🧪 COD — Chemical Oxygen Demand

Physicochemistry PN-EN ISO 15705

Determination of chemical oxygen demand using sealed tubes (cuvettes) with potassium dichromate. A key parameter for assessing water and wastewater contamination with organic matter.

Overview

Chemical Oxygen Demand (COD) is one of the most important parameters in water and wastewater analysis. It determines the amount of oxygen (in mg O₂/L) required for the chemical oxidation of organic substances and certain inorganic reducing compounds present in a water sample.

Unlike BOD5 (biological oxygen demand), COD encompasses all oxidizable substances — both biodegradable and resistant to biological decomposition. The BOD5/COD ratio allows assessing wastewater biodegradability (>0.5 = easily biodegradable).

COD is a mandatory parameter in water permits, municipal and industrial wastewater monitoring, and wastewater treatment plant efficiency evaluation. The permissible COD value in treated wastewater discharged to surface waters is 125 mg O₂/L (Regulation of the Polish Ministry of Environment). The ISO 15705 method (small-scale, sealed tubes) is preferred due to lower reagent consumption and improved work safety compared to the classical reflux method.

Method principle

A water sample is oxidized in a sealed tube (cuvette) with a strong oxidizing mixture: potassium dichromate (K₂Cr₂O₇) in concentrated sulfuric acid (H₂SO₄), in the presence of silver sulfate (Ag₂SO₄) as a catalyst for oxidizing difficult-to-decompose compounds and mercury(II) sulfate (HgSO₄) as a chloride masking agent.

Mineralization proceeds at 150°C for 2 hours. During the reaction, Cr⁶⁺ (orange) is reduced to Cr³⁺ (green). The amount of reduced chromium is measured spectrophotometrically at 600±20 nm (for range up to 1000 mg/L O₂) — Cr³⁺ absorbance is proportional to the sample's COD.

COD [mg O₂/L] = spectrophotometer reading after calibration with standard solutions (KHP — potassium phthalate).

Applications

Key parameters

ParameterValue
Measurement range0–1000 mg O₂/L (without dilution)
Detection limit6 mg O₂/L (photometry at 600 nm)
Mineralization temperature150 ± 2°C
Mineralization time120 minutes (2 hours)
Max. chloride concentration1000 mg/L Cl⁻ (without interference)
Precision (CV)5–10% (depends on concentration)

Standard

Standard number
PN-EN ISO 15705:2005
Title (PL)
Jakość wody -- Oznaczanie indeksu chemicznego zapotrzebowania tlenu (SP-ChZT) -- Metoda zminiaturyzowana z zastosowaniem szczelnych probówek
Title (EN)
Water quality — Determination of the chemical oxygen demand index (ST-COD) — Small-scale sealed-tube method

Step-by-step procedure

1. Sample preparation

Mix the wastewater sample thoroughly (suspensions affect the result). For samples with COD >1000 mg/L, dilute with deionized water. Bring sample to room temperature.

⏱ Time: 5 min

2. Adding sample to cuvette

Open the test cuvette (e.g., Hach LCK 514). Pipette precisely the required sample volume (usually 2.0 mL) into the cuvette with reagents. Close tightly with cap.

⏱ Time: 2 min

3. Mixing

Invert the cuvette several times (min. 3×) to mix the sample thoroughly with reagents. WARNING: cuvette heats up strongly (exothermic reaction with H₂SO₄) — hold by the cap!

4. Mineralization in thermoreactor

Place cuvettes in thermoreactor preheated to 150°C. Mineralize for exactly 120 minutes. Do not open reactor during the process.

⏱ Time: 120 min • 🌡 Temperature: 150°C

5. Cooling

After mineralization, turn off reactor. Leave cuvettes in the block for 15–20 minutes for initial cooling. Then remove and place in rack. Invert several times. Cool to room temperature (~30 min).

⏱ Time: 45–60 min

6. Spectrophotometric measurement

Wipe the cuvette with a clean cloth (no streaks, fingerprints). Insert into spectrophotometer. Measure absorbance at 600 nm (Cr³⁺). Read COD result from calibration curve or built-in program.

⏱ Time: 1 min

7. Quality control

With each batch, run: blank sample (deionized water), KHP standard solution (e.g., 500 mg O₂/L). Acceptable deviation: ±10% of certified value.

8. Waste disposal

Used cuvettes contain mercury and chromium — treat as hazardous waste. Collect in labeled containers. Transfer to laboratory waste disposal company. Do not pour into sewage!

Required equipment and apparatus

EquipmentExampleIndicative price
Thermoreactor (heating block)Hach DRB200, WTW CR 4200, Macherey-Nagel Nanocolor Vario C24 000–12 000 PLN
VIS/UV-VIS spectrophotometerHach DR3900, Hach DR6000, WTW photoLab 760015 000–45 000 PLN
Test cuvettes (ready-to-use reagents)Hach LCK 314 (15–150 mg/L), LCK 514 (100–2000 mg/L), LCK 014 (1000–10000 mg/L)250–450 PLN / 25 pcs
Automatic pipettesEppendorf Research Plus 0.5–5 mL, Brand Transferpette S800–2 000 PLN
Cuvette rackDedicated rack for cooling after mineralization100–300 PLN
Deionized waterMillipore Milli-Q system or Hydrolab, conductivity <0.1 mS/msystem 15 000–40 000 PLN

Reagents, media and consumables

ReagentCASDetails
Potassium dichromate K₂Cr₂O₇7778-50-9Oxidizing solution in concentrated H₂SO₄, concentration 0.01667 mol/L. Contained in ready-to-use test cuvettes.
Sulfuric acid H₂SO₄ (concentrated)7664-93-9Reaction medium, concentration >95%. Highly corrosive, exothermic mixing with water.
Silver sulfate Ag₂SO₄10294-26-5Catalyst for oxidation of difficult-to-decompose compounds (aliphatic, aromatic). 5.5 g/kg H₂SO₄.
Mercury(II) sulfate HgSO₄7783-35-9Chloride masking (Cl⁻ complexation). 33.3 g/L mineralizing solution. Mercury waste requires special disposal.
Potassium phthalate (KHP)877-24-7Calibration standard, 1.000 g KHP = 1.176 g O₂ (theoretical COD). For preparing calibration curve.
COD standard solution 1000 mg/LReady certified solution (CRM) for calibration verification and quality control.

Health and safety (OHS)

Training and video materials

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