impacts to the environment.
International Journal of Engineering Research and Applications (IJERA) is an open access online peer reviewed international journal that publishes research and review articles in the fields of Computer Science, Neural Networks, Electrical Engineering, Software Engineering, Information Technology, Mechanical Engineering, Chemical Engineering, Plastic Engineering, Food Technology, Textile Engineering, Nano Technology & science, Power Electronics, Electronics & Communication Engineering, Computational mathematics, Image processing, Civil Engineering, Structural Engineering, Environmental Engineering, VLSI Testing & Low Power VLSI Design etc.
This document discusses various organic and inorganic compounds found in water. It covers topics like biochemical oxygen demand (BOD), chemical oxygen demand (COD), and suspended solids. For BOD and COD, it explains the test procedures and calculations used to measure levels of each compound. It also discusses how temperature affects BOD reaction rates. Inorganic compounds are classified as metals or non-metals. The document provides details on measuring parameters that indicate levels of organic pollution in water samples.
ESTIMATION OF DO, BOD AND COD IN CANAL WATER SAMPLESadia Rahat
The document discusses the estimation of dissolved oxygen (DO), biological oxygen demand (BOD), and chemical oxygen demand (COD) in a canal water sample. DO was found to be 3.20 ppm, BOD was 54.24 ppm, and COD was 220 ppm in the sample. BOD measures the amount of oxygen consumed by microorganisms to break down organic matter over 5 days. COD uses a strong chemical oxidant to measure total organic compounds and some inorganic compounds. While related, BOD and COD measure oxygen demand slightly differently. BOD is more relevant for organic-rich waters, while COD provides a faster test that is not affected by toxins.
Dissolved Oxygen Demand (DO) AND Chemical Oxygen Demand (COD) PDFchetansingh999
Dissolved oxygen (DO) refers to the level of oxygen present in water or other liquids. It is important for assessing water quality and supporting aquatic life. Chemical oxygen demand (COD) measures the amount of oxygen required to chemically break down pollutants in water. DO enters water through diffusion from air and as a byproduct of photosynthesis. It can be measured using electrochemical, optical, or colorimetric methods. COD is determined by using potassium dichromate as an oxidizing agent under acidic conditions, then measuring the amount of chromium formed.
Biochemical Oxygen Demand and its Industrial SignificanceAdnan Murad Bhayo
BOD is the amount of dissolved oxygen needed by aerobic biological organism in a body of water to breakdown organic material present in a given water sample at certain temperature over a specific time period .
Most of Bacteria in the aquatic columns are aerobic. Escherichia coli, Bacillus subtilis, Vibrio cholera.
Atmosphere contains 21% oxygen (210000 mg/dm3)
Higher the temperature of water higher will be the rate of respiration. So, concentration of oxygen decreases.
Many Animal species can grow and reproduce normally when dissolved oxygen level is ~ 5.0 mg/L.
HYPOXIA: When dissolve oxygen content below 3.0 mg/L. Many Species move elsewhere and immobile species may die
ANOXIA: When dissolve oxygen content below 0.5 mg/L. All aerobic species will die
Fertilizer contains Nitrate contributes to high BOD
Phosphate present in Soap and detergent that enhances the growth of algal blooms. As a result depletion of oxygen occur.
In a body of water with large amount of decaying organic material , the dissolved oxygen level may drop by 90 %, this would represent High BOD
In a body of water with small amount of decaying organic material , the dissolved oxygen level may drop by 10 %, this would represent Low BOD
ANALYSIS OF BOD OF WATER
Use glass bottles having 60 mL or greater capacity. Take samples of water.
Turn on the constant temperature chamber to allow the
controlled temperature to stabilize at 20°C ±1°C.
Record the DO level (ppm) of one immediately.
Place water sample in an incubator in complete darkness at 20 C for 5 days. Exclude all light to prevent possibility of photosynthetic production of DO
If don't have an incubator, wrap the water sample bottle in aluminum foil or black electrical tape and store in a dark place at room temperature (20o C or 68 °F).
DILUTION OF SAMPLE
Most relatively unpolluted streams have a BOD5 that ranges from 1 to 8 mg/L
Dilution is necessary when the amount of DO consumed by microorganisms is greater than the amount of DO available in the air-saturated.
If the BOD5 value of a sample is less than 7 mg/L, sample dilution is not needed.
The DO concentration after 5 days must be at least 1 mg/L and at least 2 mg/L lower in concentration than the initial DO
(American Public Health Association and others, 1995).
BOD of the dilution water is less than 0.2 mg/L.
Discard dilution water if there is any sign of biological growth.
pH of the dilution water needs to be maintained in a range suitable for bacterial growth
Bacterial growth is very good between 6.5 to 7.5
Sulfuric acid or sodium hydroxide may need to be added to the dilution water to lower or raise the pH, respectively.
CALCULATION:
The general equation for the determination of a BOD5 value is:
BOD = D1-D2/P
Where
D1 = initial DO of the sample,
D2 = final DO of the sample after 5 days, and
P = decimal volumetric fraction of sample used.
If 100 mL of sample a
pollution monitoring and control methods, COD lethovik
This document discusses pollution monitoring and control methods. It introduces different types of pollutants like nitrate, sulfate, and phosphate that come from sources such as fertilizers, industrial effluents, and sewage. These pollutants can cause eutrophication of water bodies and acid rain. The document then explains methods used to monitor waste water treatment like chemical oxygen demand, biochemical oxygen demand, and total organic carbon. It concludes by emphasizing the importance of preventing pollution to protect the environment and emphasizes reducing, reusing, and recycling to control pollution.
Distillery Wastewater Decontamination by the Fenton Advanced Oxidation MethodIJRES Journal
This study evaluated the effect of Fenton advanced oxidation process on the treatment of an industrial wastewater (distillery). The comparison of the effects of Fe2+ loadings, H2O2 dosages (2%(v/v)and 4%(v/v)), reaction temperature and reaction time, established optimum efficiency in terms of BOD and COD reductions. The best operating conditions for the treatment of the distillery wastewater containing 43.85 mg/L BOD concentration and 274.28 mg/L COD concentration in the raw effluent was 2% H2O2 dosage at constant loadings of Fe2+ (1.5 g), 80 oC pretreatment temperature, and 1 h reaction time. At this optimized condition, the BOD content reduced to about 35 mg/L (about 21% removal) and COD content reduced to about 53 mg/L (about 81% removal). There was a complete removal of the initial colour present in the wastewater after the treatment process. The process proved the ability to effectively reduce the COD content which when high in industrial wastewaters can lead to serious impacts to the environment.
This document discusses chemical oxygen demand (COD) testing. COD testing measures the amount of organic matter in water by determining the oxygen required to chemically oxidize the matter. Potassium dichromate is commonly used as the strong oxidizing agent. The COD test procedure involves refluxing a water sample with dichromate and sulfuric acid, then titrating the remaining dichromate with ferrous ammonium sulfate to determine the COD level in mg/L. COD testing provides faster results than biochemical oxygen demand (BOD) testing and oxidizes a wider range of compounds, though the results do not directly correlate to 5-day BOD levels.
Nutrient loads and heavy metals assessment along sosiani river, kenya.Alexander Decker
This document summarizes a study that analyzed nutrient loads and heavy metal levels along the Sosiani River in Kenya. Water, soil, and sediment samples were collected from 5 sites along the river and analyzed for nitrates, phosphates, and heavy metals. Nitrate and phosphate levels were found to be below recommended limits. However, concentrations of heavy metals like iron, lead, cadmium, zinc, and copper exceeded Kenyan standards, with zinc levels above WHO standards for drinking water. The study concluded that the river water is not safe for domestic use due to heavy metal contamination.
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 information about wastewater engineering as part of a civil engineering course. It discusses why wastewater engineering is important when pollution loads exceed the environment's carrying capacity. Nature has limits on its ability to self-purify, so wastewater treatment systems must be engineered to treat pollutants within smaller areas and timeframes. The document then covers characteristics of wastewater, parameters for analysis including biochemical oxygen demand, and methods for determining measures like total and volatile solids.
The document discusses the biochemical oxygen demand (BOD) test procedure for determining the amount of dissolved oxygen consumed by microorganisms while decomposing organic matter in water samples over a 5 day period. It provides background on BOD and dissolved oxygen, lists the necessary supplies and reagents, and describes the steps to conduct the BOD test and calculate results to evaluate water quality. A 5-day duration is used for the BOD test because most of the biodegradable organic matter will be degraded within 5 days if sufficient microorganisms and oxygen are present.
This study examined how pH and redox potential (Eh) influence the leaching of mercury from mining waste materials. Laboratory experiments were conducted by varying the pH from 2 to 12 and Eh under different gas purging conditions. Results showed that mercury concentration in leachates increased with rising pH until pH 10.65, above which it sharply decreased. The presence of iron significantly reduced mercury concentrations by 1/10th to 1/100th. Varying the Eh had little effect on mercury leaching, except when hydrogen peroxide was added to increase Eh, which sharply increased mercury levels. Alkaline and reduced conditions enhanced mercury solubility the most.
The document summarizes a study that measured dissolved oxygen levels at 5 sites along a river using the Winkler method. The results showed variations in DO levels across sites, with the highest amount at Site E (10.7 mg/L) and the lowest at Site C (3.9 mg/L). Factors like temperature, nutrients, and water flow can affect dissolved oxygen concentrations in aquatic environments.
Routine analysis of wastewaters quality parametersArvind Kumar
This document discusses parameters for analyzing waste water quality. It describes the objectives of waste water analysis which include monitoring treatment plant efficiency. Physical analyses examine characteristics like color and odor, while chemical analyses determine substance amounts. Key parameters discussed include biochemical oxygen demand (BOD), chemical oxygen demand (COD), dissolved oxygen, pH, nitrogen, and solids. BOD testing measures oxygen consumed by bacteria breaking down organic matter over time. COD testing uses chemical oxidization to similarly assess ability to consume oxygen. Their ratio provides information on a waste water's biodegradability.
The document describes an experiment to measure water pollution using biochemical oxygen demand (BOD), chemical oxygen demand (COD), and dissolved oxygen (DO). [1] The experiment tested leachate from a landfill and a nearby river. [2] The leachate had much higher COD and BOD levels compared to the river, indicating it was highly polluted and possibly polluting the river. [3] BOD measures biodegradable pollution over 5 days while COD more quickly measures all oxidizable chemicals, so COD is usually higher.
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
The document describes an experiment to measure biochemical oxygen demand (BOD) of various water samples. BOD is a measure of the amount of oxygen consumed by microorganisms as they break down organic matter in water. The experiment involves taking water samples from a river, lake, and rain water, incubating them for 5 days, and measuring the dissolved oxygen levels initially and after 5 days. The BOD values were calculated and reported. The results showed that river water had the highest BOD at 2.4 mg/L, indicating more organic matter to be broken down by microbes. The conclusion discusses how BOD is used to understand how organic pollutants affect dissolved oxygen levels in water bodies.
Technetium sorption by anionexchange resins, inorganic sorbents, natural minerals and rocks. Effect of radiation. Precipitstion of sulfide. Solubility of sulfide.
This document provides information on measuring dissolved oxygen (DO) in water and wastewater samples. It describes proper sampling methods and sample preservation to ensure accurate results. The modified Winkler titration method and electrochemical meter method for analyzing DO are explained, including necessary reagents, equipment, and procedures. Maintaining clean sample containers and calibrating meters daily are emphasized for obtaining reliable DO measurements.
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)
The document discusses the biochemical oxygen demand (BOD) method for determining sewage quality. It defines BOD as the amount of dissolved oxygen needed by organisms to break down organic material in water. The most common BOD test is the 5-day BOD (BOD5) test, which measures the oxygen demand over a 5-day incubation period at 20°C. Elevated BOD levels can be caused by human/animal waste, fertilizer runoff, and higher water temperatures that increase plant growth. The document outlines the detailed procedures for conducting the BOD5 test and analyzing the results. It notes advantages of the test being simple and widely used but disadvantages include its long incubation period and susceptibility to inhibition.
The document discusses using forward osmosis (FO) to treat reverse osmosis concentrate (ROC) from water treatment plants. It examines using FO alone and with granular activated carbon (GAC) pretreatment to reduce the volume of ROC and remove organic micropollutants. Five steps of FO using 2-3M NaCl as the draw solution reduced the ROC volume to 8%. FO rejected some organic micropollutants but GAC pretreatment followed by FO removed almost all organic micropollutants from the ROC. Reducing the pH of the ROC feed solution arrested flux decline caused by fouling during FO.
The microprocessor based automatic, advance, electronic and latest designed COD Analyzers are used for detection of Chemical Oxygen Demand. The Laboratory COD analyzer acts as water analyzer for detection of Chemical Oxygen Demand in both polluted and normal water. Weiber water analyzer works as high quality analysis tool for determination of inorganic pollution, waste water, sewage and Plant Effluent Treatment. For More Information Please Logon http://goo.gl/gaktwZ
IA Design and interesting reseach questionsLawrence kok
This document describes several experiments investigating the kinetics and rates of various chemical reactions through measuring changes over time. It includes studying the effect of temperature on the rate of decomposition of hydrogen peroxide and determining the activation energy using the iodine clock reaction. Other proposed experiments examine the rates of dissolution of seashells in carbonated water, dissolving of candies in water at different temperatures, and decolorization of dyes with changes in reactants.
Salinity is a measure of the total amount of dissolved salts in water, measured in grams per kilogram or parts per thousand. Seawater contains 11 major dissolved constituents that make up over 99.99% of all dissolved materials, with the largest proportions being chloride at 55.07% and sodium at 30.62%. Salinity affects the distribution of ocean plants and animals as well as other seawater properties like density and dissolved oxygen levels.
This document discusses chemical oxygen demand (COD) testing. COD testing measures the amount of organic matter in water by determining the oxygen required to chemically oxidize the matter. Potassium dichromate is commonly used as the strong oxidizing agent. The COD test procedure involves refluxing a water sample with dichromate and sulfuric acid, then titrating the remaining dichromate with ferrous ammonium sulfate to determine the COD level in mg/L. COD testing provides faster results than biochemical oxygen demand (BOD) testing and oxidizes a wider range of compounds, though the results do not directly correlate to 5-day BOD levels.
Nutrient loads and heavy metals assessment along sosiani river, kenya.Alexander Decker
This document summarizes a study that analyzed nutrient loads and heavy metal levels along the Sosiani River in Kenya. Water, soil, and sediment samples were collected from 5 sites along the river and analyzed for nitrates, phosphates, and heavy metals. Nitrate and phosphate levels were found to be below recommended limits. However, concentrations of heavy metals like iron, lead, cadmium, zinc, and copper exceeded Kenyan standards, with zinc levels above WHO standards for drinking water. The study concluded that the river water is not safe for domestic use due to heavy metal contamination.
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 information about wastewater engineering as part of a civil engineering course. It discusses why wastewater engineering is important when pollution loads exceed the environment's carrying capacity. Nature has limits on its ability to self-purify, so wastewater treatment systems must be engineered to treat pollutants within smaller areas and timeframes. The document then covers characteristics of wastewater, parameters for analysis including biochemical oxygen demand, and methods for determining measures like total and volatile solids.
The document discusses the biochemical oxygen demand (BOD) test procedure for determining the amount of dissolved oxygen consumed by microorganisms while decomposing organic matter in water samples over a 5 day period. It provides background on BOD and dissolved oxygen, lists the necessary supplies and reagents, and describes the steps to conduct the BOD test and calculate results to evaluate water quality. A 5-day duration is used for the BOD test because most of the biodegradable organic matter will be degraded within 5 days if sufficient microorganisms and oxygen are present.
This study examined how pH and redox potential (Eh) influence the leaching of mercury from mining waste materials. Laboratory experiments were conducted by varying the pH from 2 to 12 and Eh under different gas purging conditions. Results showed that mercury concentration in leachates increased with rising pH until pH 10.65, above which it sharply decreased. The presence of iron significantly reduced mercury concentrations by 1/10th to 1/100th. Varying the Eh had little effect on mercury leaching, except when hydrogen peroxide was added to increase Eh, which sharply increased mercury levels. Alkaline and reduced conditions enhanced mercury solubility the most.
The document summarizes a study that measured dissolved oxygen levels at 5 sites along a river using the Winkler method. The results showed variations in DO levels across sites, with the highest amount at Site E (10.7 mg/L) and the lowest at Site C (3.9 mg/L). Factors like temperature, nutrients, and water flow can affect dissolved oxygen concentrations in aquatic environments.
Routine analysis of wastewaters quality parametersArvind Kumar
This document discusses parameters for analyzing waste water quality. It describes the objectives of waste water analysis which include monitoring treatment plant efficiency. Physical analyses examine characteristics like color and odor, while chemical analyses determine substance amounts. Key parameters discussed include biochemical oxygen demand (BOD), chemical oxygen demand (COD), dissolved oxygen, pH, nitrogen, and solids. BOD testing measures oxygen consumed by bacteria breaking down organic matter over time. COD testing uses chemical oxidization to similarly assess ability to consume oxygen. Their ratio provides information on a waste water's biodegradability.
The document describes an experiment to measure water pollution using biochemical oxygen demand (BOD), chemical oxygen demand (COD), and dissolved oxygen (DO). [1] The experiment tested leachate from a landfill and a nearby river. [2] The leachate had much higher COD and BOD levels compared to the river, indicating it was highly polluted and possibly polluting the river. [3] BOD measures biodegradable pollution over 5 days while COD more quickly measures all oxidizable chemicals, so COD is usually higher.
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
The document describes an experiment to measure biochemical oxygen demand (BOD) of various water samples. BOD is a measure of the amount of oxygen consumed by microorganisms as they break down organic matter in water. The experiment involves taking water samples from a river, lake, and rain water, incubating them for 5 days, and measuring the dissolved oxygen levels initially and after 5 days. The BOD values were calculated and reported. The results showed that river water had the highest BOD at 2.4 mg/L, indicating more organic matter to be broken down by microbes. The conclusion discusses how BOD is used to understand how organic pollutants affect dissolved oxygen levels in water bodies.
Technetium sorption by anionexchange resins, inorganic sorbents, natural minerals and rocks. Effect of radiation. Precipitstion of sulfide. Solubility of sulfide.
This document provides information on measuring dissolved oxygen (DO) in water and wastewater samples. It describes proper sampling methods and sample preservation to ensure accurate results. The modified Winkler titration method and electrochemical meter method for analyzing DO are explained, including necessary reagents, equipment, and procedures. Maintaining clean sample containers and calibrating meters daily are emphasized for obtaining reliable DO measurements.
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)
The document discusses the biochemical oxygen demand (BOD) method for determining sewage quality. It defines BOD as the amount of dissolved oxygen needed by organisms to break down organic material in water. The most common BOD test is the 5-day BOD (BOD5) test, which measures the oxygen demand over a 5-day incubation period at 20°C. Elevated BOD levels can be caused by human/animal waste, fertilizer runoff, and higher water temperatures that increase plant growth. The document outlines the detailed procedures for conducting the BOD5 test and analyzing the results. It notes advantages of the test being simple and widely used but disadvantages include its long incubation period and susceptibility to inhibition.
The document discusses using forward osmosis (FO) to treat reverse osmosis concentrate (ROC) from water treatment plants. It examines using FO alone and with granular activated carbon (GAC) pretreatment to reduce the volume of ROC and remove organic micropollutants. Five steps of FO using 2-3M NaCl as the draw solution reduced the ROC volume to 8%. FO rejected some organic micropollutants but GAC pretreatment followed by FO removed almost all organic micropollutants from the ROC. Reducing the pH of the ROC feed solution arrested flux decline caused by fouling during FO.
The microprocessor based automatic, advance, electronic and latest designed COD Analyzers are used for detection of Chemical Oxygen Demand. The Laboratory COD analyzer acts as water analyzer for detection of Chemical Oxygen Demand in both polluted and normal water. Weiber water analyzer works as high quality analysis tool for determination of inorganic pollution, waste water, sewage and Plant Effluent Treatment. For More Information Please Logon http://goo.gl/gaktwZ
IA Design and interesting reseach questionsLawrence kok
This document describes several experiments investigating the kinetics and rates of various chemical reactions through measuring changes over time. It includes studying the effect of temperature on the rate of decomposition of hydrogen peroxide and determining the activation energy using the iodine clock reaction. Other proposed experiments examine the rates of dissolution of seashells in carbonated water, dissolving of candies in water at different temperatures, and decolorization of dyes with changes in reactants.
Salinity is a measure of the total amount of dissolved salts in water, measured in grams per kilogram or parts per thousand. Seawater contains 11 major dissolved constituents that make up over 99.99% of all dissolved materials, with the largest proportions being chloride at 55.07% and sodium at 30.62%. Salinity affects the distribution of ocean plants and animals as well as other seawater properties like density and dissolved oxygen levels.
Soma Sekhar Sriadibhatla presented on the effects of increasing carbon dioxide levels in the environment and methods of sequestering carbon dioxide. The presentation discussed how rising CO2 levels are leading to global warming and ocean acidification. Testing of water samples from Visakhapatnam, India found decreasing pH levels and carbonate ion concentrations over time, indicating ongoing ocean acidification. The presentation proposed carbon dioxide sequestration techniques including reversible adsorption and discussed using captured CO2 for commercial purposes like enhanced oil recovery. It concluded more must be done to regulate CO2 emissions and deal with issues like global warming and ocean acidification.
This presentation focuses, how carbon dioxide plays dirty role in Ocean Acidification and Global Warming. I have analyzed data and presented it with some real samples collected from Visakhapatnam, India. Thank you!
this presentation showsChemical oxygen demand (mg O2 / lit.) which is the amount of oxygen required for reacting with the organic (harmful) matter present in waste water, both soluble or insoluble (suspended) matters, producing CO2 and H2O. In this experiment, organic compounds are oxidized to carbon dioxide and water by a boiling acid dichromate solution
Materials
Waste water sample.
Distilled water.
Potassium dichromate (K2Cr2O7).
Sulfuric acid (H2SO4).
Silver sulfate (Ag2SO4).
Mercuric sulfate (HgSO4).
and procedures
Take a sample of waste water (2.5 ml) in a standard test tube.
Add K2Cr2O7 (1.5 ml) to the above sample.
Add 3.5 ml of a solution containing H2SO4, Ag2SO4 and HgSO4 to the above mixture. This solution is known as "digestion solution" which is prepared by adding Ag2SO4 and HgSO4 to 1 kg of H2SO4.
Repeat the above procedure with a sample of distilled water (2.5 ml) in another test tube.
Heat the two test tubes in the reactor for 2 hrs. at a temperature of 150 ºC and after that leave them to cool.
Use the spectrophotometer to detect the COD (in mg/lit.) value for the waste water sample.
some notes
K2Cr2O7 is used as an oxidizing agent (source of oxygen needed to react with organic matters).
H2SO4 is a digesting agent which helps in decomposing the organic matters to be easily reacted with oxygen.
Ag2SO4 is used to reduce the volatility of the organic matters exist in the waste water sample and keep them in liquid phase. If those matters vaporized, the measured value of COD will be incorrect.
HgSO4 is used to avoid oxidation of 〖𝐶𝑙〗^− if it exists in wastewater as salt. This will lead to high misleading value of COD since 〖𝐶𝑙〗^− is oxidized by K2Cr2O7 into Cl2.
The distilled water sample is used as a blank sample which allows the calibration of the spectrophotometer. The COD value for this sample is zero.
also shows Biological oxygen demand (mg O2 / lit.) is the amount of oxygen required to be used up by bacteria so as to decompose the waste matters in a liter of wastewater. This test may need at least 3 months to be finished: the standard test defines it as BOD5 as it is performed within 5 days only. During those 5 days, about 70 – 80% of degradation is achieved.
In the COD test we completely oxidize the wastes, whether biodegradable (i.e. can be decomposed by bacteria) or non – biodegradable.
In the BOD test we oxidize the biodegradable wastes only.
Determination of the BOD5 of undiluted samples of sewage containing high levels of industrial pollutants may be considerably impaired(damaged) by the presence of inhibitors or toxic substances. Measurements can only be carried out after the sample has been diluted with dilution water that contains a sufficient amount of nutrients and microorganisms in order to reduce the interfering substances to an acceptable level.
Determination of the BOD5 of undiluted samples of sewage containing high levels of industrial pollutants may be considerably impaired(damaged) by the presence of CO
This document summarizes a student's experiment investigating whether aquatic plants can combat ocean acidification by absorbing atmospheric carbon dioxide. The student hypothesized that introducing duckweed to a carbon dioxide-acidified freshwater environment would increase the pH level. The experiment involved measuring the pH and number of duckweed fronds over 10 days in jars with and without duckweed exposed to carbon dioxide levels 10 times atmospheric concentration. The results showed no significant difference in pH changes or duckweed growth between the jars. While plants could help locally, the carbon dioxide levels used were too high for the duckweed to significantly affect acidification. Further experimentation is needed to fully understand the relationship between aquatic plants and ocean acidification.
Carbon and oxygen cycling are directly linked through photosynthesis and respiration. Photosynthesis uses carbon dioxide and releases oxygen, while respiration uses oxygen and releases carbon dioxide. Measuring gas exchange in aquatic samples is ideal because dissolved gases are more easily handled in the lab than atmospheric gases. A plankton community in water provides a microcosm of autotrophs and heterotrophs. This experiment will use light and dark bottles to see how dissolved oxygen changes with and without photosynthesis over an incubation period. The hypothesis is that dark bottles will have lower dissolved oxygen than light bottles after incubation.
Determination of p h of waste water sample .....................................Hafiz M Waseem
ecologyDetermination of pH of Waste Water Sample ..................................................... 4
Determination Dissolved Oxygen within Water ................................................... 5
Adaptive Features of Animals in Relation to Food and Environment .................. 7
Study the Plant Population Density ................................................................... 10
Experimental Design and Approaches to Ecological Research ........................ 12
This document provides instructions for measuring water salinity using either a hydrometer or titration method as part of the GLOBE hydrology protocol, describing how to select a study site, the importance of salinity measurements, and steps for conducting the salinity protocol and recording data. It explains that salinity measures the total dissolved solids in water and can provide insights into environmental conditions and changes over time. The document also provides examples of how salinity levels vary in different water bodies and responds to climate factors like evaporation.
The study compared water quality parameters of greywater samples collected before and after treatment from four systems in Monteverde, Costa Rica. While water quality did not significantly differ before and after treatment within systems, some parameters differed between systems after treatment. Specifically, samples from the Monteverde Institute system had significantly higher conductivity, total dissolved solids, and salinity than other systems, possibly due to sediment and stagnant water. Samples from the Monteverde Country Lodge system had significantly higher nitrate nitrogen, likely due to its treatment of both greywater and blackwater. The study found treatment systems can improve some greywater quality aspects but their effectiveness depends on system design and water sources.
This document discusses factors that affect biochemical oxygen demand (BOD), including ultimate BOD, BOD rate constant, nature of waste, ability of organisms to utilize waste, and temperature. Ultimate BOD represents the maximum oxygen demand of a waste. The BOD rate constant depends on these factors and indicates how quickly oxygen will be depleted. Simple sugars degrade quickly while more complex compounds degrade more slowly. The organisms used to inoculate BOD tests may not be able to degrade all waste components. BOD tests are conducted at 20°C to standardize temperature effects and allow comparison of results.
Laboratory manual of water supply and sewerage engineeringTaufique Hasan
This document provides the procedure for determining the total alkalinity of water through titration. It defines alkalinity as the capacity of water to neutralize acids and discusses the significance of alkalinity measurements in water and wastewater treatment. The procedure involves titrating a water sample with sulfuric acid to two end points using phenolphthalein and methyl orange indicators. The ml of acid used is then used to calculate the total, hydroxide, carbonate, and bicarbonate alkalinity concentrations in the sample.
Sterlization of water using bleaching powder Gaurav Sharma
The document describes an experiment to determine the dosage of bleaching powder required to sterilize different water samples. It includes a certificate of authenticity, acknowledgements, introduction on water purification techniques, theory on bleaching powder preparation, experimental procedure, observations, calculations and results. The key findings are that 0.215gm, 1.077gm and 1.231gm of bleaching powder are required to sterilize 1 liter of Bisleri water, rain water and borewell water respectively.
This document discusses various physicochemical parameters that are used to test water quality, including temperature, pH, electrical conductivity, carbon dioxide, alkalinity, bicarbonate, biochemical oxygen demand (BOD), and chemical oxygen demand (COD). It explains that water quality must be regularly monitored and tested against these parameters to ensure it is safe for drinking, domestic, agricultural, and industrial uses. Each parameter is important to measure as it provides insight into the water ecosystem and potential contamination issues.
Samantha Miller worked on the Denitrification project, performing sample preservation and pH/alkalinity tests every Friday from 11am to 2pm. Proper sample preparation and testing of pH and alkalinity is important to monitor conditions for nitrifying bacteria and algae growth. Data tables show results for pH, alkalinity, and nitrate levels over time for the influent and three ponds. pH levels affected nitrate levels on some dates. Pond death occurred on November 28 when pH conditions hindered algae and bacteria, though the reason for death is unclear. The experience provided insights into water treatment processes.
This document summarizes a study that examined the impact of water chemistry on the dissolution of lead carbonate in drinking water distribution systems. Specifically, it investigated the effects of pH (7.0-9.5), temperature (5°C vs 20°C), and alkalinity (moderate vs low) on the dissolution of hydrocerussite and cerussite in batch experiments. The results showed that pH did not significantly impact dissolution from 7.0-9.5. Cold temperature (5°C) and moderate alkalinity decreased the solubility of lead species, which was unexpected. The purpose was to better understand how water chemistry affects the stability of lead corrosion scales and the release of lead into drinking water.
This document discusses dissolved oxygen (DO) in aquatic environments. It provides background on DO including its importance to aquatic organisms and factors that affect its concentration. Methods are described for measuring DO directly in water or from samples. Key points include:
- DO is vital for aquatic life and its concentration indicates water quality. Higher DO supports more diversity.
- Factors like temperature, aquatic plants, decaying matter, and human activities influence DO levels.
- DO can be measured on site or from stored samples. Proper collection and storage methods are outlined.
A STUDY ON OCEAN ACIDIFICATION DUE TO CARBON DIOXIDE ALONG THE COAST OF VISAK...Soma Sekhar Sriadibhatla
Extensive Data Analytics on samples to understand Ocean Acidification process, a serious damage to ecosystem, increase in production of Carbon dioxide.
This document contains instructions for a lab experiment to determine the rate of oxygen consumption in a fish and the effect of temperature on the operculum movement of a fish. It provides background information on fish respiration and how temperature affects physiological processes. The procedure for the oxygen consumption experiment involves measuring the dissolved oxygen content of water with and without a fish, while the temperature experiment involves counting operculum movements of a fish at different temperatures. Safety precautions for the lab are also listed.
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.
Similar to The Effect of Surface Temperature and Salinity of Ocean Water on Carbon Dioxide Absorption (20)
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...Open Access Research Paper
Water polluted by dyestuffs compounds is a global threat to health and the environment; accordingly, we prepared a green novel sorbent chemical and Physical system from an algae, chitosan and chitosan nanoparticle and impregnated with algae with chitosan nanocomposite for the sorption of Malachite green dye from water. The algae with chitosan nanocomposite by a simple method and used as a recyclable and effective adsorbent for the removal of malachite green dye from aqueous solutions. Algae, chitosan, chitosan nanoparticle and algae with chitosan nanocomposite were characterized using different physicochemical methods. The functional groups and chemical compounds found in algae, chitosan, chitosan algae, chitosan nanoparticle, and chitosan nanoparticle with algae were identified using FTIR, SEM, and TGADTA/DTG techniques. The optimal adsorption conditions, different dosages, pH and Temperature the amount of algae with chitosan nanocomposite were determined. At optimized conditions and the batch equilibrium studies more than 99% of the dye was removed. The adsorption process data matched well kinetics showed that the reaction order for dye varied with pseudo-first order and pseudo-second order. Furthermore, the maximum adsorption capacity of the algae with chitosan nanocomposite toward malachite green dye reached as high as 15.5mg/g, respectively. Finally, multiple times reusing of algae with chitosan nanocomposite and removing dye from a real wastewater has made it a promising and attractive option for further practical applications.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.tiwarimanvi3129
This presentation is for us to know that how our Environment need Attention for protection of our natural resources which are depleted day by day that's why we need to take time and shift our attention to renewable energy sources instead of non-renewable sources which are better and Eco-friendly for our environment. these renewable energy sources are so helpful for our planet and for every living organism which depends on environment.
Microbial characterisation and identification, and potability of River Kuywa ...Open Access Research Paper
Water contamination is one of the major causes of water borne diseases worldwide. In Kenya, approximately 43% of people lack access to potable water due to human contamination. River Kuywa water is currently experiencing contamination due to human activities. Its water is widely used for domestic, agricultural, industrial and recreational purposes. This study aimed at characterizing bacteria and fungi in river Kuywa water. Water samples were randomly collected from four sites of the river: site A (Matisi), site B (Ngwelo), site C (Nzoia water pump) and site D (Chalicha), during the dry season (January-March 2018) and wet season (April-July 2018) and were transported to Maseno University Microbiology and plant pathology laboratory for analysis. The characterization and identification of bacteria and fungi were carried out using standard microbiological techniques. Nine bacterial genera and three fungi were identified from Kuywa river water. Clostridium spp., Staphylococcus spp., Enterobacter spp., Streptococcus spp., E. coli, Klebsiella spp., Shigella spp., Proteus spp. and Salmonella spp. Fungi were Fusarium oxysporum, Aspergillus flavus complex and Penicillium species. Wet season recorded highest bacterial and fungal counts (6.61-7.66 and 3.83-6.75cfu/ml) respectively. The results indicated that the river Kuywa water is polluted and therefore unsafe for human consumption before treatment. It is therefore recommended that the communities to ensure that they boil water especially for drinking.
Climate Change All over the World .pptxsairaanwer024
Climate change refers to significant and lasting changes in the average weather patterns over periods ranging from decades to millions of years. It encompasses both global warming driven by human emissions of greenhouse gases and the resulting large-scale shifts in weather patterns. While climate change is a natural phenomenon, human activities, particularly since the Industrial Revolution, have accelerated its pace and intensity
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...Joshua Orris
The incorporation of a 3DCSM and completion of HRSC provided a tool for enhanced, data-driven, decisions to support a change in remediation closure strategies. Currently, an approved pilot study has been obtained to shut-down the remediation systems (ISCO, P&T) and conduct a hydraulic study under non-pumping conditions. A separate micro-biological bench scale treatability study was competed that yielded positive results for an emerging innovative technology. As a result, a field pilot study has commenced with results expected in nine-twelve months. With the results of the hydraulic study, field pilot studies and an updated risk assessment leading site monitoring optimization cost lifecycle savings upwards of $15MM towards an alternatively evolved best available technology remediation closure strategy.
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...Joshua Orris
Results of geophysics and pneumatic injection pilot tests during 2003 – 2007 yielded significant positive results for injection delivery design and contaminant mass treatment, resulting in permanent shut-down of an existing groundwater Pump & Treat system.
Accessible source areas were subsequently removed (2011) by soil excavation and treated with the placement of Emulsified Vegetable Oil EVO and zero-valent iron ZVI to accelerate treatment of impacted groundwater in overburden and weathered fractured bedrock. Post pilot test and post remediation groundwater monitoring has included analyses of CVOCs, organic fatty acids, dissolved gases and QuantArray® -Chlor to quantify key microorganisms (e.g., Dehalococcoides, Dehalobacter, etc.) and functional genes (e.g., vinyl chloride reductase, methane monooxygenase, etc.) to assess potential for reductive dechlorination and aerobic cometabolism of CVOCs.
In 2022, the first commercial application of MetaArray™ was performed at the site. MetaArray™ utilizes statistical analysis, such as principal component analysis and multivariate analysis to provide evidence that reductive dechlorination is active or even that it is slowing. This creates actionable data allowing users to save money by making important site management decisions earlier.
The results of the MetaArray™ analysis’ support vector machine (SVM) identified groundwater monitoring wells with a 80% confidence that were characterized as either Limited for Reductive Decholorination or had a High Reductive Reduction Dechlorination potential. The results of MetaArray™ will be used to further optimize the site’s post remediation monitoring program for monitored natural attenuation.
Improving the viability of probiotics by encapsulation methods for developmen...Open Access Research Paper
The popularity of functional foods among scientists and common people has been increasing day by day. Awareness and modernization make the consumer think better regarding food and nutrition. Now a day’s individual knows very well about the relation between food consumption and disease prevalence. Humans have a diversity of microbes in the gut that together form the gut microflora. Probiotics are the health-promoting live microbial cells improve host health through gut and brain connection and fighting against harmful bacteria. Bifidobacterium and Lactobacillus are the two bacterial genera which are considered to be probiotic. These good bacteria are facing challenges of viability. There are so many factors such as sensitivity to heat, pH, acidity, osmotic effect, mechanical shear, chemical components, freezing and storage time as well which affects the viability of probiotics in the dairy food matrix as well as in the gut. Multiple efforts have been done in the past and ongoing in present for these beneficial microbial population stability until their destination in the gut. One of a useful technique known as microencapsulation makes the probiotic effective in the diversified conditions and maintain these microbe’s community to the optimum level for achieving targeted benefits. Dairy products are found to be an ideal vehicle for probiotic incorporation. It has been seen that the encapsulated microbial cells show higher viability than the free cells in different processing and storage conditions as well as against bile salts in the gut. They make the food functional when incorporated, without affecting the product sensory characteristics.
Presented by The Global Peatlands Assessment: Mapping, Policy, and Action at GLF Peatlands 2024 - The Global Peatlands Assessment: Mapping, Policy, and Action
Epcon is One of the World's leading Manufacturing Companies.EpconLP
Epcon is One of the World's leading Manufacturing Companies. With over 4000 installations worldwide, EPCON has been pioneering new techniques since 1977 that have become industry standards now. Founded in 1977, Epcon has grown from a one-man operation to a global leader in developing and manufacturing innovative air pollution control technology and industrial heating equipment.
The Effect of Surface Temperature and Salinity of Ocean Water on Carbon Dioxide Absorption
1. The Effect of Surface
Temperature and Salinity on the
Maximum Acidification of Ocean
Water by Carbon Dioxide
Dissolution
by Vignesh Rajmohan
2. Introduction
The amount of carbon dioxide emitted into Earth’s atmosphere
is increasing substantially every year. This carbon dioxide is
brought into the atmosphere and is also absorbed by oceans.
So far, the ocean has absorbed half of all carbon dioxide
released to the atmosphere since the beginning of the Industrial
Revolution. (Ocean Acidification Nat) When the water absorbs
carbon dioxide, it converts it to form carbonic acid. (Ocean
Acidification.) This reaction increases the acidity of the water.
The increased acidity harms creatures living in the ocean by
deteriorating shells and causing differences in organism size,
metabolic activity and growth rates during blooms. (Stories.)
3. Introduction Cont.
This poses as a threat to the food web, which can cause a
multitude of problems. It is interesting to research this topic because
of its magnitude and global problem-causing potential. When carbon
dioxide is dissolved in water, it reacts with water molecules to produce
carbonic acid. This makes the water acidic. It can be visually
observed using a universal pH indicator.
A pH indicator is a mixture of several special chemical
compounds that is added in small amounts to a solution so that the
pH (acidity or basicity) of the solution can be determined visually.
4. Introduction Cont.
The ocean’s salinity that is generally expressed as Parts Per
Thousand (ppt) varies throughout the ocean. The Atlantic
Ocean’s salinity is the highest between North America and
Africa as well as South American and Africa. Ocean salinity
ranges from 28-38 ppt. Generally, salinity values are lower
close to the north and south poles. The ocean’s temperature
varies depending on the location. The temperature of the
ocean gets higher as one goes closer to the equator. Ocean
temperatures range from 33 – 86 degrees Fahrenheit. (Note:
Colder than 32 degrees F will form ice.)
5. Introduction Cont.
Corals and coralline algae are being deteriorated because of ocean
acidification. Their enamels are fading away and reefs are
deteriorating. Scientists predict that it will not be long before all of the
coral reefs are deteriorated and gone. These creatures are one of the
starting points of the enormous food web in the ocean. Aragonite, the
material that the pteropods use to build their shells, is becoming
weaker and more brittle, because of ocean acidification. (The
Dangers) Several other sea creatures with shells are losing shell
quality and in turn, are starting to die out. The loss of these creatures
will lead to a terrible disaster in the food web. Plankton is also
another key element in the food web. Ocean acidification is going to
have major impacts on plankton physiology and cause differences in
organism size, metabolic activity and growth rates during blooms.
This will lead to problems in the food web.
6. Introduction Cont.
The Effect Of Ocean
Acidification on a Sea
Butterfly (Ocean.)
Any acid can be neutralized through the
usage of a base. This method can be used
to quantify the level of acidity with help of a
pH indicator. Using a basic solution, one can
record the amount needed to neutralize the
acid, which then quantifies the acidity of a
solution. This method is a lot more accurate
than the usual color matching method
because scientists are able to count the
amount of drops needed to neutralize a
solution. This amount of drops can be
recorded to give the scientist numbers that
can be used to make proper calculations.
Usually, a conventional dropper is used to
complete this process.
7. Introduction Cont.
The varying temperatures and salinities of ocean water from around the
world might plays a role in the amount of CO2 that can be absorbed by that
part of the ocean. If patterns could be found to those amounts and the
carbon dioxide dissolution limit, then one could create a diagram of the
world’s oceans and display where the most carbon dioxide could be
absorbed, which also leads to where the most damage will be caused
because of the maximum amount of ocean acidification. This will be of great
use to several people because of this diagram’s importance to finding out
the safety and survival of the creatures of the different parts of the ocean.
8. Testable Question
Does the carbon dioxide absorption potential of salt water
change depending on the salinity and the surface
temperature?
9. Variables
The independent variables are the salinity of the water and the
temperature of the water
The dependent variable is amount of carbon dioxide absorbed
(the amount of baking soda solution needed to neutralize the
acidic water)
The controlled variables are the weights of the materials, the
temperature during the salinity experimentation, the salinity
during temperature experimentation, and the atmospheric air
pressure
10. Hypotheses
If the temperature of ocean water is increased, then the
oceans water’s potential carbon dioxide absorption
amount increases.
If the salinity of ocean water is increased, then the oceans
water’s potential carbon dioxide absorption amount
increases.
11. Materials and Methods
The materials used to complete this experimentation
consist of chemicals and tools. The chemicals used were
de-ionized water [H2O], baking soda [NaHCO2], salt
[NaCl], dry ice (for carbon dioxide [CO2]), and a universal
pH indicator. The tools used were 2 thermometers, a
measuring cup, 19 beakers, flasks, and bottles, an
electronic kitchen-weighing machine (grams), an oven, a
refrigerator, a syringe, a pipet, a
TI-84 Plus Silver Edition Graphing Calculator, a funnel, a
pad, pen and 15 data collecting tables, a pair of safety
glasses, and an iPhone app for color detection (RGB).
12. Materials and Methods cont.
In order to complete this experimentation, one must first prepare 28, 34,
and 38 ppt (parts per thousand) saline water solutions by taking 4.2g,
5.1g, and 5.7g, respectively, of sea salt in 150g of deionized water. Then
he/she must prepare 5 ppt baking soda solution by taking 0.75 g of
baking soda in 150g of deionized water for neutralizing acid solutions.
Then one must take a clear bottle and add 10 g of prepared 28 ppt saline
water. Name this bottle #1. Similarly, prepare another 3 bottles with 10 g
of 28 ppt saline water in each bottle and name these bottles #2, #3, and
“Control”. Then the experimenter should add 2 drops of universal pH
indicator in each bottle. Shake the bottles individually to mix the universal
pH indicator thoroughly. Notice that the color is close to green (pH = 7) at
this stage in each bottle. The solutions should be kept at room
temperature (70 F) for 30 minutes.
13. Materials and Methods cont.
Now one must add 2 g of dry ice in bottle #1, #2 and #3 and shake it well for
a few seconds, then notice the color change as the solution turns from
neutral to an acid. The experimenter must remember not to add dry ice in
the 4th (Control) bottle and use this bottle for referencing color in the
following steps (pH is close to 7). At this stage the pH is close to 2 in bottles
#1, #2 and #3. One must then measure the weight of bottle #1. Add the
baking soda solution little by little and shake the solution at the same time
till the solution changes color to the original pH 7 color (green). The
experimenter should then compare the color of Control bottle for reference.
He or she must then use the RGB iPhone app for an exact color
comparison and note down the weight of the added baking soda solution.
He or she must then repeat the step 8 for bottle #2 and #3 and record the
weights of the baking soda solution in each bottle.
14. Materials and Methods cont.
The experimenter must then repeat the steps 3 to 10 for
the rest of the salinities and temperatures. A total of 36
experiments will be completed by the end of the
experimentation. Also, the reasons for the certain
salinities used are because of the actual salinities of parts
of the ocean. The reasons for the certain temperatures
used are because of the temperatures needed to get a
good spread of the temperatures in the ocean to create a
convenient graph for extrapolation and interpolation.
18. The Effect of Various Temperatures on the Amount of Neutralizer Needed to
Neutralize the Liquid Given (Maximum Acidification of Ocean Water by Carbon
Dioxide Dissolution)
19. The Effect of Various Salinities on the Amount of Neutralizer Needed to
Neutralize the Liquid Given (Maximum Acidification of Ocean Water by Carbon
Dioxide Dissolution)
Experimentally, the weight of neutralizer was determined at temperatures 40 F, 57 F,
70 F & 80 F. Then the data was extrapolated to 33 F and 86 F
20. List of Quadratic equations derived by curve fitting the weight
(in grams) of baking soda solution (5 ppt) used to neutralize
the acidity created by dissolved CO2 in solutions of
various salinity at various temperatures
y = -0.0059x2 + 0.7073x - 14.977
y = -0.0064x2 + 0.7927x - 17.405
y = -0.0073x2 + 0.875x - 17.243
y = 0.0442x2 - 2.6883x + 44.447
y = 0.0408x2 - 2.415x + 41.707
y = 0.0056x2 - 0.0833x + 3.3444
y = 0.005x2 - 0.0933x + 2.3267
y = 0.0492x2 - 3.065x + 49.173
y = -0.005x2 + 0.51x - 8.16
Equations @ constant salinity Equations @ constant temperature
Here:
y = wt. of baking soda solution.
x = Salinity in ppt
Here:
y = wt. of baking soda solution.
x = Temperature in degree F
@ 28 ppt
@ 34 ppt
@ 38 ppt
@ 33 F
@ 40 F
@ 57 F
@ 70 F
@ 80 F
@ 86 F
21. The Effect of Surface Temperature and Salinity on the Amount of Neutralizer
Needed to Neutralize the Liquid Given (Maximum Acidification of Ocean
Water by Carbon Dioxide Dissolution)
Neutralizerweightingram
22. Results cont.
The data table shows that the combination of a salinity of 38 ppt and a
temperature of 57 degrees Fahrenheit has the highest carbon dioxide
absorption potential of all of the tested combinations. The combination
with the lowest carbon dioxide absorption potential is 28 ppt salinity and a
temperature of 80 degrees Fahrenheit. The graphs where salinity was the
independent variable show that as salinity goes up, the amount of baking
soda needed to neutralize the acidic solution goes up as well. The graph
that uses salinity as the independent variable shows that as the
temperature reaches a middle point of around 60 degreed F, the amount
of carbon dioxide the ocean water absorbs goes up. There are two graphs
that aren’t straight from the data that are extrapolated from the data
collected. Interpolation and extrapolation use data and patterns to
calculate the numbers in between data points and outside of data points.
This makes use of math to get rid of the need for more experimentation,
although the more experiments the better. The 3-D graph shows that as
temperature reaches a middle point and as salinity goes up, the potential
carbon dioxide absorption amount goes up as well.
23. Locations, where oceanic water could potentially become more
acidic when the atmospheric concentration of CO2 increases
Very high acidity high acidity Moderate acidity
24. Discussion and Conclusions
The results show that as temperature reaches a middle point and as
salinity goes up, the potential carbon dioxide absorption amount goes
up. Using the information derived from the data collected, one may be
able to fuse it with that of a world map. Using information already
available regarding the salinity and surface temperature of certain
parts of the ocean, one may be able to make a world map that shows
scientists how high acidity levels can get in certain regions of the
ocean. For example, this may help biologists know where to focus
their efforts on protecting the marine life in the water, rather than
wasting their time in an area that might not ever get acidic enough to
kill anything. The experimentation also concludes that neutralizing
using a baking soda solution provides an excellent way for quantifying
the acidity levels of a liquid. The hypothesis was also disproven
because of the results received for temperature affecting the
absorption potential. Rather than the potential carbon dioxide amount
that could be absorbed in ocean water increasing with the rise of the
temperature, the potential amount peaked at around 60 degrees F
and decreased as the temperature decreased or increased from 60
degrees F.
25. Discussion and Conclusions
These experiments takes very long time, it is better to
plan very well to avoid time crunch before the deadline. A few
more temperature points can be tested to increase the
accuracy of the predictions. An error that may have occurred
would probably be the maintenance of the certain temperatures
during testing. After about 2 minutes of being in room
temperature, the temperatures may have changed a small
amount from what they originally were. Using that data, a
contour world map of maximum carbon dioxide dissolution can
be made (in terms amount of baking soda needed to
neutralize).
Similar to this experiment, ocean samples can be taken
from various parts of the world and can be experimented on to
predict the maximum acidity due to CO2 dissolution accurately.
Scientists, using this experimentation, can proactively find out
where there will be problems in aquatic life, and concentrate
efforts for the remediation of the area.
26. Abstract
The varying temperatures and salinities of ocean
water from around the world might plays a role in the amount
of CO2 that can be absorbed by that part of the ocean. If
patterns could be found to those amounts and the carbon
dioxide dissolution limit, then one could create a diagram of
the world’s oceans and display where the most carbon
dioxide could be absorbed, which also leads to where the
most damage will be caused because of the maximum
amount of ocean acidification. To test this question,
solutions with various salinities (28, 34 and 38 ppt) were
prepared. Dry ice was added to the solutions to find the
maximum CO2 dissolution by identifying or measuring the pH
using the pH indicator.
27. Abstract Cont.
Then the acidic solution was neutralized using baking soda and
weighed to quantify the amount of baking soda dissolved. Then those
steps are repeated at these temperatures (40, 57, 70 and 80 F) for
each salinity to understand the dependency of temperature. Then
using the data, plots are made to locate the maximum acidification by
carbon dioxide in the oceans of the world. In general the results
stated that as salinity rises, the amount of carbon dioxide that can be
absorbed by the ocean rises. As temperature reaches a medium
temperature at around 60 degrees Fahrenheit, the ocean water
reaches its highest absorption potential. As temperatures get farther
away from about 60 degrees Fahrenheit, the carbon dioxide
absorption potential decreases.
28. References
Ocean. (n.d.). Retrieved February 26, 2015, from
http://www.nrdc.org/oceans/acidification/
Ocean Acidification. (n.d.). Retrieved February 26, 2015, from
http://ocean.si.edu/ocean-acidification
Ocean Acidification Nat Geo -- National Geographic. (n.d.).
Retrieved February 26, 2015, from
http://ocean.nationalgeographic.com/ocean/critical-issues-ocean-
acidification/
Stories. (n.d.). Retrieved February 26, 2015, from
http://www.pmel.noaa.gov/co2/story/OceanAcidification
The Dangers of Ocean Acidification. (n.d.). Retrieved February 26,
2015, from http://www.scientificamerican.com/article/the-dangers-
of-ocean-acid/