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course of environmental dégradation
course of environmental dégradation
25 literature REVIEW ON solid waste management
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Organic substances can enter the environment by several sources and pathways. One of the pathways is introduced through waste water or rain water flow into surface water. According to Abwasserverband Braunschweig (2014), approximately 700 liters of waste water per second with annual quantity of 22 million m3 waste water, mainly from household activity, are admitted to Steinhof Waste Water Treatment Plant in Braunschweig, Germany. The waste water treatment plant carries out mechanical and biological treatment for this waste water in multiple stages of processes. Then, the treated waste water, together with one from other indirect discharger, is used to infiltration and irrigation purpose which some parts of it might cease in the surface water. Monitoring for 30 years shows the other major indirect discharger for the waste water are garages, petrol stations, institutes or laboratories, waste water treatment plant and print shops (Abwaserverband Brauschweig, 2013).Therefore, a number of organic substances such as cellulose as a part of carbohydrate, protein, surfactants from detergents, which are main constituent of household waste water (Devi, 2005) and also phthalate, tend to introduce to the environment. Phthalate is released particularly from floor and wall coverings or textiles with PVC prints and also from vehicle washing (European Communities, 2001). Later, they may be subjected to transformation and degradation processes depend on the environmental compartment (Kot-wasik, 2004). In case of aquatic compartment, organic compounds are likely to undergo biodegradation or photodegradation as dominant degradation process in water (Dabrowska, 2004). Degradation commonly entails microorganism (biodegradation) in fragmentation or bre...
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...bman, J.F. (2004). Paradigms and paradoxes: the solubility of AgCl in water: some thermochemical issues of aqueous Ag+ ion. Structural Chemistry. 15. 2. 165-168
Helfferich, F.G. (1962). Ion exchange. Carrier Dover Publications. New York. USA. 10-16
Dow. (2010). Vinylbenzyl chloride. http://msdssearch.dow.com/PublishedLiteratureDOWCOM/dh_04d9/0901b803804d9caf.pdf?filepath=specialtymonomers/pdfs/noreg/504-00026.pdf&fromPage=GetDoc. Access : March 10th, 2014
Ezzeldin, H.A., Apblett, A., and Foutch, G.L. (2010). Synthesis and properties of anion exchangers derived from chloromethyl styrene codivinylbenzene and their use in water treatment. International Journal of Polymer Science. 2010. 1-9
Alchin, D (Service chemist, Drew New Zealand) with summary by Heather Wansbrough. (2008). Ion exchange resins. http://nzic.org.nz/ChemProcesses/water/13D.pdf. Access: March 1st, 2014
In comparing micro-leakage of resin-modified glass-ionomers (RMGI), flowable composite liners, and no liners, it was found that by applying a RMGI liner before placing the composite decreased the extent of micro-leakage3. By doing this, the farthest the micro-leakage occurred was to the cervical wall, whereas with composite liners and no liners there was leakage to the cervical wall and into the axial wall3. The reason for the difference could be attributed to the bond between the glass ionomer and composite. This bond is weak and can be thought of as an unbounded wall, leading to less shrinkage stress to the bonds between composite and dentin3.
Table 1 provides the results from this experiment by showing which halides did react with the 1% ethanolic silver nitrate solution and which ones did not react. Through the evaluation of the precipitate, 2-chloro-2-methylpropane reacted instantly with the silver nitrate solution. This reaction occurred instantaneously due to the fact that SN1 reactions favor steric hindrance and the leaving group, chlorine, was a tertiary substrate. On the other hand, the two substrates that had secondary leaving groups were 2-chlorobutane and 2-bromobutane. When 2-bromobutane was mixed with the 1% ethanolic silver nitrate solution, the precipitate that was formed, progressively became cloudier after heating and cooling in a water bath. Although 2-chlorobutane was expected to react, the halide did not show any precipitate before or after heating and cooling. This alkyl halide did not react due to the fact that the leaving group is chlorine, which does not have a strong attraction to the silver nitrate solution. The
Cations are positively charged ions, which are attracted to their negatively charged counterparts, anions. Precipitates can form when these cations and anions combine in aqueous solutions; however, precipitates only form if one of the products of the chemical reaction is not soluble in that solution. Solubility is instrumental in understanding how precipitation reactions occur. This is because solubility rules, determine whether a precipitate can form. A precipitate can form if the cation in the compound is soluble when combined with an anion. For example when the solutions silver nitrate and sodium chloride (reactants) are mixed, silver chloride and sodium nitrate (products) are formed. Following the solubility laws, silver nitrate is the precipitate, as it isn’t
Bibliography "Sodium Bicarbonate" American Heritage Dictionary and Electronic Thesaurus (1985) 21: 347 "Acids and Bases" Science Activities Winter 95, Vol. 31 issue 4, p28. McCarthy, E. Jerome Basic Chemistry Homewood Illinois: Irwin-Dorsey, 1968.
...le of the specific binding to metal molecular cations. 18-crown-6 and 15- crown ethers are used for the recrystallization of AN from non aqueous solvents. The crystals formed by this method showed decrease in hygroscopicity . T. Lee et al. used crown ethers to minimize the polymorphic transition near room temperature. The room temperature phase transition is minimized by forming 1:1 co-crystal of AN-benzo-18-crown-6 with a melting point of 125-129 0C. One disadvantage of this Phase stabilized AN is that it reduces the burn rate of the propellant. Organic compounds, those are having crystallographic structure close to AN crystalline structure are also used as phase stabilizers. N. Galavina et al. have been studied the phase stabilization of AN using the organic compounds containing plane unsaturated N-Heterocycles substituted by carbonyl, amine or imine groups.
Michael P. Broadribb, C. (2006). Institution of Chemical Engineers . Retrieved July 26, 2010, from IChemE: http://cms.icheme.org/mainwebsite/resources/document/lpb192pg003.pdf
The 205-thousand-square-mile Appalachian Mountain range, which spans from Eastern Canada to northern Alabama, boasts North America’s oldest mountains (formed approximately 400 million years ago), the highest peak of the eastern United States (Mount Mitchell), industrial production opportunities and leisurely recreation. The range includes the Blue Ridge Mountains and the Great Smoky mountains (NCSU, n.d.). A range of recreational activities such as fishing in freshwater streams, camping, biking the Blue Ridge Parkway, skiing and hiking are available in the region. One popular hiking location is the 2,184-mile Appalachian Natural Scenic Trail, which is the longest walking trail in the eastern United States (United States. National Park Service, 2014). Its rich natural capital offers a plethora of resources, allowing production to range from small-scale agricultural establishments to larger industrial outputs of metal and timber. Approximately 80 percent of land has been used for the coal and logging industry since the 90’s (Little, 1995). Though the commercial utilization of the mountains has boosted the economy of Appalachian towns and cities, it has also degraded the range aesthetically and commercially.
Arsenic is the 20th most common element in the earth’s crust and can be found naturally in our environment. There is around 0.006 to 0.03 ppm or arsenic distributed in seawater, and 20 ppm of arsenic in soil (before pesticides). Every human will ingest about 0.5 to 1 mg of arsenic in a day from food and water, because arsenic is present in higher quantities in se...
Objective The ability to analyze a substance and determine properties of the substance is an important skill for AP Chemistry students. Major concepts for the “Analysis of Alum” laboratory are percent composition, water of hydration, and molecular formula. They will be used in three different experiments to determine the melting point of alum, the mole ratio of hydrated water to anhydrous alum, and percent of sulfate ion contained in alum. The values acquired in the lab should be close to the calculated values of 92.5 ˚F, 12 moles of water to 1 mole of alum, and 59%, respectively.
Frey, Regina F., and Maureen J. Donlin. "Chemistry 257." Olfaction Tutorial. Washington University, 1998. Web. 4 Dec. 2013.
The bonding nature of both ionic and molecular compounds will show that the materials produced tend to have many different properti...
Contamination of Water and Air. Urbanization enhances the proliferation of industries, automobiles, and agricultural practices. Most toxic air contaminants are produced as we endeavor to fuel our homes, automobiles, factories, energy production facilities, and might also be discovered in indoor cleansing mixtures, and construction supplies. Furthermore pollutants found in gasoline, dry cleaning services, and paint thinners and strippers; som...
Boston: Unwin Hyman, 1988. Works Consulted -. Sazlberg, Hugh W. From Caveman to Chemist: Circumstances and Achievements. Washington, D.C.: American Chemical Society, 1991.
Household water softeners are ion exchange devices. Ion exchange involves removing the hardness ions calcium and magnesium and replacing them with non-hardness ions, typically sodium supplied by dissolved sodium chloride salt, or brine. The softener contains a micro porous exchange resin, usually sulfonated polystyrene beads that are supersaturated with sodium to cover the bead surfaces. As water passes through this resin bed, calcium and magnesium ions attach to the resin beads and the loosely held sodium is released from the resin into the water. The softening process is illustrated in Figure 1.
If using ion exchange resin beads softens the hard water then the water will become purified because it will eliminate the calcium and magnesium ions, which is what causes hard water to be formed. Ion exchange allows efficient elimination of