I. Introduction Environmental pollution is currently one of the most important issues facing humanity. It was increased exponentially in the past few years and reached alarming levels in terms of its effects on living creatures. The presence of toxic metals in the environment specifically in various water resources is of major concern because of their toxicity, non-biodegradable nature and threat to human, animal and plant life. Electroplating, painting, metallurgical, mining, textile, municipal incineration and chemical manufacturing industries all generate toxic metals of various levels.[1] Strict regulations have been made by different countries for safe discharge standards of these effluents. Chromium ions and other toxic metal ions enter …show more content…
Batch mode adsorption studies: a. Effect of pH: pH variation is one of the most important parameters controlling the uptake of toxic metals from wastewater and aqueous solutions. The studies were conducted at room temperature with an initial metal ion concentration of 10ppm, 15ppm, 20ppm and constant adsorbent dose of 10gm/l solution, at an agitation period of 30min. Effect of pH on adsorption was conducted at ranges of 2, 4, 6, 8, and 10 in each solution. The maximum percentage of adsorption was found in range of pH between up 2 to 4, and there after it decreases with further decrease in pH between up 6 to 8. Table 2.1. Effect of pH on percentage removal of chromium. A. For 100mg/l concentration pH Adsorbent Dose(grams) Contact Time(min) Initial Metal Ion Concentration(mg/l) Final Concentration(mg/l) % Removal 2 10 30 100 5.89 94.11 4 10 30 100 7.12 92.88 6 10 30 100 15 85 8 10 30 100 26.25 73.75 10 10 30 100 35.95 64.05 B. For 150mg/l concentration pH Adsorbent Dose(grams) Contact Time(min) Initial Metal Ion Concentration(mg/l) Final Concentration(mg/l) % Removal 2 10 30 150 10.5 93 4 10 30 150 14.1 90.6 6 10 30 150 24.12
Question3: Experiment 3 The unknown acid sample was 1 • Monoprotic Acid Trails Initial NaOH solution (mL) final NaOH solution (mL) The volume of NaOH to titrate the acid (mL) Amount of Unknown Acid sample 1 (g) The moles of the Unknown Acid (mol) Molar mass of the Unknown Acid (g/mol) A 3.38 28.31 24.93 0.150 0.0026 57.69 B 0.18 29.32 29.14 0.175 0.0029
First one is the independent variable which was Magnesium chloride (Mgcl2) that we would be changing. The dependent variable was the speed of the Paramecium and to see how Magnesium chloride will change it. We had two treatment levels they were our control group without Magnesium chloride and experimental group with Magnesium chloride. Our experiment was replicated twenty times. In our control group sample size, we added drop of Paramecium on 217 ml dryl’s solution.
From the best fit equations found in Graph 2, we were able to create a graph for the concentrations of the bleach and diluted dye solutions at each given reaction time. With this graph, we are able to calculate the half-lives for the bleaching reactions. A half-life is the specific time at which the concentration of the solution is exactly half of its starting value. Our starting concentration of the allura red dye was 0.000938 M, so our half-life occurred at 3 minutes and 20 seconds. Our starting concentration of the sunset yellow was 0.0009864 M, so our half-life occurred at 5 minutes and 15 seconds.
For this titration, one drop of EBT indicator, NH4Cl buffer, and the water sample were added to each well in a 1x12 well strip. Once each well was filled, the titration proceeded: one drop of the 2 x 10-4 M EDTA was added to the first well, two drops to the second, three drops to the third, etc. Once one of the wells turned a blue color, that particular well represented the point at which there was excess EDTA and all of the Mg2+ combined with the EDTA to remove the ions from solution and form the chelate. Following the test, the equation MEDTAVEDTA= MCa2+VCa2+ was used to calculate the Ca2+ and Mg2+ concentrations.1 Similar to the previous AA test, the water sample was diluted with a 1:1 ratio along with the Atherton and Virginia samples.
In test tube 2, when pH 4.0 solution was mixed with the reactants this reaction reached completion at 225 seconds. When pH 7.0 solution reacted with the reactants its reaction went to completion at 180 seconds. Finally, when pH 8.0 solution was mixed with the reactants its reaction came to completion at 210 seconds (Figure 1). Test tube 3 was filled with a pH 7.0 solution had the highest initial reaction velocity followed by test tube 4 containing a pH 8.0 solution. Test tube 2 had the pH4.0 solution which was second to last for the IRV calculation, and finally the base line test tube had the lowest IRV (Table
While the barrels rusted, dangerous elements such as radium, thorium
a. At 60 mm Hg, the data values in the table are not consistent with the data in the plots; for example, total mm Hg O2 bound is 30 with oxygen for Bonnie and 2 for Clyde. On the conventional plot, the 60 mm Hg is depicted at 50 with oxygen for Bonnie and about 9 for Clyde. The table says Bonnie should be shown at 6 instead of 19 at this concentration on the seating plot; also, the table says Clyde should be shown at 0 additional amount bound instead of 10 on the seating plot. b.
The unknown solution contained 20+ -0.05 mL of the unknown in a 40 mL beaker. A 10 mL graduated cylinder was used to accurately measure. The pH value of the unknown was recorded, and then the probe was removed again and cleaned. Last, the pH probe was placed into potassium nitrate. The potassium nitrate was contained in a 40 mL beaker, .520
SECS 20 SECS 40 SECS 60 SECS 80 SECS 100 SECS 120 SECS TRIAL 1 0.04 0.107 0.166 0.225 0.266 0.288 0.323 TRIAL 2 0.082 1.205 0.289 0.352 0.399 0.439 0.472 TRIAL 3 0.04 0.104 0.156 0.201 0.232 0.26 0.28 pH: 5 (TRANSMITTANCE
Environment: Air Pollution Annotated Bibliography Holden C. Edmonds COMM 2367: Persuasive Communication TR 8:00-9:20 Kristie Sigler September 5, 2016 Environment: Air Pollution Annotated Bibliography Newspaper or Periodical Hawthorne, M. (2011, April 1). High levels of toxic lead found in air outside Chicago school. The Chicago Tribune. Retrieved from http://www.chicagotribune.com/lifestyles/health/ct- met-pilsen-lead-problems-20110331- story.html
Use these results to determine the product concentration, using Beer-Lambert’s Law: A= ɛCl (where A is the absorbance, ɛ is the molar absorptivity, C is the product concentration and l is the length of solution that the light passes through). Calculate the product concentrations at every minute for 10 minutes for all 7 of the test tubes using Beer-Lambert’s Law. Plot a graph of product concentration vs. time and then use the gradients of the 7 test tubes to determine the velocities of the reaction. After calculating the velocities, plot a Michaelis-Menten graph of velocity vs. substrate concentration.
IV. Data and observations Mass of beaker (g) 174.01 Mass of beaker + NaOH pellets (g) 174.54 Mass of NaOH pellets 0.53 TRIAL 1 TRIAL 2 Mass of potassium acid phtalate (KHP) (g) 0.15 0.15 final buret reading (ml) 30.75
The solution with the pigments was spotted 15 times on both region A and region B and then allowed to dry. When the plate was dry it was placed into the tank for at least 20
LITERATURE REVIEW What is water pollution? As the country is becoming more and more populated, the demands for social services have increased significantly. This has led to an increase of the pollution in many developing towns such as Ga-kgapane. The most disturbing and problematic forms of pollution in Ga-kgapane is the pollution of the natural streams. Water pollution is when there is a build of one or more substances in water to such an extent that it causes problems for animals or plants.
In this essay, the discussion will point to Nile contamination as a controversial issue and highlight some health problems which occur as consequences of using polluted water in Egypt. Likewise, the essay will raise some scientific methods to determine the percentage of heavy metal in water supported by example. Then it will suggest some chemical technical solutions to reduce the percentage of heavy metals in Nile and reuse it again for many purposes.