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Preadjustment of analyte oxidation state

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1 Preadjustment of analyte oxidation state
It is necessary to adjust the oxidation state of the analyte to one that can be titrated with an auxiliary oxidizing or reducing agent. Ex Preadjustment by auxiliary reagent Fe(II), Fe(III) Fe(II) 4 Titration Ce4+ Preoxidation : Peroxydisulfate ( (NH4)2S2O8 ) 2 ) Sodium bismuthate ( NaBiO 3 Hydrogen peroxide (H O Prereduction : Stannous chloride ( SnCl ) 2 Chromous chloride Jones reductor (zinc coated with zinc amalgam) Walden reductor ( solid Ag and 1M HCl) 901013

2 2Zn (s) + Hg2+  Zn2+ + Zn(Hg) (s)
Jones reductor : 2Zn (s) + Hg2+  Zn2+ + Zn(Hg) (s) 901013

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4 Reagents used in redox titration
Reducing agents Ferrous salts : ammonium iron(II) sulfate hexahydrate (Mohr’s salt) FeSO4(NH4)2SO4· 6H2O iron(II) ethylene diamine sulfate (Oesper’s salt) FeC2H4(NH3)2(SO4)2· 4H2O Sodium thiosulfate pentahydrate Na2S2O3·5H2O Arsenic trioxide: arsenious oxide As2O3 Sodium oxalate and oxalic acid dihydarte Na2(COO)2 , (COOH)2·2H2O Titanium trichloride TiCl3 Potassium ferrocyanide K4Fe(CN)6 · 3H2O 901013

5 Sodium thiosulfate, Na2S2O3
Thiosulfate ion is a moderately strong reducing agent that has been widely used to determine oxidizing agents by an indirect procedure that involves iodine as an intermediate. With iodine, thiosulfate ion is oxidized quantitatively to tetrathionate ion according to the half-reaction: 2S2O3 2–  S4O6 2– + 2e Eo = 0.08 Ex. Determination of hypochlorite in bleaches [CaCl(OCl)H2O]: OCl– + 2I– + 2H+  Cl– + I2 + H2O (unmeasured excess KI) I S2O3 2–  2I– + S4O6 2– Indicator: soluble starch (-amylose) 901013

6 Standardization of thiosulfate solution:
Primary standard : potassium iodate (KIO3), K2Cr2O7, KBrO3 Titration reactions: KIO3 + 5KI + 6HCl  3I KCl H2O I Na2S2O3  2NaI + Na2S4O6 KIO  3I  6Na2S2O3·5H2O  6 Equivalent mw g  6 × g g /  1 N × 1000 ml 35.67 g  1 N × 1000 ml a g  x N × V ml x N = ( a g × 1 N × 1000 ml) / (35.67 g × V ml) Stabilizer for sodium thiosulfate solution : Na2CO3 Na2S2O3 + H2O + CO2  Na2CO3 + H2S2O3 H2S2O3  H2SO3 + S 901013

7 Calculations  Equivalent weight = ( formula weight) / ( e– change)
Equivalents = g / eq. wt meq = mg / eq. Wt. Normality (N) = eq / L = meq / ml Reaction eq. wt of reactant Fe2+  Fe3+ + e FW Fe ÷ 1 KMnO4 + 5e  Mn FW KMnO4 ÷ 5 Na2S2O35H2O  ½ S4O6– + e FW Na2S2O35H2O ÷ 1 Cr2O72 – + 6e  2 Cr FW Cr2O72 – ÷ 6 901013

8 Molecular model of thiosulfate ion.
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9 16-2 Finding the end point or
A redox indicator is a compound that changes color when it goes from its oxidized to its reduced state. or For ferroin, with E° = V we expect the color change to occur in the approximate range 1.088 V to V with respect SHE 901013

10 If the difference in the formal potential is > 0.4 V, then a redox
A redox titration is feasible if the difference between analyte and titrant is > 0.2 V. If the difference in the formal potential is > 0.4 V, then a redox indicator usually gives a satisfactory end point. 901013

11 Starch-Iodine Complex
Starch is the indicator of choice for those procedures involving iodine because it forms an intense blue complex with iodine. Starch is not a redox indicator; it responds specifically to the presence of I2, not to a change in redox potential. The active fraction of starch is amylose, a polymer of the sugar α-d-glucose. In the presence of starch, iodine forms I6 chains inside the amylose helix and the color turns dark blue Structure of the repeating unit of the sugar amylose. 901013

12 H3AsO3 + I3– + H2O = H3AsO4 + 3I– + 2H+
Arsenious oxide, As4O6 As4O H2O = 4H3AsO3 H3AsO3 + I3– + H2O = H3AsO4 + 3I– + 2H+ The As4O6 molecule consists of an As4 tetrahedron with a bridging oxygen atom on each edge 901013

13 Reagents used in redox titration
Oxidizing agents Potassium permanganate KMnO4 : Permanganometry Ceric sulfate / Ceric ammonium sulfate Ce(SO4)2·2(NH4)2SO4· 4H2O : Cerimetry Potassium dichromate K2Cr2O7 : Dichrometry Iodine I2 : Iodimetry, Iodometry Potassium iodate KIO3 : Iodatimetry Potassium bromate KBrO3 : Bromatimetry Sodium nitrite NaNO2 : Calcium hypochlorite Ca(ClO)2 : 901013

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15 Permanganate titration  
Oxidation with permanganate : Reduction of permanaganate KMnO4 Powerful oxidant that the most widely used. In strongly acidic solutions (1M H2SO4 or HCl, pH  1) MnO4– + 8H+ + 5e = Mn H2 O Eo = 1.51 V violet color colorless manganous KMnO4 is a self-indicator. In feebly acidic, neutral, or alkaline solutions MnO4– + 4H+ + 3e = MnO2 (s) + 2H2 O Eo = V brown manganese dioxide solid In very strongly alkaline solution (2M NaOH) MnO4– + e = MnO42 – Eo = V green manganate 901013

16 Permanganate titration  
Duration of colour in end point (30 seconds) MnO4– + 3Mn2+ + 2H2O  5MnO2 + 4H K=1*1047 Stability of aqoues solution of MnO4- MnO4– + 2H2O  4MnO2 (s) + 3O2 (g) +4OH- 901013

17 Standardization of KMnO4 solution
Potassium permanganate is not primary standard, because traces of MnO2 are invariably present. Standardization by titration of sodium oxalate (primary standard) : 2KMnO Na2(COO)2 + 8H2SO4 = 2MnSO4 + K2SO4 + 5Na2SO CO2 + 8H2O 2KMnO  Na2(COO)  10 Equivalent mw mw g /  g /  1 Eq. g  g 1N × 1000 ml  g x N × V ml a g x N = ( a g × 1N × 1000 ml) / ( g × V ml) 901013

18 Preparation of 0.1 N potassium permanganate solution
KMnO4 is not pure. Distilled water contains traces of organic reducing substances which react slowly with permanganate to form hydrous managnese dioxide. Manganesse dioxide promotes the autodecomposition of permanganate. 1) Dissolve about 3.2 g of KMnO4 (mw=158.04) in 1000ml of water, heat the solution to boiling, and keep slightly below the boiling point for 1 hr. Alternatively , allow the solution to stand at room temperature for 2 or 3 days. Filter the liquid through a sintered-glass filter crucible to remove solid MnO2. Transfer the filtrate to a clean stoppered bottle freed from grease with cleaning mixture. Protect the solution from evaporation, dust, and reducing vapors, and keep it in the dark or in diffuse light. If in time managanese dioxide settles out, refilter the solution and restandardize it. 901013

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20 Applications of permanganometry H2O2
2KMnO H2O2 + 3H2SO4 = 2MnSO4 + K2SO4 + 5O2 + 8H2O (2) NaNO2 2NaNO2 + H2SO4 = Na2SO HNO2 2KMnO HNO2 + 3H2SO4 = 2MnSO4 + K2SO4 + 5HNO3 + 3H2O (3) FeSO4 2KMnO FeSO4 + 8H2SO4 = 2MnSO4 + K2SO4 + 5Fe2(SO4)3 + 8H2O (4) CaO CaO HCl = CaCl2 + H2O CaCl H2C2O4 = CaC2O HCl (excess oxalic acid) 2KMnO H2C2O4 + 3H2SO4 = 2MnSO4 + K2SO4 + 10CO2 + 8H2O (back tit) (5) Calcium gluconate [CH2OH(CHOH)4COO]2Ca HCl = CaCl + 2CH2OH9CHOH)4COOH (NH4)2C2O CaCl2 = CaC2O NH4Cl CaCl H2SO4 = H2C2O4 + CaSO4 2KMnO H2C2O4 + 3H2SO4 = 2MnSO4 + K2SO4 + 10CO2 + 8H2O 901013

21 Preparation and standardization:
Oxidation with Ce4+ Ce4+ + e = Ce V in 1 N HClO4 yellow colorless V in 1N HNO3 1.47 V in 1N HCl 1.44 V in 1M HSO4 Indicator : ferroin, diphenylamine Preparation and standardization: Ammonium hexanitratocerate, (NH4)2Ce(NO3)6, (primary standard grade) Ce(HSO4)4, (NH4)4Ce(SO4)4·2H2O Standardized with Sodium oxalate. 901013

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23 Applications of cerimetry
(1) Menadione (2-methylnaphthoquinon: vitamin K3) O CH3 HCl, Zn Reduction OH CH3 2 Ce(SO4)2 Iron 2FeSO (NH4)4Ce(SO4)4 = Fe2(SO4)3 + Ce2(SO4)3 + 4 (NH4)2SO4 901013

24 Oxidation with potassium dichromate
Cr2O72– + 14H+ + 6e = 2Cr3+ + 7H2O Eo = 1.36 V K2Cr2O7 is a primary standard. Indicator : diphenylamine sulphonic acid 901013

25 Very large : quantitative : complete reaction
Ex. Redox titration ( hydroquinone vs dichromate standard solution ) Cr2O72– H e  2 Cr H2O Eo= 1.33 HO OH O O + 2H e Eo= 0.700 3 3 HO OH + Cr2O72– + 8H+  3 O O Cr H2O Eo= Eocathode – Eoanode = – = V K = 10 nEo/ = 10 6(0.63) / = redox indicator : diphenylamine colorless to violet Very large : quantitative : complete reaction 901013

26 16-7 Methods Involving IodineIodimetry and iodometry
Iodimetry: a reducing analyte is titrated directly with iodine (to produce I−). iodometry, an oxidizing analyte is added to excess I− to produce iodine, which is then titrated with standard thiosulfate solution. Iodine only dissolves slightly in water. Its solubility is enhanced by interacting with I- A typical 0.05 M solution of I2 for titrations is prepared by dissolving 0.12 mol of KI plus 0.05 mol of I2 in 1 L of water. When we speak of using iodine as a titrant, we almost always mean that we are using a solution of I2 plus excess I−. 901013

27 Preparation and Standardization of Solutions
Acidic solutions of I3- are unstable because the excess I− is slowly oxidized by air: In neutral solutions, oxidation is insignificant in the absence of heat, light, and metal ions. At pH ≳ 11, triiodide disproportionates to hypoiodous acid (HOI), iodate, and iodide. An excellent way to prepare standard I3- is to add a weighed quantity of potassium iodate to a small excess of KI. Then add excess strong acid (giving pH ≈ 1) to produce I2 by quantitative reverse disproportionation: 901013

28 Cu2++4I- 2CUI + I2 901013

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33 KBrO3 BrO3– + 5Br– + 6H+  3Br2 + H2O 2I– + Br2  I2 + 2Br–
Bromatimetry KBrO BrO3– + 5Br– + 6H+  3Br2 + H2O 2I– + Br2  I2 + 2Br– I S2O32–  2I– + 2S4O62– Substitution reactions BrO3– + 5Br– + 6H+  3Br2 + H2O 2I– + Br2  I2 + 2Br– I S2O32–  2I– + S4O62– 901013

34 Al3+ + 3HOC9H6N  Al(OC9H6N)3 (s) + 3H+
pH 4-9 Al HOC9H6N  Al(OC9H6N)3 (s) + 3H+ hot 4M HCl Al(OC9H6N)3 (s)  3HOC9H6N + Al3+ 3HOC9H6N Br2  3HOC9H4NBr2 + 6HBr 1 mol Al3+  3 mol HOC9H6N  6 mol Br2  2 mol KBrO3 901013

35 Addition reactions 901013

36 Determining water with the Karl Fisher Reagent
The Karl Fisher reaction : I SO H2O  2HI + H2SO4 For the determination of small amount of water, Karl Fischer(1935) proposed a reagent prepared as an anhydrous methanolic solution containing iodine, sulfur dioxide and anhydrous pyridine in the mole ratio 1:3:10. The reaction with water involves the following reactions : C5H5N•I2 + C5H5N•SO2 + C5H5N + H2O  2 C5H5N•HI + C5H5N•SO3 C5H5N+•SO3– + CH3OH  C5H5N(H)SO4CH3 Pyridinium sulfite can also consume water. C5H5N+•SO3– + H2O  C5H5NH+SO4H– It is always advisable to use fresh reagent because of the presence of various side reactions involving iodine. The reagent is stored in a desiccant-protected container. The end point can be detected either by visual( at the end point, the color changes from dark brown to yellow) or electrometric, or photometric (absorbance at 700nm) titration methods. The detection of water by the coulometric technique with Karl Fischer reagent is popular. 901013

37 Pyridine free Karl Fisher reagent
In recent years, pyridine, and its objectionable odor, have been replaced in the Karl Fisher reagent by other amines, particularly imidazole. (1) Solvolysis ROH + SO2  RSO3– ROH2+ Buffering B + RSO3– ROH2+  BH+SO3R– ROH Redox B•I BH+SO3R– + B + H2O  BH+SO4R– BH+I– 901013


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