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![Page 1: Dissolved Oxygen and Biochemical Oxygen Demand Analyses Prepared By Michigan Department of Environmental Quality Operator Training and Certification Unit.](https://reader036.fdocuments.us/reader036/viewer/2022062804/56649d085503460f949d97a1/html5/thumbnails/1.jpg)
Dissolved Oxygen Dissolved Oxygen and Biochemical and Biochemical Oxygen Demand Oxygen Demand
AnalysesAnalyses
Dissolved Oxygen Dissolved Oxygen and Biochemical and Biochemical Oxygen Demand Oxygen Demand
AnalysesAnalyses
Prepared ByMichigan Department of Environmental Quality
Operator Training and Certification Unit
Note: These Procedures are available in the OTCU Laboratory manual which is available on the OTCU website.
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Dissolved OxygenDissolved Oxygen
D.O.Amount of “FREE” Oxygen
O2In the Water
Required By :Required By :FISH
MICROORGANISMS( Bacteria)
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RESPIRATIONRESPIRATIONOrganic Matter Converted to:
Carbon Dioxide and
Water
CH2O + O2 CO2 + H2O
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RESPIRATIONRESPIRATIONCH2O + O2 CO2 + H2O
Reason for Treatment
Basis ofSecondary Treatment
Basis of BOD Analysis
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NitrificationNitrificationBIOLOGICAL Oxidation of Nitrogen
FromAMMONIA
(NH3)
toNITRITE
( NO2)
to NITRATE
(NO3)
NH3 + O2 NO2 + O2 NO3
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NITRIFICATIONNITRIFICATION
NH3 + O2 NO2 + O2 NO3
May be Required:
Oxygen Demand Reduction
Ammonia Removal (toxic)
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Reason for D.O.Reason for D.O.AnalysisAnalysis
Used in BOD Analysis
Treatment Processes
Treatment Plant Effluents
Receiving Stream
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Maximum D.O. Concentrations in Water (Saturation)
Temperature0C
Max. Concentrationmg/L
4 13.18 11.912 10.816 10.020 9.224 8.528 7.930 7.6
0 14.6
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SAMPLE COLLECTIONSAMPLE COLLECTION
21 %Atmosphere
210,000 mg/L
Sample
0 to 10 mg/L
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SAMPLE COLLECTIONSAMPLE COLLECTION
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SAMPLE COLLECTIONSAMPLE COLLECTION
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Do Not Do Not AERATE AERATE SampleSample
Do Not Splash Sample in AirDo Not Splash Sample in Air or or
Let Air Circulate in SampleLet Air Circulate in Sample
NONO YESYES
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D.O. D.O. Procedure
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WINKLER
DISSOLVED OXYGEN
DETERMINATION
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WINKLER Dissolved Oxygen PROCEDUREwith the
ALSTERBERGAZIDE
MODIFICATION
AZIDE Destroys NITRITE
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Winkler MethodIodometric Method
Mn SO4 + 2 KOH Mn(OH)2 + K2SO4
MnO(OH)2 + 2 H2SO4 Mn(SO4)2 + 3 H2O
2 Mn(OH)2 O22 MnO(OH)2+
+Mn(SO4)2 2 KI Mn SO4 + K2SO4 + I2
2. Takes Time
1. Takes Mixing
3. Free IODINE released in relation to D.O. in Sample
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Winkler Procedure
1 mL 1 mL ManganousManganous
SulfateSulfate
1 mL1 mLAlkalineAlkaline
Azide SolutionAzide Solution
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StopperStopperMix WellMix Well
AllowAllowFlocFloc
to Settleto Settle
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Repeat MixingRepeat MixingSettleSettleAgainAgain
Contact and TimeContact and Time
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WhiteWhite - No Dissolved Oxygen- No Dissolved Oxygen
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SulfamicSulfamicAcidAcid
1 mL 1 mL Sulfuric Sulfuric
AcidAcid
MixMix
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IodineIodineSolutionSolution
MeasureMeasure100 mL100 mL
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TitrationSodium ThiosulfateSodium Thiosulfate
(Thio)(Thio)Phenylarsene OxidePhenylarsene Oxide
(PAO)(PAO)OR
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End Point Indicator
StarchStarch
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BlueBlue
ClearClear
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Mg/L D.O. =
mL of Titrant X Normality of Titrant X 8 X 1000
mL of Sample
0.0125 N X 8 X 1000 = 1100
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Mg/L D.O. =
mL of Titrant X 1When 100 ml of Sample is Titrated with 0.0125 Normal Titrant
Each mL used Equals 1 mg/L of D.O.
If4.6 mLis Used
Then the D.O. in the Sample is4.6 mg/L
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1 mL of Titrant = 1 mg/L D.O.
With Any of the Following Combinations ofSample Volumes and Normalities
Sample Volume Normality
100 mL 0.0125 N
200 mL 0.0250 N
300 mL 0.0375 N
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Outline Of Winkler Dissolved Oxygen Procedure
CarefullyCollectSample
In 300 mLBOD Bottle
3.1Add1 mL
MnSO4 Soln.and
1 mLAlkali-iodide-azide
Reagent
3.11Yellow
ToBrownFloc,
D.O. Present
WhiteFloc,
No D.O.
3.12
RepeatMixing
andSettling
3.13
Add1 mLH2SO4
andMix
Mix ByInverting
andAllow To
Settle
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Titration of Iodine Solution
3.21
Pour100 mL
Into Flask
3.22
TitrateWithTHIO
Reddish-Brown
3.23
AddStarch
Indicator
PaleYellow
Blue
3.24
Titrateto
Clear
Clear
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Winkler MethodWinkler MethodIodometric MethodIodometric Method
Mn SOMn SO44 ++ 2 KOH2 KOH Mn(OH)Mn(OH)22 ++ KK22SOSO44
MnO(OH)MnO(OH)22 ++ 2 H2 H22SOSO44 Mn(SOMn(SO44))22 ++ 3 H3 H22OO
2 Mn(OH)2 Mn(OH)22 OO222 MnO(OH)2 MnO(OH)22++
++Mn(SOMn(SO44))22 2 KI2 KI Mn SOMn SO44 ++ KK22SOSO44 ++ II22
2. Takes Time2. Takes Time
1. Takes Mixing1. Takes Mixing
3. Free 3. Free IODINEIODINE released in relation to D.O. in Sample released in relation to D.O. in Sample
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D.O. D.O. Procedure
Electrode Methods
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The membrane electrode is composed of two solid metal electrodes in contact with
supporting electrolyte separated from the test solution by a gas permeable membrane.
Oxygen dissolved in the sample diffuses through the membrane on the DO probe and is chemically reduced (accepts electrons),
producing an electrical current between the anode and cathode in the probe. The amount
of current is proportional to the concentration of DO. Following proper
calibration, the meter relates this current to the concentration of DO.
MEMBRANE ELECTRODE METHODMEMBRANE ELECTRODE METHOD
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CLARK ELECTRODECLARK ELECTRODE
Sample
GasPermeableMembrane
InternalSolution
Cathode
Anode
O2
O2
O2
O2O2
O2 O2
O2
O2
O2
O2
O2
O2
O2 + 4H+ + 4e- 2H2O
e-
Meter
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1. Fill two BOD bottles completely full of BOD dilution water, being very careful not to introduce air into either bottle.
2. Analyze one bottle for D.O. using the Winkler titration.
3. Insert the electrode into the second bottle, turn on the stirring mechanism, and wait for the reading to stabilize.
4. Calibrate the meter to the D.O. value obtained in the titration.
5. The meter is now ready for sample analysis
MEMBRANE ELECTRODE METHODMEMBRANE ELECTRODE METHOD
Comparison with Winkler Titration
Calibration
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This procedure varies considerably among the various instrument models available. Therefore, the procedure must be obtained from the instrument manual, but the following points should be noted.
1. Where possible with the specific equipment being used, compensation should be made during calibration for both ambient temperature and local atmospheric pressure. This pressure should be determined using a reliable onsite barometer. The oxygen solubility table following this procedure may be used.
2. Carefully blot any water droplets from the membrane using a soft tissue.
3. During calibration, be sure the membrane is exposed to fresh air. Laying the electrode on the bench for calibration is usually adequate.
4. Complete the calibration as soon as possible before the electrode membrane begins to dry.
5. The temperature registered on the meter should be checked against a trusted thermometer often.
6. Daily calibration of the D.O. meter is required. Calibration should also be verified after every five or six sample measurements.
7. Assure sufficient sample flow across membrane surface during analysis to overcome erratic response.
MEMBRANE ELECTRODE METHODMEMBRANE ELECTRODE METHOD
“AIR” Calibration
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CLARK ELECTRODECLARK ELECTRODE
Calibration
TemperatureTemperatureAtmospheric PressureAtmospheric Pressure
(Use a Reliable Barometer)(Use a Reliable Barometer)
NONO
NOTNOTREQUIREDREQUIRED
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Luminescence D.O. ProbeLuminescence D.O. Probe
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Luminescence D.O. ProbeLuminescence D.O. Probe
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How Does LDO Work?
• A sensor is coated with a luminescent material.
• Blue light from an LED strikes the luminescent chemical on the sensor.
• The luminescent chemical instantly becomes excited.
• A sensor is coated with a luminescent material.
• Blue light from an LED strikes the luminescent chemical on the sensor.
• The luminescent chemical instantly becomes excited.
LEDPhoto Diode
Probe
Sensor
LED
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• As the excited chemical relaxes, it releases red light.
LEDPhoto Diode
Probe
Sensor
LED• The red light is
detected by a photo diode.
• The time it takes for the chemical to return to a relaxed state is measured
How Does LDO Work?
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• When oxygen contacts the luminescent chemical, the intensity of the red light decreases
• The amount of time it takes for the material to relax is reduced
LEDPhoto Diode
Probe
Sensor
LED
Oxygen
LuminescentIndicator
Molecules Gas PermeablePolymer Matrix
Clear, GasImpermeable
Substrate
How Does LDO Work?
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• The intensity of the red light is not what’s being measured.
• What’s being measured is the time it takes after excitation for red light to be given off. – Lifetime of
luminescence
LEDPhoto Diode
Probe
Sensor
LED
How Does LDO Work?
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• A red LED is also present in the probe.
• Between flashes of the
blue LED, a red LED of known intensity, is flashed on the sensor.
LEDPhoto Diode
Probe
Sensor
LED
• The red LED acts as an internal standard (or reference) for a comparison to the red light given off by the luminescent chemical.
How Does LDO Work?
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Why is this a Big Deal?
No membrane to replaceNo more stretching of Teflon and worrying about air bubbles
No more punctured membranes
No electrolyte to foul or poisonNo H2S poisoning of the electrolyte
No anode or cathodeNo cleaning of anodes
No more coating of electrodes
Reduced Maintenance
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Why is this a Big Deal?
No membrane to replaceNo more stretching of Teflon and worrying about air bubbles
No more punctured membranes
No electrolyte to foul or poisonNo H2S poisoning of the electrolyte
No anode or cathodeNo cleaning of anodes
No more coating of electrodes
Reduced Maintenance
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Why is this a Big Deal?
No membrane to replaceNo more stretching of Teflon and worrying about air bubbles
No more punctured membranes
No electrolyte to foul or poisonNo H2S poisoning of the electrolyte
No anode or cathodeNo cleaning of anodes
No more coating of electrodes
Reduced Maintenance
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• Frequent Calibration Not Required– No anode to consume and no
electrolyte to deplete means extremely stable measurements
– Internal standard with Red LED– No interference from pH swings,
wastewater chemicals, H2S, or heavy metals
Why is this a Big Deal?
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• Accurate and Stable Readings –With nothing to interfere with the
readings, LDO produces more stable measurements for a longer time
• Speed!– Turn it on and it’s running!– Response time of less than 30 seconds
to 90%!
Why is this a Big Deal?
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• Simple Operation and Maintenance– Only one replacement part– Inexpensive sensor cap is simple to
replace quickly
Why is this a Big Deal?
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NOW EPA APPROVEDNOW EPA APPROVED
Listed InFederal Register
Vol. 77,No. 97Friday, May 18, 2012
Listed as ASTM Method D888-09 (C)Footnote 63 – Hach Method 10360
(BOD and cBOD)Footnote 64 In-Situ Method 1002-8-2009
(Dissolved Oxygen Measurement by Optical Probe)
URL - http://www.gpo.gov/fdsys/browse/collection.action?collectionCode=FR&browsePath=2012%2F05%2F05-18%5C%2F6%2FEnvironmental+Protection+Agency&isCollapsed=false&leafLevelBrowse=false&isDocumentResults=true&ycord=546
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D.0. Meter
D.0. Meter
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D.O. METERD.O. METER
AdvantagesAdvantagesSaves TimeSaves Time
Continuous MonitoringContinuous Monitoring
Less Chemical InterferenceLess Chemical Interference
PortablePortable
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D.O. METERD.O. METERLimitationsLimitations
(Membrane Electrode)(Membrane Electrode)
Daily CalibrationDaily Calibration
Flow Past MembraneFlow Past Membrane
Membrane May FoulMembrane May Foul
Requires TrainingRequires Training
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BOD5
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B.O.D.Biochemical Oxygen Demand
The Quantity of Oxygen Used in the Biochemical Oxidation of Organic Material.
Under:Specified TimeSpecified Temperature
Specified Conditions
5 Days200 C
In the DarkIn the Presence
of Bacteria
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Cx H
Y Oz
C xH Y
O z
CxHYOz
C xH Y
O zCx H
Y Oz
NH3
NH3
Bacteria
Measured Volume of Wastewater is Measured Volume of Wastewater is Added to BOD Bottle.Added to BOD Bottle.
Contains:Contains:
OrganicsOrganics
AmmoniaAmmonia
BacteriaBacteria
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Cx H
Y Oz
C xH Y
O z
CxHYOz
C xH Y
O z
Cx H
Y Oz
NH3
NH3
Bacteria
O2
O2
O2
O2
O2
O2
Dilution Water AddedDilution Water Added
Dilution Water Contains:Dilution Water Contains:
NutrientsNutrients
OxygenOxygen
MeasureMeasureD.O. ConcentrationD.O. Concentration
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O2
O2
O2
Incubate 5 DaysIncubate 5 Days
Some Oxygen Used:Some Oxygen Used:
RespirationRespiration
NitrificationNitrificationCx H
Y Oz + O
2 H2 O
+ CO2
NH3 + O
2 NO3
MeasureMeasureD.O. ConcentrationD.O. Concentration
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O2
O2
O2
Cx H
Y Oz + O
2 H2 O
+ CO2
NH3 + O
2 NO3
Measure Oxygen LossMeasure Oxygen Loss(Demand)(Demand)
D.O. Day 1 D.O. Day 1 -- D.O. Day 5 D.O. Day 5
= Oxygen Demand= Oxygen Demand
(Of What Is In The Bottle)
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BOD
REAGENTS Distilled Water
High Quality
Free of Toxic Material
Free of Oxygen Demanding Substances
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BOD
REAGENTS
Phosphate Buffer Magnesium Sulfate Calcium Chloride Ferric Chloride
Distilled Water
Provide Essential NutrientsBuffer pH
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OTHER REAGENTSOTHER REAGENTS
DECHLORINATING AGENTSodium Sulfite - Na2SO3
NITRIFICATION INHIBITORCBOD
QUALITY CONTROL CHECKAccuracy
Glucose - Glutamic Acid Solution
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SAMPLE PRETREATMENTTemperature
Near 200C
pHBetween 6.5 and 7.5
(Adjust if > 8.5 or < 6.0 and seed)
Supersaturated D.O.Agitate
DechlorinateProper Amount of Sodium Sulfite
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DECHLORINATION100 mL of Sample
+ Potassium Iodide + Sulfuric Acid + Starch
Titrate with Sodium Sulfite
to Starch Iodide
Endpoint
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DILUTION WATERDILUTION WATER
Distilled WaterHigh Quality
No ToxicsNo Organics
plus
BUFFER pH 7.2
plus
NUTRIENTS(Phosphorus and Ammonia)MagnesiumCalciumIron
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DILUTION WATER PREPARATION
NEEDED VOLUME for Each Day’s UseADD NUTRIENTS (1 mL per Liter)
SATURATE WITH OXYGEN
VacuumShake(small volume)
orDraw Vacuum
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DILUTION WATER PREPARATION
NEEDED VOLUME
ADD NUTRIENTS
SATURATE WITH OXYGEN
STOREIn Incubator
ADD BUFFERDay of Use
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BOD PROCEDUREBOD PROCEDUREDILUTE SAMPLE
Minimum Residual, 1.0 mg/LMinimum Depletion, 2.0 mg/LAt Least Two DilutionsThoroughly Mix Sample
ADD NITRIFICATION INHIBITORIf Required for CBOD
TCMP0.10 gram/bottle
Two “shots”
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BOD PROCEDUREBOD PROCEDUREDILUTE SAMPLE
Minimum Residual, 1.0 mg/LMinimum Depletion, 2.0 mg/LAt Least Two DilutionsThoroughly Mix Sample
ADD NITRIFICATION INHIBITORIf Required for CBOD
Add SEED (Bacteria)If Required
Disinfected SamplesIndustrial SamplesReference Samples
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BOD PROCEDUREBOD PROCEDURESource of Seed (bacteria)
Settled SewagePrimary Effluent
CommerciallyAvailable
Adapted Seed
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BOD PROCEDURE, (cont.)BOD PROCEDURE, (cont.)
FILL BOTTLE (with dilution water)
MEASURE INITIAL D.O.
STOPPER(No Air Bubbles)
SEAL(Water and Cover)
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BOD PROCEDURE, (cont.)BOD PROCEDURE, (cont.)
INCUBATE
MEASURE FINAL D.O.
(wash bottles)
20 ± 1°C5 Days ± 6 hour
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DILUTION WATER DILUTION WATER BLANKBLANK
CHECK ON QUALITYCHECK ON QUALITY
MAXIMUM DEPLETIONMAXIMUM DEPLETION0.2 mg/L0.2 mg/L
MAXIMUM DEPLETIONMAXIMUM DEPLETION0.2 mg/L0.2 mg/L
NOT USED IN CALCULATIONS
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D.O. In - D.O. Out
= Oxygen Demand of Diluted Sample
C1 X V1 = C2 X V2
SampleBOD X Sample
Volume = BODDiluted X Diluted
Volume
BOD Sample = BOD DilutedSample Volume X Volume
Diluted
BOD Sample =Depletion
X 300 mL
= DEPLETION
B.O.D. Calculation
Sample Volume
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B.O.D. mg/L =B.O.D. mg/L =
D.0. DEPLETION (mg/L)D.0. DEPLETION (mg/L)SAMPLE VOLUME (mL)SAMPLE VOLUME (mL)
X 300 mLX 300 mL
D.O. DEPLETION = D.O. Initial - D.O. 5-Day
Minimum Depletion - 2.0 mg/L
Minimum Residual - 1.0 mg/L
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B.O.D. Example ProblemB.O.D. Example ProblemB.O.D. Example ProblemB.O.D. Example Problem
Calculate the B.O.D.:
B.O.D., mg/L = D.O. Depletion, mg/LVolume Sample, mL
X 300 mL
Initial D.O. - Residual D.O. Volume Sample, mLs
X 300 mL=
= 8.1 mg/L - 2.1 mg/L 60 mL
X 300 mL
= 6.0 mg/L 60 mL
X 300 mL
= 0.1 mg/L X 300 = 30 mg/L
Initial Sample D.O. = 8.1 mg/L5-Day Sample D.O. = 2.1 mg/LVol. Of Sample in 300 mL Bottle = 60 mL
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B.O.D. PRACTICE PROBLEMCalculate the B.O.D. value to be reported for each of the samples below. Be sure to consider the minimum depletion and residual requirements.
Sample 1 Dilution A Dilution B
mL Sample 15 30Initial D.O., mg/L 8.1 8.25-Day D.O., mg/L 6.6 4.2Depletion 1.5 4.0
B.O.D., mg/L = D.O. Depletion, mg/LVolume Sample, mL
X 300 mL
= 4.0 mg/L 30 mL
X 300 mL
= 40 mg/L
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B.O.D. PRACTICE PROBLEMCalculate the B.O.D. value to be reported for each of the samples below. Be sure to consider the minimum depletion and residual requirements.
Sample 2 Dilution A Dilution B
mL Sample 15 30Initial D.O., mg/L 8.0 8.25-Day D.O., mg/L 4.3 0.7Depletion 3.7
B.O.D., mg/L = D.O. Depletion, mg/LVolume Sample, mL
X 300 mL
= 3.7 mg/L 15 mL
X 300 mL
= 74 mg/L
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B.O.D. PRACTICE PROBLEM
Sample 3 Dilution A Dilution B
mL Sample 15 30Initial D.O., mg/L 8.1 8.15-Day D.O., mg/L 5.6 3.3Depletion 2.5 4.8
BODB =4.8 mg/L 30 mL
X 300 mL = 48 mg/L
= 49 mg/L
BODA = 2.5 mg/L 15 mL
X 300 mL = 50 mg/L
50 + 48 2
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BOD PROCEDUREBOD PROCEDURE
DILUTE SAMPLEMinimum Residual, 1.0 mg/LMinimum Depletion, 2.0 mg/LAt Least Two DilutionsThoroughly Mix Sample
ADD NITRIFICATION INHIBITORIf Required for CBOD
Add SEED (Bacteria)If Required
De-chlorinated SamplesIndustrial SamplesReference Samples
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BOD PROCEDUREBOD PROCEDURESource of Seed (bacteria)
Settled SewagePrimary Effluent
CommerciallyAvailable
Adapted Seed
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SEEDED BOD SEEDED BOD PROCEDUREPROCEDURE
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1
2
Sample
Organics
Seed
And
Organics
Bacteria
Depletion3.7 mg/L
Depletion5.0 mg/L
10 mL of seed caused 5.0 mg/L Depletion
1 mL would have caused 5.0 mg/L10 mL = 0.5 mg/L
100 mL
10 mL
1 mL
So: 0.5 mg/L would be used by 1 mL of seedSo: 0.5 mg/L would be used by 1 mL of seedin seeded samplein seeded sample
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BOD(seeded)=D1 - D2
Sample Volume X 300 mL
SEEDED BOD SEEDED BOD CALCULATIONCALCULATION
BOD =Depletion Caused by Sample
Volume of Sample UsedX 300 mL
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BOD(seeded)=D1 - D2
Sample Volume X 300 mL
D1 = Depletion Due To Sample and Seed
D2 = D.O. Depletion Due to Just Seed
SEEDED BOD CALCULATIONSEEDED BOD CALCULATION
(Total Depletion in Bottle with Seed and Sample)
(Seed Depletion in Bottle with Seed and Sample)
??
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BOD(seeded)=D1 - D2
Sample Volume X 300 mL
D2 = D.O. Depletion Due to Just Seed
D2 =D.O. Depletion of a Sample of Seed
Volume of Seed Used
(Seed Depletion in Bottle with Seed and Sample)
D2 Must Be CalculatedD2 Must Be Calculated
Based on Bottle with Just SeedBased on Bottle with Just Seed
In The Bottle with Just Seed
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BOD(seeded)=D1 - D2
Sample Volume X 300 mL
D2 = D.O. Depletion Due to Just Seed
D2 =D.O. Depletion of a Sample of Seed
Volume of Seed Used
(Seed Depletion in Bottle with Seed and Sample)
In the Example
D2 =5.0 mg/L
10mL = 0.5 mg/L
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BOD(seeded) =D1 - D2
Sample Volume X 300 mL
BOD(seeded) =
3.7 mg/L- 0.5 mg/L100 mL
X 300 mL
=3.2 mg/L100 mL X 300 mL
= 9.6 mg/L
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D2 = D.O. Depletion Due to Just Seed
D2 =D.O. Depletion of a Sample of Seed
Volume of Seed Used
(Seed Depletion in Bottle with Seed and Sample)
What If More Than 1mLWas Used for Seeding?
D2 = = 0.5 mg/L5.0 mg/L
10 mL
Multiply by mL Used for Seeding
/mL
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1
2
ReferenceSolution
Organics
Seed
And
Organics
Bacteria
5 mL
5 mL
1 mL
Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample. (300 mL BOD bottles were used)
Example Seeded BOD Calculation.
Seed Material Reference SampleVolume Used 5 mL 5 mLInitial D.O. 8.6 mg/L 8.7 mg/LFinal D.O. 5.8 mg/L 4.8 mg/L
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D1 - D2BODSample Volume, mL
X 300 mL
D1 = Depletion of Sample & Seed
seeded =
D1 = 8.7 mg/L - 4.8 mg/L
D1 = 3.9 mg/L
Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample. (300 mL BOD bottles were used)
Example Seeded BOD Calculation.
Seed Material Reference SampleVolume Used 5 mL 5 mLInitial D.O. 8.6 mg/L 8.7 mg/LFinal D.O. 5.8 mg/L 4.8 mg/L
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D1 - D2BODSample Volume, mL
X 300 mLseeded =
Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample. (300 mL BOD bottles were used)
Example Seeded BOD Calculation.
Seed Material Reference SampleVolume Used 5 mL 5 mLInitial D.O. 8.6 mg/L 8.7 mg/LFinal D.O. 5.8 mg/L 4.8 mg/L
D2 = Depletion of Seed (In Seeded Sample)
D2 =8.6 mg/L – 5.8 mg/L
5 mL
D2 =2.8 mg/L 5 mL
= 0.56
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BOD = 3.34 mg/L5 mL X 300 mL
BOD = 200.4 mg/L
BOD = 3.9 mg/L5 mL
X 300 mL- 0.56 mg/L
Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample. (300 mL BOD bottles were used)
Example Seeded BOD Calculation.
Seed Material Reference SampleVolume Used 5 mL 5 mLInitial D.O. 8.6 mg/L 8.7 mg/LFinal D.O. 5.8 mg/L 4.8 mg/L
D1 - D2BODSample Volume, mL
X 300 mLseeded =
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Calculate the B.O.D. of an de-chlorinated effluent sample given that 1mL of seed material was used in the sample. (300 mL BOD bottles were used)
Example #2 Seeded BOD Calculation.
Seed Material SampleVolume Used 10 mL 200 mLInitial D.O. 8.3 mg/L 8.5 mg/LFinal D.O. 5.6 mg/L 3.7 mg/L
D1 - D2BODSample Volume, mL
X 300 mLseeded =
D1 = Depletion of Sample & Seed
D1 = 8.5 mg/L - 3.7 mg/L
D1 = 4.8 mg/L
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Calculate the B.O.D. of an de-chlorinated effluent sample given that 1mL of seed material was used in the sample. (300 mL BOD bottles were used)
Example #2 Seeded BOD Calculation.
Seed Material SampleVolume Used 10 mL 200 mLInitial D.O. 8.3 mg/L 8.5 mg/LFinal D.O. 5.6 mg/L 3.7 mg/L
D1 - D2BODSample Volume, mL
X 300 mLseeded =
D2 = Depletion of Seed (In Seeded Sample)
D2 =8.3 mg/L – 5.6 mg/L
10 mL
D2 =2.7 mg/L 10 mL
= 0.27
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Calculate the B.O.D. of an de-chlorinated effluent sample given that 1mL of seed material was used in the sample. (300 mL BOD bottles were used)
Example #2 Seeded BOD Calculation.
Seed Material SampleVolume Used 10 mL 200 mLInitial D.O. 8.3 mg/L 8.5 mg/LFinal D.O. 5.6 mg/L 3.7 mg/L
D1 - D2BODSample Volume, mL
X 300 mLseeded =
BOD = 4.53 mg/L200 mL X 300 mL
BOD = 6.8 mg/L
BOD = 4.8 mg/L200 mL
X 300 mL- 0.27 mg/L
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Work Calculations on Separate PaperAnswers Given on Next Slides
BOD Practice Problems
1. Calculate the B.O.D. given:D.O. IN = 7.0 mg/LD.O. OUT (5-day) = 3.5 mg/L
Vol. Sample in B.O.D. bottle = 15 mL
2. Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample.
(300 mL BOD bottles were used)
Seed Material Reference SampleVolume Used 9 mL 5 mL
Initial D.O. 8.7 mg/L 8.6 mg/LFinal D.O. 5.1 mg/L 5.0 mg/L
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1. Calculate the B.O.D. given:D.O. IN = 7.0 mg/LD.O. OUT (5-day) = 3.5 mg/L
Vol. Sample in B.O.D. bottle = 15 mL
BOD =Depletion, mg/L
Sample Volume, mLX 300 mL
BOD = 3.5 mg/L15mL X 300 mL
BOD = 70 mg/L
BOD =7.0 mg/L - 3.5 mg/L
15 mL X 300 mL
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2. Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample.
(300 mL BOD bottles were used)
D1 - D2BOD Sample Volume, mL X 300 mL
D1 = Depletion of Sample & Seed
D2 = Depletion of Seed (In Seeded Sample)
seeded =
Seed Material Reference SampleVolume Used 9 mL 5 mL
Initial D.O. 8.7 mg/L 8.6 mg/LFinal D.O. 5.1 mg/L 5.0 mg/L
D1 = 8.6 mg/L - 5.0 mg/L
D1 = 3.6 mg/L
D2 =8.7 mg/L – 5.1 mg/L
9 mL
D2 =3.6 mg/L
9 mL= 0.40
![Page 104: Dissolved Oxygen and Biochemical Oxygen Demand Analyses Prepared By Michigan Department of Environmental Quality Operator Training and Certification Unit.](https://reader036.fdocuments.us/reader036/viewer/2022062804/56649d085503460f949d97a1/html5/thumbnails/104.jpg)
D1 - D2BODSample Volume, mLX 300 mL
BOD =3.2 mg/L
5 mLX 300 mL
BOD = 192 mg/L
BOD =3.6 mg/L - 0.40 mg/L
5 mL X 300 mL
D1 = Depletion of Sample & SeedD2 = Depletion of Seed
seeded =
2. Calculate the B.O.D. of a reference sample given that 1mL of seed material was used in the reference sample.
(300 mL BOD bottles were used)
Seed Material Reference SampleVolume Used 9 mL 5 mL
Initial D.O. 8.7 mg/L 8.6 mg/LFinal D.O. 5.1 mg/L 5.0 mg/L
![Page 105: Dissolved Oxygen and Biochemical Oxygen Demand Analyses Prepared By Michigan Department of Environmental Quality Operator Training and Certification Unit.](https://reader036.fdocuments.us/reader036/viewer/2022062804/56649d085503460f949d97a1/html5/thumbnails/105.jpg)
Dissolved Oxygen Dissolved Oxygen and Biochemical and Biochemical Oxygen Demand Oxygen Demand
AnalysesAnalyses
Dissolved Oxygen Dissolved Oxygen and Biochemical and Biochemical Oxygen Demand Oxygen Demand
AnalysesAnalyses
Prepared ByMichigan Department of Environmental Quality
Operator Training and Certification Unit