Monitoring Dissolved Oxygen & BOD
In 2007, the Hawkesbury-Nepean River in New South Wales experienced a cyanobacterial bloom that drove dissolved oxygen below 2 mg/L for 11 consecutive days across a 40 km stretch — NSW DPI fisheries staff recorded over 200,000 dead fish and estimated the BOD5 of decomposing algal biomass at 3× the safe threshold.
Practise this lesson
Four printable worksheets that build from the foundations up to exam-style questions — start at whatever level suits you.
A river sample is taken after a bloom. The water looks green and murky, and dead fish are reported downstream. A scientist says, "The dissolved oxygen reading matters now, but the BOD value may matter even more over the next few days."
- Why might a water sample still become more dangerous after the first dissolved oxygen reading is taken?
- What would a high BOD value suggest about what is happening in that river?
Hold your answer — you will return to revise it after reading.
Know
- How dissolved oxygen can be measured using a DO meter or Winkler titration
- The sequence of reactions in the Winkler method
- The meaning and formula for BOD5
Understand
- Why dissolved oxygen is a key ecological water-quality parameter
- How the Winkler titration links oxygen to thiosulfate titre through redox chemistry
- Why eutrophication increases oxygen stress through decomposition
Can Do
- Calculate dissolved oxygen from Winkler titration data
- Calculate BOD5 and interpret the pollution level
- Connect nutrient loading, BOD rise and fish kill in a logical chain
A direct measure of oxygen available to aquatic life
Dissolved oxygen is one of the most urgent water-quality parameters because aquatic ecosystems can fail quickly when it falls too low.
Dissolved oxygen (DO) is the concentration of oxygen gas dissolved in water. Fish, many invertebrates and aerobic microbes depend on it. If DO falls too low, aquatic organisms experience stress or die.
DO can decrease because of higher temperature, reduced mixing, or increased biological consumption of oxygen. This is why a low DO reading is often a warning sign that the system is under chemical or biological stress.
Dissolved oxygen (DO) is the concentration of O₂ dissolved in water — essential for aerobic aquatic life. DO decreases with higher temperature, reduced mixing, or increased biological consumption. A low DO reading signals chemical or biological stress.
Pause — copy the highlighted DO definition into your book.
Recall
Lesson 6 introduced the inverse relationship between temperature and dissolved oxygen solubility. Lesson 7 extends that idea by showing how chemical and biological oxygen demand make the problem worse.
Fast instrumental reading or redox-based wet chemistry
We just saw that dissolved oxygen is a critical ecological signal. That raises a question: how exactly is it measured in the field or laboratory? This card answers it → a DO meter gives speed, while the Winkler titration gives stoichiometric chemistry.
A DO meter gives speed. The Winkler method gives stoichiometric chemistry. Both aim to answer the same question: how much oxygen is dissolved in the sample right now?
A DO meter is a convenient field instrument that provides a rapid dissolved oxygen reading. The Winkler titration is a classical chemical method that converts the dissolved oxygen in the sample into a titre value through a chain of redox reactions.
The Winkler method is especially useful in teaching because it shows that water-quality monitoring is not only about sensors — it is also about chemical transformations that can be followed quantitatively.
In the Winkler titration, sodium thiosulfate does NOT titrate dissolved oxygen directly — it titrates iodine (I₂), and the amount of iodine is stoichiometrically linked to the original dissolved oxygen. Key ratio: 1 mol O₂ : 4 mol Na₂S₂O₃.
Pause — copy the highlighted Winkler key ratio into your book.
The Winkler method does not titrate dissolved oxygen directly. Oxygen is first trapped chemically, then converted into iodine, and finally linked to a thiosulfate titre through stoichiometry.
From dissolved oxygen to iodine to thiosulfate titre
We just saw that the Winkler method links DO to a thiosulfate titre through two intermediate steps. That raises a question: what are those intermediate reactions, in order? This card answers it → O₂ → MnO₂ → I₂ → thiosulfate titre, with the critical 1:4 stoichiometric shortcut.
The Winkler method works because dissolved oxygen is converted into a measurable amount of iodine, and that iodine is then titrated with sodium thiosulfate.
WINKLER LOGIC
Winkler chain: O₂ oxidises Mn²⁺ to MnO₂ → MnO₂ oxidises I⁻ to I₂ → I₂ is titrated with Na₂S₂O₃. HSC shortcut: 1 mol O₂ : 4 mol Na₂S₂O₃. Thiosulfate titrates iodine, NOT oxygen directly.
Pause — copy the highlighted Winkler chain into your book.
Common error
"The thiosulfate titrates oxygen directly." It does not. Thiosulfate titrates iodine, and the amount of iodine is linked stoichiometrically to the original dissolved oxygen.
Not how much oxygen is present, but how much oxygen is consumed
We just saw how to measure dissolved oxygen right now using Winkler or a DO meter. That raises a question: what if the real problem is not the oxygen right now, but the oxygen that will be consumed over the next five days? This card answers it → BOD₅ measures that future oxygen demand, making it a forecast rather than a snapshot.
Dissolved oxygen gives a snapshot. BOD gives a forecast of oxygen stress caused by biodegradable organic matter.
Biochemical Oxygen Demand, usually measured as BOD5, is the amount of dissolved oxygen consumed by microorganisms as they decompose organic matter over five days at 20°C in the dark.
BOD5 REFERENCE
BOD₅ = initial DO − final DO (after 5 days at 20°C in the dark). <2 mg L⁻¹ = clean; 2–8 = moderate pollution; >8 = heavy pollution. BOD measures oxygen consumed, NOT oxygen present.
Pause — copy the highlighted BOD formula and thresholds into your book.
Misconception
"BOD measures how much oxygen is in the water." Not quite. BOD measures how much oxygen is used up by microbial decomposition. A high BOD means more pollution pressure, not more oxygen availability.
Why nutrient-rich water can end in fish kill
We just saw that high BOD signals a heavy organic load consuming oxygen. That raises a question: where does that organic load come from in a natural river, and how does it turn into a fish kill? This card answers it → eutrophication is the six-step chain from excess nutrients to aquatic death, driven by microbial decomposition raising the BOD.
A green-tinted river on a warm Monday morning looks like a minor aesthetic problem. By Friday, after the algal bloom begins to die and bacteria surge to decompose the biomass, the dissolved oxygen has collapsed below 1 mg/L and fish are surfacing for air. The danger of eutrophication is not the bloom itself but the oxygen crash that follows it.
- Excess nutrients such as nitrates and phosphates enter the water.
- Algal growth increases rapidly, producing a bloom.
- Light penetration falls and submerged plants die.
- Dead algae and plants are decomposed by microorganisms.
- Microbial respiration raises oxygen demand (high BOD).
- Dissolved oxygen falls, causing hypoxia and possible fish kill.
This is why BOD and DO together are so useful: one shows how much oxygen is available, and the other shows how strongly the system is likely to consume it.
Eutrophication sequence: excess nutrients → algal bloom → light loss + plant death → microbial decomposition → high BOD → low DO → hypoxia → fish kill. DO = snapshot of oxygen now; BOD = forecast of future oxygen demand.
Pause — copy the highlighted eutrophication chain into your book.
Hawkesbury anchor
After an algal bloom, a river can seem stable at first glance. But if BOD is high, the system may still be heading toward a sharp drop in dissolved oxygen as microbial decomposition intensifies over the following days.
Data card: Site A: DO initial 8.8, final 7.4 → BOD = 1.4 mg L⁻¹ (clean). Site B: DO initial 7.2, final 3.6 → BOD = 3.6 mg L⁻¹ (moderate). Site C: BOD = 9.1 mg L⁻¹ (heavy pollution).
BOD rises sharply as aerobic bacteria break down organic matter, consuming dissolved oxygen. DO falls, sometimes near zero, creating the 'oxygen sag curve'. Further downstream, as organic matter is depleted, bacterial activity decreases and re-aeration from the atmosphere allows DO to recover toward saturation.
Complete the Learn phase to unlock Practice.
Calculating Dissolved Oxygen from Winkler Data
n(Na2S2O3) = cV = 0.0100 × 0.00800 = 8.00 × 10-5 mol
n(O2) = (8.00 × 10-5) / 4 = 2.00 × 10-5 mol
m(O2) = nM = 2.00 × 10-5 × 32.00 = 6.40 × 10-4 g = 0.640 mg in 100.0 mL
DO = 0.640 × 10 = 6.40 mg L-1
Calculating BOD5
BOD5 = initial DO − final DO = 8.4 − 4.9 = 3.5 mg L-1
A BOD of 3.5 mg L-1 lies in the moderate-pollution range (2–8 mg L-1).
Use the stoichiometric chain carefully and show the link between thiosulfate, oxygen moles and mg L-1 DO.
1. A 100.0 mL sample requires 6.50 mL of 0.0200 mol L-1 Na2S2O3(aq). Calculate the dissolved oxygen concentration.
2. Explain why the thiosulfate titre can be used to determine oxygen even though thiosulfate never reacts directly with dissolved oxygen.
Use BOD values and environmental context together to classify pollution and predict ecosystem impact.
1. A river sample has initial DO 9.0 mg L-1 and final DO 7.6 mg L-1 after 5 days. Calculate BOD5 and classify the water.
2. A second sample has BOD5 = 9.5 mg L-1. What does this suggest about pollution level and likely ecological stress?
3. Explain eutrophication as a sequence of linked events starting from excess nutrients and ending in fish kill.
1. Understand Band 3 What does dissolved oxygen measure?
2. Understand Band 4 In the Winkler method, sodium thiosulfate titrates:
3. Apply Band 4 A water sample has initial DO 8.0 mg L-1 and final DO after 5 days 5.5 mg L-1. What is the BOD5?
4. Analyse Band 5 What does a BOD5 value above 8 mg L-1 indicate?
5. Analyse Band 5 Which sequence best describes eutrophication?
Use both the chemistry and the environmental meaning
Q1. Apply Band 4 (4 marks)
Explain the sequence of reactions in the Winkler titration and how the final thiosulfate titre is linked to dissolved oxygen.
Q2. Analyse Band 5 (4 marks)
Explain the difference between dissolved oxygen and BOD5, and why both are useful when assessing river health after an algal bloom.
Q3. Evaluate Band 5–6 (5 marks)
Evaluate the usefulness of BOD5 as an indicator of pollution in the Hawkesbury River after an algal bloom. In your answer, refer to what BOD5 reveals, one limitation of using it alone, and how it should be interpreted with other data.
Show All Answers
MC Answers: 1-A, 2-D, 3-B, 4-C, 5-A
Activity 1: (1) n(thiosulfate) = 0.0200 × 0.00650 = 1.30 × 10⁻⁴ mol. n(O₂) = 1.30 × 10⁻⁴ / 4 = 3.25 × 10⁻⁵ mol. m(O₂) = 3.25 × 10⁻⁵ × 32.00 = 1.04 × 10⁻³ g = 1.04 mg in 100.0 mL. DO = 10.4 mg L⁻¹. (2) The thiosulfate titrates iodine, and the amount of iodine is stoichiometrically related to the original dissolved oxygen through the Winkler redox chain.
Activity 2: (1) BOD₅ = 9.0 − 7.6 = 1.4 mg L⁻¹ — clean water. (2) BOD₅ 9.5 mg L⁻¹ → heavy pollution, serious oxygen demand and likely ecological stress. (3) Excess nutrients → algal bloom → algae die → microbial decomposition → oxygen demand rises → dissolved oxygen falls → hypoxia → fish kill.
Q1 (4 marks): Dissolved oxygen first oxidises Mn²⁺ to MnO₂. The oxidised manganese then oxidises I⁻ to I₂. That iodine is titrated with sodium thiosulfate. Because the amount of iodine depends on the oxygen originally present, the thiosulfate titre can be converted stoichiometrically to dissolved oxygen. Key HSC ratio: 1 mol O₂ to 4 mol Na₂S₂O₃.
Q2 (4 marks): DO measures how much oxygen is currently dissolved and available for aquatic life. BOD₅ measures how much oxygen microorganisms consume over 5 days while decomposing organic matter. After an algal bloom, DO shows the immediate oxygen status, while BOD₅ indicates how strongly the system will keep consuming oxygen. Together they give both a snapshot and a forecast of oxygen stress.
Q3 (5 marks): BOD₅ is useful because it indicates the biodegradable organic load by measuring oxygen consumed during microbial decomposition. After an algal bloom this is valuable because dead algae can drive strong oxygen demand and threaten aquatic life. A limitation is that BOD₅ alone does not show the current dissolved oxygen level at sampling, so it cannot describe the immediate river condition. It should be interpreted alongside DO and other water-quality data. Overall, BOD₅ is a strong pollution indicator but most useful as part of a broader assessment.
Return to the 2007 Hawkesbury-Nepean cyanobacteria bloom. Now that you understand DO and BOD5, explain the analytical sequence that NSW DPI scientists followed.
- Why did the initial DO reading of 5.5 mg/L give false reassurance — and why did the BOD5 of 9.2 mg/L O₂/L provide the critical warning instead?
- How does microbial decomposition of dead algal biomass actually drive the DO crash that kills fish days after the bloom peaks?
- Write one sentence distinguishing clearly between DO (instantaneous measurement) and BOD5 (predictive measurement) as used by river-monitoring scientists.
What is the formula for BOD₅ and what are its concentration thresholds?
Give the stoichiometric shortcut for the Winkler titration.
What is the difference between dissolved oxygen and BOD₅?
List the 6 steps in the eutrophication sequence.
What does a DO meter measure, and what is one advantage over the Winkler titration?