⚛️ Cadmium in Water — GF-AAS

Physicochemistry PN-EN ISO 15586

Determination of trace concentrations of cadmium in water by atomic absorption spectrometry with graphite furnace (GF-AAS). Detection limit of about 0.05 µg/L.

Overview

Cadmium (Cd) is a heavy metal with strong toxic action — it accumulates in the body (half-life in kidneys is 10–30 years), causes kidney damage (cadmium nephropathy), osteoporosis (itai-itai disease), is carcinogenic (group 1 according to IARC). The permissible cadmium concentration in drinking water is 5 µg/L (EU Directive 2020/2184) — one of the lowest limits among heavy metals.

Sources of cadmium in waters are metallurgical industry (zinc, copper), Ni-Cd battery production, phosphorus fertilization (phosphates contain cadmium as contamination), electroplating, and corrosion of galvanized steel pipes. Cadmium is very mobile in the aquatic environment at low pH.

The GF-AAS technique is particularly suited for cadmium determination due to excellent sensitivity — a detection limit of about 0.05 µg/L allows reliable determination at 1/10 of the permissible standard. Cadmium atomizes at a relatively low temperature (1500–1800°C), but is sensitive to chloride interference — excess chlorides can cause premature volatilization of cadmium during pyrolysis. Therefore, use of a matrix modifier (NH₄H₂PO₄) is mandatory.

The PN-EN ISO 15586 standard provides detailed instrumental conditions for cadmium: wavelength 228.8 nm, modifier NH₄H₂PO₄ or mixture Mg(NO₃)₂ + NH₄H₂PO₄, pyrolysis temperature 500–700°C (with modifier), atomization temperature 1500–1800°C.

Method principle

A water sample (10–20 µL) is dosed into a graphite tube in the furnace. The temperature program includes: drying (110–130°C), pyrolysis (500–700°C with NH₄H₂PO₄ modifier — matrix removal without Cd losses), atomization (1500–1800°C — evaporation and atomization of cadmium), cleaning (2400°C). Free Cd atoms absorb radiation from a hollow cathode lamp at 228.8 nm. Absorbance (peak area) is proportional to the cadmium mass in the sample. Background correction (Zeeman or D₂ lamp) eliminates nonspecific absorption from matrix components.

Applications

Key parameters

ParameterValue
Wavelength228.8 nm
Detection limit (LOD)~0.05 µg/L
Limit of quantification (LOQ)~0.2 µg/L
Linear range0.2–5 µg/L
Atomization temperature1500–1800°C
Matrix modifierNH₄H₂PO₄ + Mg(NO₃)₂

Standard

Standard number
PN-EN ISO 15586:2005
Title (PL)
Jakość wody — Oznaczanie pierwiastków śladowych z zastosowaniem atomowej spektrometrii absorpcyjnej z piecem grafitowym
Title (EN)
Water quality — Determination of trace elements using atomic absorption spectrometry with graphite furnace

Step-by-step procedure

1. Preparation of vessels

PP/PTFE vessels soak in 10% HNO₃ (min. 24 h), rinse three times with ultrapure water. Do not use glass — cadmium adsorbs on glass.

⏱ Time: 24 h

2. Acidification and storage of samples

Add Suprapur HNO₃ to pH <2 (1 mL conc. HNO₃ per 100 mL sample). Store in PP at 4°C. Analysis within 14 days.

⏱ Time: 5 min

3. Preparation of standards

Prepare calibration series: 0, 0.5, 1, 2, 3, 5 µg/L Cd in 1% HNO₃. Prepare standards immediately before measurement.

⏱ Time: 15 min

4. Setting temperature program

Drying: 110°C (30 s), 130°C (20 s). Pyrolysis: 600°C (20 s). Atomization: 1650°C (5 s, reading). Cleaning: 2400°C (3 s). Ar flow: 250 mL/min (stop at atomization).

🌡 Temperature: 110–2400°C

5. Dosing modifier

Autosampler doses 5 µL mixture NH₄H₂PO₄ 1% + Mg(NO₃)₂ 0.1% together with 15 µL sample into graphite tube.

⏱ Time: 5 min

6. Calibration

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

⏱ Time: 20 min

7. Sample measurement

Measure samples in duplicates. Time of one measurement approx. 3 min (temperature program + cooling). Instrument works automatically.

⏱ Time: 3 min/sample

8. Quality control

Every 10 samples: blank <LOD, control standard (recovery 90–110%), duplicate (RPD <15%). For new matrix — standard addition method.

⏱ Time: 10 min

9. Verification of graphite tubes

Monitor tube condition — replace after 100–300 atomizations. Sign of wear is sensitivity drop and repeatability deterioration.

10. Calculation and reporting

Cd concentration from calibration curve. Result in µg/L with measurement uncertainty. For results <LOQ report as "<LOQ (0.2 µg/L)".

Required equipment and apparatus

EquipmentExampleIndicative price
AAS spectrometer with graphite furnaceAgilent 280Z AA, Analytik Jena ZEEnit 700P, Shimadzu AA-7000150 000–400 000 PLN
AutosamplerAgilent GTA 120, Analytik Jena MPE 60included with instrument
Hollow cathode lamp (HCL) CdAgilent Cd HCL, Heraeus, Photron — current 4 mA800–2 000 PLN
Graphite tubes with L'vov platformPyrolytically coated tubes with platform — improved sensitivity and repeatability50–150 PLN/pc.
Argon 5.0 (protective gas)50 L cylinder, two-stage regulator, purity 99.999%300–600 PLN/cylinder
PP/PTFE vesselsPolypropylene or PTFE containers — do not use glass (Cd adsorption)5–30 PLN/pc.

Reagents, media and consumables

ReagentCASDetails
Cd standard solution 1000 mg/L7440-43-9Certified CRM in 2% HNO₃ (e.g., Merck CertiPUR), traceable to NIST SRM
Nitric acid 65% Suprapur7697-37-2Ultrapure HNO₃ for acidifying samples (pH <2) and preparing dilutions
Modifier — NH₄H₂PO₄7722-76-1Ammonium dihydrogen phosphate 1% (w/v) — prevents Cd volatilization with chloride matrices
Modifier — Mg(NO₃)₂10377-60-3Magnesium nitrate 0.1% (w/v) — used together with NH₄H₂PO₄ for optimal stabilization
Ultrapure waterResistivity ≥18.2 MΩ·cm, Milli-Q system — mandatory for trace Cd analysis
Diluted nitric acid 1%For rinsing vessels and as blank — prepared from Suprapur HNO₃ and ultrapure water

Health and safety (OHS)

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