3. bod& cod

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1 BOD The oxygen content of water samples stored in a full, airtight bottle decrease with time owing to the oxidation of organic matter by microorganisms Excretions of aquatic biota, water-soluble humus compounds and industrial, domestic and agricultural effluents BOD is an empirical determination of the amount of oxygen required to oxidize the organic matter in the sample

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8/10/2019 3. BOD& COD

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BOD

The oxygen content of water samples stored ina full, airtight bottle decrease with time

owing to the oxidation oforganic matter by microorganisms

Excretions of aquatic biota, water-solublehumus compounds and industrial,domestic and agricultural effluents

BOD is an empirical determination of theamount of oxygen required to oxidize theorganic matter in the sample

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UBOD 

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BOD

BOD5 does not represent the total BOD,since the biological oxidation of organic

matter takes a lot longer than 5 days to

go to completion

95-99% of the reaction is complete after

20 days

The BOD test is widely used to

determine the pollution strength of

wastewater and the quality of receiving

surface waters

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BOD - METHODOLOGY

• The water sample is diluted with a suitable

volume of oxygen-saturated water

containing nutrients and incubated in thedark for 5 days at 20oC

• The DO concentration is determined

before and after incubation and BOD5 iscalculated by difference

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MATERIALS FOR BOD ANALYSIS

o  All the reagents required for the DO testby the Winkler method

o BOD incubation bottles: 250 mL capacity

o  Air incubator or water bath at 20  1oCplace in the dark

o Phosphate buffer solution

o Calcium chloride solution

o Magnesium sulfate solution

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MATERIALS FOR BOD ANALYSIS

Ferric chloride solution

Dilution water

HCl 1:1

NaOH 6M

pH meter and electrode

NOTE : DISCARD ANY OF THE

REAGENT SOLUTIONS IF THEY SHOW

SIGNS OF BACTERIAL GROWTH

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SAMPLING & STORAGE FOR

BOD ANALYSISCollect 0.5  – 1 L of sample

The test should be started as soon as

possible after sampling

Otherwise, store at 3-5oC in a refrigerator

for up to 24 h.

Bring the sample to 20oC before starting

the test

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BOD ANALYSIS

Measure the pH of the sample, and adjustto pH 7-8 using HCl or NaOH. If the pH is

between 6.5 & 8 do not adjust. The recommended dilution

§ raw sewage : 30-100 times dilution

§ purified effluent : 3-10 times dilution§ polluted river water : 1-5 times dilution 

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BOD ANALYSIS

Completely fill three 250 mL BOD bottleswith the diluted solution, ensuring that no

air bubbles are trapped

Determine the DO in one bottleimmediately using the Winkler method

Stopper the other two bottles, water-seal,

place in the air incubator and incubate inthe dark for 5 days at 20oC. After 5 days,

determine the DO using the Winkler

method

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BOD ANALYSIS

Fill 3 bottles with dilution water in the same way.Determine DO in one bottle immediately and the

other after incubating for 5 days

This dilution water blank serves as a rough

check on the quality of the dilution water and itshould not exceed 0.2 mg/L

Calculate the BOD = F (Di  – Df )

Di is the initial DO in the diluted sampleDf  is the DO in diluted sample after 5 days of

incubation

F is the dilution factor

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COD (Chemical Oxygen Demand)

 A measure of the oxygen equivalent of theorganic matter in the sample that is

susceptible to oxidation by a strongoxidizing agent.

BOD determines compounds that can bebiologically oxidized, COD measuresthose substances which can be chemicallyoxidized.

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METHODOLOGY-COD

o The sample is refluxed with excess

potassium dichromate in concentrated

sulfuric acid for 2 h.

o This oxidizes most of the organic matter in

the sample

o Silver sulfate is included as a catalyst to

speed up the oxidation process

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METHODOLOGY-COD

o After digestion, the unreacted dichromate

remaining in solution is titrated with ferrous

ammonium sulfate:

Cr 2O72- + 6Fe2+ + 14H+ 2Cr 3+ + 6Fe3+ +

7H2O

The amount of dichromate consumed is

calculated and the oxidisable organicmatter is reported in term of oxygen

equivalent

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COD analysis

COD (mg/L O2) = 8000 x M x (V1  – V2)/Vs

V1  is the volume of ferrous ammoniumsulfate titrant used to titrate the blank (mL)

V2  is the volume of ferrous ammoniumsulfate titrant used to titrate the sample(mL)

Vs is the volume of sample (mL)

M is the exact concentration of ferrousammonium sulfate titrant (M)