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SAB 4973: HAZARDOUS WASTE TREATMENT TECHNOLOGIES

SAB 4973: HAZARDOUS WASTE TREATMENT TECHNOLOGIES. Technologies. Chemical methods Coagulation, flocculation , combined with flotation and filtration, precipitation , ion exchange , electroflotation, electrokinetic coagulation. Physical methods

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SAB 4973: HAZARDOUS WASTE TREATMENT TECHNOLOGIES

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  1. SAB 4973:HAZARDOUS WASTE TREATMENT TECHNOLOGIES

  2. Technologies • Chemical methods Coagulation, flocculation, combined with flotation and filtration, precipitation, ion exchange, electroflotation, electrokinetic coagulation. • Physical methods Membrane-filtration processes (nanofiltration, reverse osmosis, electrodialysis, . . .) and adsorption techniques. • Biological treatments Biodegradation methods such as fungal decolorization, microbial degradation, adsorption by (living or dead) microbial biomass and bioremediation systems

  3. Advantages and disadvantages Chemical methods Advantages : • Rapid and efficient process • Removes all pollutants types, produce a high-quality treated effluent • No loss of sorbent on regeneration and effective Disadvantages : • Expensive, and although the pollutants are removed, accumulation of concentrated sludge creates a disposal problem • High energy cost, chemicals required.

  4. Advantages and disadvantages Physical methods Advantages : • The most effective adsorbent, great, capacity, produce a high-quality treated effluent • No sludge production, little or no consumption of chemicals. Disadvantages : • Economically unfeasible, formation of by-products, technical constraints

  5. Advantages and disadvantages Biological treatments Advantages : • Economically attractive, publicly acceptable treatment Disadvantages : • Slow process, necessary to create an optimal favorable environment, maintenance and nutrition requirements

  6. COAGULATION • Definition Destabilisation of colloid particles by the addition of chemicals (coagulant) • Applications Industrial waste containing colloidal and suspended solids (e.g. pulp and paper, textile)

  7. Coagulant type • Metal coagulants :aluminium-based coagulants, Fero-based coagulants magnesium chloride (MgCl2) • Organic polymer coagulants : Polyacrylamide, Chitosan, Moringa olifeira Alginates (brown seaweed extracts)

  8. Coagulant agent Alum Magnesium chloride Polyacrylamide Moringa oleifera Chitosan

  9. Coagulant - Reaction • Some of the coagulants used include: • Aluminium sulphate • Ferric chloride • Ferric sulphate • Lime (not true coagulant) • Polymer as coagulant aid eg cationic, anionic, non-ionic. • PAC – new types Al2(SO4)3.18H20+ 3Ca(HCO3) 2AI(OH)3+ 3CaSO4+ 6C02 + 18H20 AI(OH)3 or Al2O3 ( form as floc is the key element causing destabilisation of charge).

  10. Raw waste Floc Formation Settle floc

  11. Flocculation • is a process of forming aggregate of flocs to form larger settleable particle. The process can be described as follows: • Mutual collision of small floc resulting in bigger size. • Usually slow speed or gentle mixing is used so as not to break the large flocs due to shear. • Polymer or large molecular wt compound is added to enhance floc build up. Most of them are proprietary chemicals.

  12. Flocculation mechanism

  13. Flocculation mechanism

  14. Flocculation mechanism

  15. Flocculation • The benefits of flocculation are: • To improve settling of particles in sedimentaion tank • To increase removal of suspended solids and BOD • To improve performance of settling tanks

  16. Differences • Coagulation: is a chemical technique which is directed towards the destabilisation of the charged colloidal particals. • Flocculation: is the slow mixing technique which promotes the agglomeration of the stabilised particles.

  17. CHEMICAL PRECIPITATION • Definition: Removal of metal ions from solution by changing the solution composition, thus causing the metal ions to form insoluble metal complexes. chemical reaction insoluble complexes “clean Water” solution with soluble ions +

  18. Natural methods of precipitation include settlingor sedimentation, where a solid forms over a period of time due to ambient forces like gravity or centrifugation

  19. CHEMICAL PRECIPITATION(Applications) • Removal of metals from waste stream • e.g. plating and polishing operations, mining, steel manufacturing, electronics manufacturing • include arsenic, barium, chromium, cadmium, lead, mercury, silver • Treatment of “hard” water – removal of Mg2+ and Ca2+ • Phosphorus removal • Making pigments • Removing salts from water in water treatment

  20. CHEMICAL PRECIPITATION(Theoretical Background) • Solubility equilibria A chemical reaction is said to have reached equilibrium when the rate of forward reaction is equal to the rate of the reverse reaction ABs A+ + B- where ABs : solid; A+, B- - ionic species

  21. CHEMICAL PRECIPITATION(Theoretical Background) A+ + B- ABs Due to dilute concentration, Ksp = [A+] [B-] = solubility product constant where [ ] refer to molar concentration Eg.

  22. CHEMICAL PRECIPITATION(Basic Principles) • Add chemical precipitants to waste stream • Mix thoroughly • Allow solid precipitates to form floc by slow mixing • Allow floc to settle in clarifier

  23. CHEMICAL PRECIPITATION(Types of Precipitation) Heavy metals removal • Hydroxide precipitation (OH-) • Sulphide precipitation (S2-) • Carbonate precipitation (CO32-) Phosphorus removal • Phosphate precipitation (PO42-)

  24. CHEMICAL PRECIPITATION(Hydroxide Precipitation) • Add lime (CaO) or sodium hydroxide (NaOH) to waste stream to precipitate heavy metals in the form of metal hydroxides. Cd2+ + Ca(OH)2Cd (OH)2 + Ca2+ • CaO in the form of slurry (Ca(OH)2) while NaOH in the form of solution. • NaOH is easier to handle but is very corrosive. • Will form floc and settle in clarifier

  25. CHEMICAL PRECIPITATION(Sulphide Precipitation) • Use of sulphide in the form of FeS, Na2S or NaHS • Better metal removal as sulphide salt has low solubility limit Cu2+ + FeS CuS  + Fe2+ • Limitation: can produce H2S (g) at low pH 2H+ + FeS  H2S + Fe2+ • At low pH, reaction will proceed to the right. Thus, require pH > 8 for safe sulphide precipitation.

  26. CHEMICAL PRECIPITATION

  27. Reaction rate • Reaction rate is a measure of how fast a reaction occurs, or how something changes during a given time period. • Consider the oxidation of glucose, C6H12O6 : C6H12O6(s) + 6 O2(g) → 6 CO2(g) + 6 H2O(g) • One of the things that happens during this reaction is simply that glucose gets used up as it reacts with oxygen in the air, and carbon dioxide and water start to form.

  28. A common measure of reaction rate is to express how the concentration of a reaction participant changes over time. It could be how the concentration of a reactant decreases, or how the concentration of a product increases. This is the standard method we will be using. • Now that we have something that changes to measure, we must consider the second key aspect of determining rate - time. Rate is a measure of how something changes over time. Change in concentration Change in time

  29. Chemistry Notation • In chemistry, we typically represent concentration by using square brackets around the chemical formula of the substance. For example to indicate the concentration of SO2(g) in the following reaction we would write it as [SO2]. • Also, the delta symbol, Δ is used to indicate a change. ΔT, for example, means "the change in temperature." • Therefore, if we wanted to express the rate of the following reaction: SO2(g) + NO2(g) → SO3(g) + NO(g)

  30. Let's try an example of calculating a reaction rate. Consider the following reaction: A → B • The following data were obtained for how the concentration of these substances changed during the experiment. TimeAB (min)mol/Lmol/L 0.0 1.000 0.000 3.0 0.400 0.600 6.0 0.250 0.750

  31. We could measure the rate of the reaction either by measuring how the concentration of reactant A changes or how the concentration of product B changes. Let's measure A's average rate of change first: Compare this rate to the rate of just the first three minutes of the reaction: If we calculate the average rate based on the production of product B:

  32. Factors that Affect the Chemical Reaction Rate • Concentration of Reactants A higher concentration of reactants leads to more effective collisions per unit time, which leads to an increasing reaction rate (except for zero order reactions). • Temperature Usually, an increase in temperature is accompanied by an increase in the reaction rate. Temperature is a measure of the kinetic energy of a system, so higher temperature implies higher average kinetic energy of molecules and more collisions per unit time.

  33. Factors that Affect the Chemical Reaction Rate • Medium The rate of a chemical reaction depends on the medium in which the reaction occurs. It may make a difference whether a medium is aqueous or organic; polar or nonpolar; or liquid, solid, or gaseous. • Presence of Catalysts and Competitors Catalysts (e.g., enzymes) lower the activation energy of a chemical reaction and increase the rate of a chemical reaction without being consumed in the process. Catalysts work by increasing the frequency of collisions between reactants, altering the orientation of reactants so that more collisions are effective, reducing intramolecular bonding within reactant molecules, or donating electron density to the reactants.

  34. OXIDATION a method by which wastewater is treated by using oxidizing agents. Generally, two forms viz. • Chemical oxidation and • UV assisted oxidation using chlorine, hydrogen peroxide, fenton’s reagent, ozone, or potassium permanganate are used for treating the effluents, especially those obtained from primary treatment (sedimentation)

  35. CHEMICAL OXIDATION(Oxidants) • Rapid and efficient process • High energy cost, chemicals required REDOX Oxidation and reduction in terms of oxygen transfer Definitions Oxidation is gain of oxygen. Reduction is loss of oxygen. • Fe2O3 + 3CO  2Fe + 3CO2

  36. Another definition Oxidation and reduction in terms of hydrogen transfer • These are old definitions which aren't used very much nowadays. The most likely place you will come across them is in organic chemistry. Definitions • Oxidation is loss of hydrogen. • Reduction is gain of hydrogen. CH3CH2OH CH3CHO Oxidation by loses of hydrogen

  37. Another definition Oxidation and reduction in terms of electron transfer • This is easily the most important use of the terms oxidation and reduction at A' level. Definitions • Oxidation is loss of electrons. • Reduction is gain of electrons. OIL RIG  oxidation is loss, reduction is gain CuO + Mg  Cu + MgO Cu2+ + Mg  Cu + Mg2+

  38. OXIDATION STATES (OXIDATION NUMBERS) • Oxidation state shows the total number of electrons which have been removed from an element (a positive oxidation state) or added to an element (a negative oxidation state) to get to its present state. • Oxidation involves an increase in oxidation state • Reduction involves a decrease in oxidation state

  39. Some elements almost always have the same oxidation states in their compounds: • Group 1 metals : always +1 • Group 2 metals : always +2 • Oxygen : usually -2 except in peroxides and F2O • Hydrogen : usually +1 except in metal hydrides where it is -1 • Fluorine : always -1 • Chlorine : usually -1 except in compounds with O or F

  40. Example 1: • This is the reaction between magnesium and hydrochloric acid or hydrogen chloride gas: Mg + 2HCl MgCl2 + H2 0 +1 -1 +2 -1 0 • The magnesium's oxidation state has increased - it has been oxidised. The hydrogen's oxidation state has fallen - it has been reduced. The chlorine is in the same oxidation state on both sides of the equation - it hasn't been oxidised or reduced.

  41. Example 2: • The reaction between sodium hydroxide and hydrochloric acid is: NaOH + HCl  NaCl + H2O +1 -2 +1 +1 -1 +1 -1 +1 -2 • Nothing has changed. This isn't a redox reaction.

  42. Example 3: • The reaction between chlorine and cold dilute sodium hydroxide solution is: 2NaOH + Cl2 NaCl + NaClO + H2O +1 -2 +1 0 +1 -1 +1 +1 -2 +1 -2 • One atom has been reduced because its oxidation state has fallen. The other has been oxidised.

  43. Symbols European Union chemical hazard symbol for oxidizing agents Dangerous goods label for oxidizing agents

  44. Common oxidizing agents • Hydrogen peroxide and other inorganic peroxides • Nitric acid and Nitrates • Chlorites, chlorate, perchlorate, and other analogous halogen compounds • Hypochlorite and other hypohalite compounds such as bleach • Fluorine and other halogens • Ozone • Nitrous oxide(N2O) • Silver oxide • Permanganate salts

  45. Hydrogen peroxide • In acidic solutions H2O2 is one of the most powerful oxidizers known—stronger than chlorine, chlorine dioxide, and potassium permanganate. • Also, through catalysis, H2O2 can be converted into hydroxyl radicals (.OH), which are highly reactive. • H2 + O2 → H2O2 • It is used as a disinfectant, antiseptic, oxidizer, propellant in rocket. Hydrogen peroxide is naturally produced in organisms as a by-product of oxidative metabolism. Nearly all living things (specifically, all obligate and facultative aerobes) possess enzymes known as peroxidase.

  46. Nitric acid • Nitric acid is made by reacting nitrogen dioxide (NO2) with water. • 3 NO2 + H2O → 2 HNO3 + NO • Nitric acid reacts with most metals. 3 Cu + 8 HNO2 → 3 Cu2+ + 2 NO + 4 H2O + 6 NO3- Cu + 4 H+ + 2 NO3-→ Cu2+ + 2 NO2 + 2 H2O

  47. ION EXCHANGE • Definition Ion exchange is basically a reversible chemical process wherein an ion from solution is exchanged for a similarly charged ion attached to an immobile solid particle. Removal of undesirable anions and cations from solution through the use of ion exchange resin • Applications • Water softening • Removal of non-metal inorganic • Removal or recovery of metal

  48. ION EXCHANGE(Medium - resin) • Consists of an organic or inorganic network structure with attached functional group • Synthetic resin made by the polymerisation of organic compounds into a porous three dimensional structure • Exchange capacity is determined by the number of functional groups per unit mass of resin

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