⚗️ Bromides and Bromates in Water

Physicochemistry PN-EN ISO 15061

Determination of bromates (BrO₃⁻) and bromides (Br⁻) in drinking water by ion chromatography with conductometric detection. Bromates are a by-product of water ozonation.

Overview

Bromates (BrO₃⁻) are a hazardous by-product of drinking water disinfection with ozone. When water contains natural bromides (Br⁻), ozonation causes their oxidation to bromates — compounds with proven carcinogenic activity (group 2B according to IARC). The EU Directive 98/83/EC and the Polish Ministry of Health Regulation set the maximum permissible concentration of bromates in drinking water at 10 µg/L.

Ion chromatography (IC) is the reference method for bromate determination according to PN-EN ISO 15061. The method allows simultaneous separation and quantitative determination of bromates and bromides in the presence of other inorganic anions (chlorides, sulfates, nitrates). The use of an anion-exchange column and a conductometric detector with suppressor achieves sensitivity in the range of 0.5–5 µg/L.

Bromate determination is required as part of drinking water quality monitoring, especially in treatment plants using ozonation. The method also applies to surface, swimming pool, and bottled waters. In Poland, the obligation to control bromates results from the Ministry of Health Regulation of December 7, 2017.

ISO 15061 covers two techniques: direct conductometric detection (LOD ~3–5 µg/L) and concentration method on ion-exchange cartridges (LOD ~0.5 µg/L). Alternatively, the post-column reaction method (ISO 11206) with UV detection after KI reaction is used, achieving LOD 0.5 µg/L.

Method principle

A water sample is introduced into an ion chromatograph equipped with an anion-exchange column. Anions present in the sample (Br⁻, BrO₃⁻, Cl⁻, NO₃⁻, SO₄²⁻) are separated based on differences in affinity for the ion-exchange resin. Elution is carried out with sodium carbonate/bicarbonate solution or KOH. After separation, the eluent flows through a chemical or electrochemical suppressor, which eliminates background conductivity, and the analyte anions are detected by a conductometric detector. Quantification is performed by comparing peak areas with a calibration curve. For low concentrations, sample concentration on mini-columns in Ba²⁺, Ag⁺, and H⁺ form is used to remove interfering chlorides and sulfates.

Applications

Key parameters

ParameterValue
Measurement range (bromates)0.5–1,000 µg/L
Limit of detection (LOD)0.5 µg/L (with concentration), 3–5 µg/L (direct)
Permissible BrO₃⁻ concentration10 µg/L (drinking water, EU/PL)
Sample volume5–50 mL (depending on concentration)
Precision (CV)3–8% at concentration >5 µg/L
Analysis time15–30 minutes per chromatogram

Standard

Standard number
PN-EN ISO 15061:2003
Title (PL)
Jakość wody — Oznaczanie rozpuszczonych bromianów — Metoda chromatografii jonowej
Title (EN)
Water quality — Determination of dissolved bromate — Method by liquid chromatography of ions

Step-by-step procedure

1. Eluent preparation

Prepare eluent: Na₂CO₃ 4.5 mmol/L + NaHCO₃ 0.8 mmol/L in deionized water (18.2 MΩ). Degas in ultrasonic bath for 15 min.

⏱ Time: 20 min

2. Column conditioning

Flush anion-exchange column with eluent for at least 30 min at 1.0 mL/min flow rate. Check baseline stability.

⏱ Time: 30 min

3. Calibration

Prepare series of bromate standards: 1, 2, 5, 10, 25, 50 µg/L from certified CRM. Inject sequentially, record chromatograms.

⏱ Time: 2–3 h

4. Sample preparation (direct)

Filter sample through 0.22 µm filter. Transfer to autosampler vial. Analyze samples within 24 h of collection.

⏱ Time: 5 min

5. Concentration (optional, low concentrations)

Pass 50 mL sample through OnGuard Ba → Ag → H cartridges to remove SO₄²⁻, Cl⁻ and reduce ionic strength. Collect filtrate.

⏱ Time: 15 min

6. Sample injection

Inject sample (250 µL or 1 mL loop for concentrated samples) onto column. Start chromatogram recording.

⏱ Time: 1 min

7. Separation and detection

Anions separate on column. BrO₃⁻ typically elutes at 8–12 min, Br⁻ at 12–16 min. Conductometric detection after suppression.

⏱ Time: 15–25 min

8. Integration and calculations

Identify peaks based on retention times. Calculate concentration from calibration curve (linear regression, R² > 0.999).

⏱ Time: 5 min

9. Quality control

Analyze control sample every 10 samples, blank (deionized water) every 5 samples. Spike recovery 90–110%.

⏱ Time: 20 min

10. Column flushing

After series, flush column with eluent for 15 min. Store in eluents or deionized water.

⏱ Time: 15 min

Required equipment and apparatus

EquipmentExampleIndicative price
Ion chromatograph with suppressorThermo Dionex Aquion/Integrion, Metrohm 940 Professional IC Vario120,000–280,000 PLN
Anion-exchange columnThermo AS19/AS23, Metrohm Metrosep A Supp 73,000–6,000 PLN
Electrochemical suppressorThermo ASRS 300/AERS 500e, Metrohm MSM8,000–15,000 PLN
AutosamplerThermo AS-DV, Metrohm 858 Professional30,000–60,000 PLN
Concentration cartridges (Ba²⁺, Ag⁺, H⁺)Thermo OnGuard II Ba/Ag/H200–500 PLN/pc
Vials and sample filtersPP vials 0.5 mL, syringe filters 0.22 µm PVDF0.50–3 PLN/pc

Reagents, media and consumables

ReagentCASDetails
Bromate standard solution (BrO₃⁻)15541-45-4Potassium bromate (KBrO₃), 1,000 mg/L solution, certified CRM
Bromide standard solution (Br⁻)7647-15-6Sodium bromide (NaBr), 1,000 mg/L solution, certified CRM
Sodium carbonate (Na₂CO₃)497-19-8Analytical grade, eluent component (4.5 mmol/L)
Sodium bicarbonate (NaHCO₃)144-55-8Analytical grade, eluent component (0.8 mmol/L)
Sulfuric acid (H₂SO₄)7664-93-9Suppressor regenerant solution, 50 mmol/L
Deionized waterResistivity >18.2 MΩ·cm, for eluent and standard preparation

Health and safety (OHS)

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