☣️ Chromium VI in Water

Physicochemistry PN-EN ISO 18412

Determination of hexavalent chromium Cr(VI) by spectrophotometric method with 1,5-diphenylcarbazide. Critical toxicological determination — Cr(VI) is carcinogenic.

Overview

Hexavalent chromium Cr(VI) is one of the most dangerous water pollutants — it is a strong oxidizer, carcinogenic (group 1 according to IARC), mutagenic and teratogenic. Sources of Cr(VI) in waters are electroplating plants, tanneries, chemical plants, power plants, and natural leaching from chromium-bearing minerals. The permissible concentration of total chromium in drinking water is 50 µg/L (according to EU Directive 2020/2184 and MH Regulation).

The method with 1,5-diphenylcarbazide (DPC) is selective for Cr(VI) — in an acidic environment (pH 1–2), chromate ions react with DPC forming a red-violet Cr(III)-diphenylcarbazone complex, whose absorbance is measured at 540 nm. The reaction is highly sensitive — the detection limit is about 2 µg/L, and the linear range 2–50 µg/L.

The PN-EN ISO 18412 standard is dedicated to lightly contaminated waters (drinking water, groundwater, surface water). For heavily contaminated waters (industrial wastewater), additional dilution or alternative methods (IC, ICP-MS) are used. It is important that the method determines only Cr(VI) — it does not react with Cr(III), which allows chromium speciation.

Samples for Cr(VI) determination require special storage conditions — they must be analyzed as soon as possible (preferably within 24 h), stored at 4°C, and the container must not contain reducing substances that could reduce Cr(VI) to Cr(III).

Method principle

In an acidic environment (pH 1–2, after adding sulfuric acid), chromate ions CrO₄²⁻ react with 1,5-diphenylcarbazide (DPC) forming a red-violet Cr(III)-diphenylcarbazone complex. The reaction proceeds in two stages: first Cr(VI) oxidizes DPC to diphenylcarbazone, simultaneously reducing to Cr(III), then Cr(III) forms a colored chelate with diphenylcarbazone. The absorbance of the complex is measured spectrophotometrically at a wavelength of 540 nm. The color intensity is proportional to the Cr(VI) concentration according to the Beer-Lambert law.

Applications

Key parameters

ParameterValue
Measurement range2–50 µg/L Cr(VI)
Detection limit (LOD)~2 µg/L
Wavelength540 nm
Cuvette optical path10–50 mm
RepeatabilityCV <5% at 20 µg/L
Color reaction time5–10 minutes

Standard

Standard number
PN-EN ISO 18412:2007
Title (PL)
Jakość wody — Oznaczanie chromu(VI) — Metoda fotometryczna dla wód słabo zanieczyszczonych
Title (EN)
Water quality — Determination of chromium(VI) — Photometric method for weakly contaminated water

Step-by-step procedure

1. Preparation of Cr(VI) standard solution

Dissolve 2.829 g K₂Cr₂O₇ (dried at 102°C, 2h) in water and make up to 1 L. Solution 1000 mg/L Cr(VI). Prepare working dilutions from it.

⏱ Time: 20 min

2. Preparation of DPC solution

Dissolve 250 mg 1,5-diphenylcarbazide in 50 mL acetone. Store in dark bottle in refrigerator (4°C). Solution loses validity after color change.

⏱ Time: 10 min

3. Calibration series

Prepare standards: 0, 5, 10, 20, 30, 40, 50 µg/L Cr(VI) in 50 mL volumetric flasks from working solution.

⏱ Time: 15 min

4. Acidification of samples and standards

To each sample (and standard) add 1 mL H₂SO₄ 0.2 mol/L per 50 mL solution. Mix. pH should be 1–2.

⏱ Time: 5 min

5. Addition of DPC reagent

Add 1 mL DPC solution to each sample. Mix and leave for 5 minutes for full development of red-violet color.

⏱ Time: 5 min

6. Absorbance measurement

Measure absorbance at 540 nm in 10 mm cuvette (or 50 mm for low concentrations) against blank (water + reagents).

⏱ Time: 10 min

7. Plotting calibration curve

Plot absorbance vs Cr(VI) concentration. Correlation coefficient R² ≥0.999. Read sample concentrations from curve.

⏱ Time: 5 min

8. Measurement of test samples

Measure absorbance of acidified samples with DPC. Read concentrations from calibration curve. For concentrations >50 µg/L — dilute sample.

⏱ Time: 10 min

9. Quality control

Measure control sample (standard of known concentration), duplicate and blank. Recovery of control sample: 90–110%.

⏱ Time: 10 min

10. Calculation and reporting

Calculate Cr(VI) concentration from calibration curve. Consider any dilution. Report result in µg/L with accuracy to 1 µg/L.

Required equipment and apparatus

EquipmentExampleIndicative price
UV-Vis SpectrophotometerHach DR6000, Shimadzu UV-1900i, JASCO V-77015 000–60 000 PLN
Glass/quartz cuvettesHellma 100-QS 10 mm and 50 mm150–600 PLN/pc.
Automatic pipettesEppendorf Research Plus 0.5–5 mL, 100–1000 µL800–1 800 PLN
Volumetric flasks class ADURAN / Brand 50, 100, 250 mL40–100 PLN/pc.
Water bath (optional)For accelerating color reaction3 000–8 000 PLN

Reagents, media and consumables

ReagentCASDetails
1,5-Diphenylcarbazide (DPC)140-22-70.5% (w/v) solution in acetone; 250 mg in 50 mL acetone. Store in dark glass bottle, valid 1–2 weeks.
Sulfuric acid 0.2 mol/L7664-93-9H₂SO₄ for acidifying sample — ensures pH 1–2 necessary for reaction
Acetone analytical grade67-64-1Solvent for DPC — analytical quality
Potassium dichromate (standard)7778-50-9K₂Cr₂O₇ — for preparing Cr(VI) 1000 mg/L standard solution; dried at 102°C
Distilled water free from chromiumQuality at least grade 2 according to PN-EN ISO 3696, verified for Cr presence

Health and safety (OHS)

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