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SAB 4973: HAZARDOUS WASTE TREATMENT TECHNOLOGIES

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Title: SAB 4973: HAZARDOUS WASTE TREATMENT TECHNOLOGIES


1
SAB 4973HAZARDOUS 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
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Coagulant type
  • Metal coagulants aluminium-based coagulants,
    Fero-based coagulants magnesium chloride (MgCl2)
  • Organic polymer coagulants Polyacrylamide,
    Chitosan, Moringa olifeira Alginates (brown
    seaweed extracts)

9
Coagulant agent
Alum
Magnesium chloride
Polyacrylamide
Moringa oleifera
Chitosan
10
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).

11
Raw waste Floc Formation Settle floc
12
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.

13
Flocculation mechanism
14
Flocculation mechanism
15
Flocculation mechanism
16
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

17
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.

18
CHEMICAL PRECIPITATION
  • Definition
  • Removal of metal ions from solution by changing
    the solution composition, thus causing the metal
    ions to form insoluble metal complexes.

insoluble complexes
clean Water
chemical reaction
solution with soluble ions

19
Natural methods of precipitation include settling
or sedimentation, where a solid forms over a
period of time due to ambient forces like gravity
or centrifugation
20
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

21
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

22
CHEMICAL PRECIPITATION(Theoretical Background)
  • Due to dilute concentration,
  • Ksp A B-
  • solubility product constant
  • where refer to molar concentration
  • Eg.

Compound Solubility (mg/L) Ksp
CaCO3 18 5 x 10-9
CaCl 745000 159 x 106
23
CHEMICAL PRECIPITATION(Basic Principles)
  1. Add chemical precipitants to waste stream
  2. Mix thoroughly
  3. Allow solid precipitates to form floc by slow
    mixing
  4. Allow floc to settle in clarifier

24
CHEMICAL PRECIPITATION(Types of Precipitation)
  • Heavy metals removal
  • Hydroxide precipitation (OH-)
  • Sulphide precipitation (S2-)
  • Carbonate precipitation (CO32-)
  • Phosphorus removal
  • Phosphate precipitation (PO42-)

25
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

26
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 gt 8 for safe sulphide
    precipitation.

27
CHEMICAL PRECIPITATION
28
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.

29
  • 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

30
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, ? is used to indicate a
    change. ?T, 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)

31
  • 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.
  • Time A B
  • (min) mol/L mol/L
  • 0.0 1.000 0.000
  • 3.0 0.400 0.600
  • 6.0 0.250 0.750

32
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
33
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.

34
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.

35
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, fentons reagent, ozone, or potassium
    permanganate are used for treating the effluents,
    especially those obtained from primary treatment
    (sedimentation)

36
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

37
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

38
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

39
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

40
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

41
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42
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.

43
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.

44
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.

45
Symbols
European Union chemical hazard symbol for
oxidizing agents
Dangerous goods label for oxidizing agents
46
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

47
Hydrogen peroxide
  • In acidic solutions H2O2 is one of the most
    powerful oxidizers knownstronger 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.

48
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

49
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

50
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

51
ION EXCHANGE(Type of Resin)
  1. Cationic resin - exchange positive ions
  2. Anionic resin exchange negative ions

(a)
(b)
52
ION EXCHANGE(Exchange Reactions)
  • Cation exchange on the sodium cycle
  • Na2 R Ca2 ? Ca R 2Na
  • where R represents the exchange resin. When all
    exchange sites are substantially replaced with
    calcium, resin is regenerated by passing a
    concentrated solution of sodium ions (5-10)
    through the bed
  • 2Na Ca R ? Na2 R Ca2

53
ION EXCHANGE(Exchange Reactions)
  • Anion exchange replaces anions with hydroxyl
    ions
  • SO42- R (OH)2 ? R SO4 2OH-
  • where R represents the exchange resin. When all
    exchange sites are substantially replaced with
    sulphate, resin is regenerated by passing a
    concentrated solution of hydroxide ions (5-10)
    through the bed
  • R SO4 2OH- ? SO42- R (OH)2

54
ION EXCHANGE(Basic Principles)
H, CN-
H, OH-
Clean water
Cation Resin
Anion Resin
Cr3, CN-
55
ION EXCHANGE(Selectivity)
  • Cations
  • Ra2 gt Ba2 gt Sr2 gt Ca2 gt Ni2 gt Cu2 gt Co2 gt
    Zn2 gt Mn2 gt Ag gtCs gt K gt NH4 gt Na gt Li
  • Anions
  • HCRO4- gt CrO42- gt ClO4- gt SeO42- gt SO42- gt NO3-
    gt Br- gt HPO4- gt HAsO4- gt SeO32- gt CO32- gt CN- gt
    NO2- gt Cl- gt H2PO4-, H2AsO4-, HCO3- gt OH- gt
    CH3COO- gt F-
  • Note The least preferred has the shortest
    retention time, and appears first in the effluent
    and vice versa for the most preferred.

56
Ion exchange-electrochemistry
  • During redox reactions, electrons pass from one
    substance to another. Electrochemistry is the
    branch of chemistry that deals with the
    conversion between chemical and electrical
    energy.
  • The fact that different substances are oxidized
    more readily than others is the driving force
    behind electrochemical cells, and it is this
    force that forces electrons through the external
    circuit from the anode (site of oxidation) to the
    cathode (site of reduction). This force is known
    as the potential difference or electromotive
    force (emf or E). Potential difference is
    measured in volts (V), and thus is also referred
    to as the voltage of the cell. Voltage is a
    measure of the tendency of electrons to flow. The
    higher the voltage, the greater the tendency for
    electrons to flow from the anode to the cathode.

57
  • For example, if copper and hydrogen half-cells
    are joined together we find that the copper
    half-cell will gain electrons from the hydrogen
    half-cell. Thus the copper half-cell is given a
    positive voltage and given a relative value of
    0.34 V
  • Cu2(aq) 2e- ? Cu(s)    E 0.34 V
  • Since both half-reactions cannot undergo
    reduction, we must reverse the equation of the
    reaction that will undergo oxidation. This will
    give us an electrochemical cell voltage of 0.34
    V
  • E
  • Cu2(aq) 2e- ? Cu(s)    0.34
    V
  • H2 (g)  ? 2H(aq) 2e- 0.00 V
  • Cu2(aq) H2 (g) ? 2H(aq) Cu(s)    0.34 V

58
  • We see in the Table of Standard Reduction
    Potentials that zinc has a negative E indicating
    that it is not as good at competing for electrons
    as hydrogen.
  •  Zn2(aq) 2e- ? Zn(s)    E -0.76 V
  • Therefore if zinc and hydrogen are paired
    together in an electrochemical cell, the hydrogen
    would be reduced (gain the electrons) and zinc
    would be oxidized (losing electrons). To
    determine the net redox reaction as well as the
    voltage of the electrochemical cell we reverse
    the zinc equation, and also reverse it's sign
    before adding the equations and E together
  • E
  • Zn(s)  ? Znu2(aq) 2e-   0.76 V
  • 2H(aq) 2e- ? H2 (g)  0.00 V
  • Zn(s) 2H(aq) ? Zn2(aq) H2 (g)    
    0.76 V
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