Dissolved
Oxygen (DO)
Reference:
Standard
Methods; 4500-O A, 4500-O B, 4500-O C, 4500-O G
Scope
and Application
The concentration
of Dissolved Oxygen (DO) in natural water and wastewater is a function of the
temperature of the air and water, the degree of hardness of the water, and the
demand for oxygen in the body of water. The solubility of oxygen increases with
decreasing water temperature (oxygen solubility in water is inversely proportional
to temperature). DO is an important parameter in wastewater treatment processes,
most notably when dealing with an activated sludge system.
There are
two methods for measuring DO: an electrometric method using a Dissolved Oxygen
meter and an iodometric method commonly known as the Winkler titration. The
most common method used employs the Dissolved Oxygen meter which compensates
for pressure and temperature variations in water, and is the preferred method
for measuring DO in polluted and highly colored waters.
The use
and calibration of a dissolved oxygen electrode will vary from manufacturer
to manufacturer. Refer to the manufacturer’s instruction manual for the specific
procedures to use. The rest of this section on the measurement of dissolved
oxygen will focus on the analysis by titration.
The Winkler
titration (we will discuss the sodium azide modification of this method in this
manual) is useful in a number of DO measurements;
- To determine the initial
or final DO in the Biochemical Oxygen Demand (BOD5) test;
- to calibrate or verify
readings obtained with a DO meter; and
- to make a direct determination
of DO on a water sample.
Apparatus
- 300 mL BOD bottle(s)
with stopper(s)
- 500 mL Erlenmeyer Flask
- Pipette (20 mL)
- Burette
- Magnetic Stirplates
and Stirbars
- Magnetic Stirbar Retriever
Reagents
The first
two solutions can be prepared in house. The laboratory practices committee
recommends that buffer solutions be purchased due to ease of use and being
relatively inexpensive compared to the time, effort, and chemicals used to prepare
them in house. One supplier also provides prepackaged reagents that can be added
directly to the sample to be analyzed.
- Manganous sulfate –
Dissolve 480 g MnSO4•4H2O, 400 g MnSO4•2H2O,
or 364 g MnSO4•H2O in distilled or deionized water.
Filter the solution and dilute to 1 liter.
- Alkali-iodide-azide
– Place 500 g sodium hydroxide (NaOH) in 500 mL distilled water;
in a separate container dissolve 150 g potassium iodide (KI) in 200 mL
distilled water. Allow both solutions to cool. Carefully combine these two
chemicals in a Pyrex® or other heat resistant container. Add the
two slowly, stirring constantly (this can be best accomplished using a magnetic
stirbar and stirplate). Heat will be created. Avoid breathing the fumes or
body contact with the solution. Allow the solution to cool to room temperature.
To this add 10 g sodium azide (NaN3) that has been dissolved
in 40 mL distilled water. The sodium azide is poisonous, handle it carefully.
Dilute to 1 liter. This solution will decompose in time and should be
replaced after three months.
- Sulfuric acid – concentrated
- Starch solution – Dissolve
2 g of soluble starch in 100 mL of hot distilled water. To preserve
the solution, add 0.2 g salicylic acid.
- Sodium thiosulfate (0.025 M)
– Place 6.205 g sodium thiosulfate (Na2S2O3•5H2O)
to distilled water. Add 0.4 g NaOH (solid). Dilute to 1 liter. The
laboratory practices committee recommends that this solution be purchased.
This will alleviate the need to purchase or prepare the potassium bi-iodate
and potassium iodide listed below and remove the requirement to standardize
the sodium thiosulfate.
- Potassium bi-iodate
(0.0021 M) – Dissolve 812.4 mg potassium bi-iodate, KH(IO3)2
in distilled water. Dilute to 1 liter. The potassium bi-iodate should
have been dried in an oven at 103 –105°C and then cooled in a desiccator before
being weighed to prepare the solution.
- Potassium iodide – free
from iodate
Storage
/ Preservation
When used
for the direct determination of DO, the samples measured must be analyzed immediately.
There is no method available for preservation of DO samples. Therefore, all
samples are grab samples. The DO level of the sample can be fixed (by
performing the "Preparation of Sample" step) to allow time to transport
to a laboratory setting for completion of the analysis. The sample should be
kept cool and protected from sunlight until the analysis can be completed.
Procedure
Standardization
of Sodium Thiosulfate
- In a 500 mL wide-mouth
Erlenmeyer flask place 2 g potassium iodide in 100-150 mL distilled
water. Swirl to dissolve.
- Add 2 drops of concentrated
sulfuric acid and 20.0 mL of standard potassium bi-iodate solution.
- Record the initial volume
of sodium thiosulfate in the burette.
- Titrate the potassium
iodide solution with sodium thiosulfate to a straw yellow color.
- Add several drops of
starch, a blue / purple color will develop. Titrate dropwise until the blue
/ purple color disappears (solution will become clear).
- Record the final volume
of sodium thiosulfate in the burette.
- Calculate the volume
of sodium thiosulfate used.
Note: The
amount of sodium thiosulfate used should be equal to the amount of potassium
bi-iodate solution titrated (20 mL). This verifies that the sodium thiosulfate
is 0.025 M (± 0.001).
Preparation
of Sample
- Fill a 300 mL BOD
bottle with the sample to be analyzed.
- With a pipette, add
1 mL of manganous sulfate.
- With a pipette, add
1 mL of alkali-iodide-azide.
- Stopper and invert the
bottle several times to mix.
- Allow the floc in the
solution to settle to about half the volume of the bottle.
- Invert the bottle several
times to mix the floc back into the solution.
- Allow the floc in the
solution to settle to about half the volume of the bottle.
- After settling, add
1 mL concentrated sulfuric acid, stopper and gently invert several times.
Continue until the precipitate has dissolved back into solution.
- If a brown color develops,
there is dissolved oxygen in the sample. If no color develops or it is very
faint, it may be appropriate to obtain another sample at this time to ensure
that there has not been an error in the sample preparation.
Titration
- Pour 200 mL of
the sample to be titrated in a 500 mL wide-mouth flask.
- Record the initial volume
of sodium thiosulfate in the burette.
- Titrate with standardized
sodium thiosulfate solution to a pale yellow endpoint (swirl the flask gently
while titrating or use a magnetic stirrer).
- Add several drops of
starch solution and continue titrating dropwise until the disappearance of
the blue / purple coloration.
- Record the final volume
of sodium thiosulfate in the burette.
- Calculate the volume
of sodium thiosulfate used.
Calculations
When a
200 mL sample is used, 1 mL of sodium thiosulfate solution (0.025 M)
is equivalent to 1 mg/L Dissolved Oxygen in the sample. (If 8.7 mL
of sodium thiosulfate was used, then the DO of the sample is 8.7 mg/L).
Goals
for a New Analyst Performing Dissolved Oxygen Analysis
- Know safety procedures
for dissolved oxygen analyses
- Know how to fill out
raw data sheets
- Understand analysis
procedures used to perform dissolved oxygen analyses
How to
prepare samples for analysis
- Understand equipment
used to perform dissolved oxygen analyses
pH / ISE
meter
Dissolved
oxygen electrode
How to
calculate calibration value
How to
calibrate
General
use and care of the electrode
- Know where to find equipment
/ supplies
BOD bottles
Graduated
cylinders
Burette
Reagents
necessary to perform analyses
Pipettes
and tips
- Know how to calculate
dissolved oxygen results
- Understand quality control
procedures
- Know how to clean and
prepare BOD bottles
Dissolved
Oxygen Analysis; the Tips for Techs version
Electrometric
Analysis
- Prepare raw data sheets
- Calibrate meter and
probe
- Collect sample
- Check dissolved oxygen
of sample
- Record raw data in the
log book
- Calculate results
Analysis
by Titration
- Prepare raw data sheets
- Collect sample
- Fix dissolved oxygen
(preparation of sample)
- Titrate sample
- Record raw data in the
log book
- Calculate results