🧪 Aluminium in Water

Physicochemistry PN-EN ISO 12020

Determination of aluminium in water by atomic absorption spectrometry (AAS) — flame or graphite furnace. Control of aluminium coagulant residues in drinking water.

Overview

Aluminium (Al) is the third most abundant element in the Earth's crust, but its presence in drinking water is undesirable. The permissible aluminium concentration in drinking water is 200 µg/L (0.2 mg/L) according to MH Regulation (Journal of Laws 2017, item 2294). The main sources of aluminium in drinking water are aluminium coagulants (aluminium sulfate, polyaluminium chloride) used in the water treatment process — with improper dosing or pH, Al residues can penetrate treated water.

Elevated aluminium concentrations in drinking water raise health controversies — the relationship between aluminium exposure and Alzheimer's disease has been discussed for years. Although epidemiological evidence is inconclusive, the precautionary principle requires minimizing Al in drinking water. Moreover, aluminium deteriorates the organoleptic properties of water (turbidity, color) and can cause problems in installations (deposits).

The PN-EN ISO 12020 standard describes two AAS methods for determining aluminium in water: flame method (FAAS) — with atomization in nitrous oxide-acetylene flame (N₂O-C₂H₂), used for concentrations 5–100 mg/L, and graphite furnace method (GF-AAS) — for concentrations 5–200 µg/L, relevant in drinking water control. Alternatively, spectrophotometric method with chromoazurol S or pyridylazo resorcinol (PAR) is used, as well as ICP-OES.

In practice, drinking water laboratories most commonly use GF-AAS or ICP-OES due to the required low limit of quantification (of the order of 10 µg/L).

Method principle

GF-AAS method: water sample (10–20 µL) is dosed into graphite tube. Temperature program includes: drying (110–130°C), pyrolysis (1200–1500°C — without modifier or with Mg(NO₃)₂), atomization (2400–2600°C — high temperature necessary due to Al thermal resistance), cleaning (2700°C). Free Al atoms absorb HCL radiation at λ = 309.3 nm. FAAS method: sample is aspirated into N₂O-C₂H₂ flame (temp. ~3000°C) — regular air-acetylene flame does not provide sufficient energy for Al atomization.

Applications

Key parameters

ParameterValue
Wavelength309.3 nm
GF-AAS detection limit~1 µg/L
FAAS detection limit~30 µg/L (N₂O-C₂H₂)
GF-AAS linear range5–200 µg/L
FAAS linear range5–100 mg/L
GF-AAS atomization temperature2400–2600°C

Standard

Standard number
PN-EN ISO 12020:2002
Title (PL)
Jakość wody — Oznaczanie glinu — Metody atomowej spektrometrii absorpcyjnej
Title (EN)
Water quality — Determination of aluminium — Atomic absorption spectrometric methods

Step-by-step procedure

1. Preparation of vessels (contamination control)

Aluminium is ubiquitous — PP/PTFE vessels soak in 10% HCl (not HNO₃!) for 24 h, rinse three times with ultrapure water. Work in clean bench recommended.

⏱ Time: 24 h

2. Sample acidification

Add Suprapur HNO₃ to pH <2. For drinking water — analysis within 24 h (Al may precipitate at pH >4).

⏱ Time: 5 min

3. Preparation of standards (GF-AAS)

Prepare series: 0, 10, 20, 50, 100, 200 µg/L Al in 1% Suprapur HNO₃. Prepare standards immediately before measurement.

⏱ Time: 15 min

4. GF-AAS temperature program

Drying: 110°C (30 s), 130°C (20 s). Pyrolysis: 1400°C (20 s, with Mg(NO₃)₂). Atomization: 2500°C (5 s, reading). Cleaning: 2700°C (3 s).

🌡 Temperature: 110–2700°C

5. Dosing modifier

Autosampler doses 5 µL Mg(NO₃)₂ 0.1% + 15 µL sample. Modifier allows raising pyrolysis temp. without Al losses.

⏱ Time: 5 min

6. Calibration

Measure calibration standards. Plot curve (peak area vs concentration). R² ≥0.998. Check sensitivity.

⏱ Time: 20 min

7. Sample measurement

Measure samples in duplicates. Measurement time approx. 3–4 min/sample. Monitor background (Zeeman correction).

⏱ Time: 3–4 min/sample

8. Quality control

Laboratory blank, field blank, control standard (recovery 90–110%), duplicate (RPD <15%). Special attention to contamination!

⏱ Time: 15 min

9. Contamination control

Laboratory blank must be <3 µg/L Al. If higher — search for contamination source (vessels, reagents, air).

10. Calculation and reporting

Al concentration from calibration curve. Result in µg/L with accuracy to 1 µg/L. Consider measurement uncertainty.

Required equipment and apparatus

EquipmentExampleIndicative price
AAS spectrometer with graphite furnaceAgilent 280Z AA, Shimadzu AA-7000, Analytik Jena ZEEnit 700P150 000–400 000 PLN
N₂O-C₂H₂ burner (for FAAS)Slot-burner type for nitrous oxide — included with FAAS instrumentincluded
Al HCL lampAgilent Al HCL, Heraeus — current 10 mA600–1 500 PLN
Graphite tubesPyrolytically coated tubes with L'vov platform50–150 PLN/pc.
Nitrous oxide N₂O (for FAAS)50 L cylinder, purity 2.0, regulator300–600 PLN/cylinder
PP/PTFE vesselsAluminium ubiquitous — avoid contamination; do not use aluminosilicate glass5–30 PLN/pc.

Reagents, media and consumables

ReagentCASDetails
Al standard solution 1000 mg/L7429-90-5Certified CRM in 2% HNO₃ (Merck CertiPUR), traceable to NIST SRM
Nitric acid 65% Suprapur7697-37-2Ultrapure HNO₃ — for acidifying samples and standards (pH <2). Suprapur quality for GF-AAS!
Modifier — Mg(NO₃)₂10377-60-3Magnesium nitrate 0.1% — matrix modifier for GF-AAS, thermally stabilizes Al
Ultrapure waterResistivity ≥18.2 MΩ·cm, Milli-Q system — checked for Al content (<1 µg/L)
Hydrochloric acid 30% Suprapur7647-01-0HCl — for washing vessels; soaking in 10% HCl, 24 h

Health and safety (OHS)

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