Journal of Analytical Methods in ChemistryVolume 2012 (2012), Article ID 512709, 10 pagesdoi:10.1155/2012/512709

Research Article

Effects of Iron Concentration Level in Extracting Solutions from Contaminated Soils on the Determination of Zinc by Flame Atomic Absorption Spectrometry with Two Background Correctors

Christophe Waterlot,1,2 Aurélie Pelfrêne,1,2 and Francis Douay1,2

¹Université Lille Nord de France, 59044 Lille, France²Groupe ISA, Equipe Sols et Environnement, Laboratoire Génie Civil et géo-Environnement (LGCgE) Lille, Nord de France (EA 4515), 48 boulevard Vauban, 59046 Lille Cedex, France

Received 8 November 2011; Accepted 10 December 2011

Academic Editor: K. K. Verma

Copyright © 2012 Christophe Waterlot et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

Zinc and iron concentrations were determined after digestion, water, and three-step sequential extractions of contaminated soils. Analyses were carried out using flame absorption spectrometry with two background correctors: a deuterium lamp used as the continuum light source (D₂ method) and the high-speed self-reversal method (HSSR method). Regarding the preliminary results obtained with synthetic solutions, the D₂ method often emerged as an unsuitable configuration for compensating iron spectral interferences. In contrast, the HSSR method appeared as a convenient and powerful configuration and was tested for the determination of zinc in contaminated soils containing high amounts of iron. Simple, fast, and interference-free method, the HSSR method allows zinc determination at the ppb level in the presence of large amounts of iron with high stability, sensitivity, and reproducibility of results. Therefore, the HSSR method is described here as a promising approach for monitoring zinc concentrations in various iron-containing samples without any pretreatment.

1. Introduction

Flame atomic absorption spectrometry (FAAS) is often described as a fast, simple, and sensitive technique for the measurement of zinc (Zn). This technique is widely used for the determination of Zn at trace levels in biological samples and food after mineralization process [1–4], but it usually requires pretreatment of samples such as sorption and/or preconcentration [5, 6], coprecipitation [7–9], liquid-liquid extraction [9, 10], solid-phase extraction [9–15], and more recently cloud point extraction [16, 17] in order to eliminate the matrix effects. However, these methods usually suffer from a lack of automation, increasing greatly the handling effort. Many research efforts have recently focused on a minimally time-consuming sample pretreatment, and consequently flow injection analysis (FIA) systems have been developed for the determination of Zn using FAAS [18–20]. Despite of these attempts, it is worth noting that the digestion process of soil samples is needed to convert them into solutions to be introduced through nebulization chambers of the FAAS.

Of the two atomic absorption lines of Zn, at 213.856 and 307.950 nm, the latter is hardly used for trace Zn analysis in FAAS because its sensitivity is 3,000 times lower than the former. Because this analytical line is subjected to spectral interferences by line overlapping at 213.859 nm and 213.853 nm due to the presence of Fe and Cu, respectively [21, 22], the determination of Zn at trace levels in the presence of Fe and/or Cu may be difficult with FAAS. For instance, the iron line at 213.859 nm cannot be completely resolved from the zinc resonance line at 213.856 nm by the optical system, resulting in a spectral interference using the conventional FAAS, without or with background correction, like deuterium lamp or Zeeman effect [23]. According to our knowledge, only the combination of the high-resolution continuum-source atomic absorption spectrometry with the least-squares background correction is able to resolve completely the problem of spectral interferences by direct overlap of absorption lines such as Fe and Zn [22, 23].

While very few studies have focused on the elimination of Fe in the determination of Zn using FAAS [24–27], the determination of Zn concentrations within the extracting solutions from contaminated soils without any pretreatment using FAAS is poorly documented, probably due to the low level of Fe and Cu matrix and the high level of Zn. Therefore, the present study focused on the use of a self-reversal background corrector. A first approach of the method has been proposed in 1983 by Smith and Hieftje [28]. A second approach has been recently developed and was called high-speed self-reversal method (HSSR method) [29]. This method was described as a universal technique covering the entire wavelength range from 190 to 900 nm. Based on previous studies in which it was shown that Cu concentrations were much lower than Zn within the contaminated soils located in the studied area [28, 29], the present work focused on the determination of Zn in extracting solutions containing high Fe concentrations using FAAS combined with the HSSR method. Results were compared with those obtained with the deuterium lamp used as the continuum-source background corrector (D₂ method). A systematic study was first conducted in spiked Zn solutions with low and high Fe concentrations in order to handle spectral interferences and matrix effects when the mobility of Zn in contaminated soils was examined. The method was then used to detect Zn concentrations extracted by water and aqua regia in certified reference materials and in contaminated soils, focusing on the possible overlapping analytical line of Zn at 213.856 nm with NO molecular absorption bands in the air-acetylene flame. The HSSR method was then validated using the first three steps of the sequential extraction procedure recommended by the SM&T (standards, measurements, and testing program) using two certified reference materials and contaminated soil samples.

2. Materials and Methods

2.1. Standard Solutions and Reagents

All solutions were prepared from analytical-grade reagents unless otherwise specified. Doubly distilled water (Carlo Erba, Val de Reuil, France) was used to prepare all aqueous solutions and dilutions.(i)Glacial acetic acid (Acrōs Organics, Noisy-le-Grand, France, d = 1.048) was used to obtain the 0.11 M acetic acid.(ii)0.5 M hydroxylamine hydrochloride was prepared by dissolving 34.75 g of the solid (Acrōs Organics) in 975 mL of doubly distilled water after adding 25 mL of 2 M nitric acid (HNO₃), prepared by diluting 12.7 mL of HNO₃ (J.T. Baker for metal trace analysis, Deventer, Netherlands, 70%, d = 1.42) to 100 mL in a volumetric flask.(iii)1 M ammonium acetate solution was obtained by adding 77.08 g of the solid in 1000 mL of doubly distilled water after adjusting the pH (pH = 2) with 65% HNO₃ (d = 1.40).(iv)Hydrogen peroxide was from J.T. Baker.(v)Aqua regia was obtained by mixing concentrated 4.5 mL of hydrochloric acid (J.T. Baker, 37%, d = 1.19) and 1.5 mL of HNO₃ (70%).

All glassware and polypropylene materials were cleaned by soaking for 1 day in 0.5 M nitric acid (J.T. Baker) and by rinsing with doubly distilled water. Zinc solutions of 1, 2, and 5 mg L⁻¹ in 2% HNO₃ (Chemical Products for Analysis, Association Corporation Standard Distribution; C.P.A. groupe A.C.S.D., Voisins le Bretonneux, France) were used for the preparation of the calibration solutions and test solutions containing Fe.

2.2. Instrumentation

An atomic absorption spectrometer (Shimadzu AA-6800, Tokyo, Japan) with an ASC-6100 auto-sampler (Shimadzu) was used for the determination of Fe and Zn with an air-acetylene flame. For Fe, the instrumental parameters were as follows: wavelength 248.3 nm; lamp current 12 mA; bandpass 0.2 nm; a deuterium lamp (Hamamatsu, Photonics K.K., Tokyo, Japan) for the background correction. For Zn, a conventional hollow-cathode lamp from Hamamatsu was used at 213.856 nm with a 0.5-nm spectral bandpass and at 10 mA in combination with a deuterium lamp. A Zn high-intensity boosted-discharge hollow-cathode lamp from Hamamatsu was also used as the spectral radiation source. This lamp was operated with two different discharges (10 mA and 300 mA) in order to increase the emission intensity. During the analytical measurements, the Zn lamp was operated at low and high currents with a frequency of 100 Hz. At high currents (300 mA), the absorbance (Abs) measured for a narrow atomic line is low, and the specific absorption of the target element is zero as well, whereas the apparent absorbance caused by a broadband background contributor remains as high as when the lamp is operated at low current levels. In contrast, at conventional current levels (10 mA) and specific wavelength (213.856 nm), the energy related to the absorption of the target element is maximum. As a consequence, the difference in absorbance with the lamp operated at low and high currents gives the background correction.

2.3. Test Solutions of Zn and Fe

Test solutions containing Zn and Fe were prepared from the stock solutions described above. Samples were analyzed in pairs to allow for machine drift, for example: Zn 1 mg L⁻¹; Zn 1 mg L⁻¹ + Fe 0 mg L⁻¹; Zn 1 mg L⁻¹; Zn 1 mg L⁻¹ + Fe 0.5 mg L⁻¹, Zn 1 mg L⁻¹; Zn 1 mg L⁻¹ + Fe 1 mg L⁻¹, and so forth. The experiments were conducted with all extracting solutions used (water, acetic acid, and hydroxylamine hydrochloride).

2.4. Soil Sampling and Pretreatment Procedure

The soil samples (agricultural fields and kitchen gardens) used in this work were collected in a contaminated area highly affected by the past atmospheric emissions of two lead and Zn smelters located in the north of France [28–32]. For each soil type, a composite sample was constituted in the ploughed layer (0–25 cm) and was prepared following the NF ISO 11464 procedure. The soil samples were air-dried at a temperature below 40°C, crushed to pass through a 2 mm stainless steel, and sieved to less than 250 μm particle size with an ultracentrifugal mill (Retsch type ZM 200, Hann, Germany). Two certified reference materials, sediment (BCR-701, Piedmont, Italy) and sewage sludge-amended soil (CRM-483, Great Billings Sewage Farm, Northampton), were used for the validation method.

2.5. Extraction Procedures

Digestion of kitchen garden soil samples (KG1 to KG9) was carried out using a microwave oven (Berghof Speedwave MWS-2, Eningen, Germany) with a system to control the temperature inside the reactor pressure vessel. Initially, 300 mg of each sample was transferred to a 100 mL digestion tube, and a mixture of nitric acid (70%, (m/m), 1.5 mL) and hydrochloric acid (37%, (m/m), 4.5 mL) was added. After mineralization, digestion products were completed to 25 mL with doubly distilled water and stored in acid-washed plastic bottles at 4°C prior to analysis.

Water-soluble metal ions were extracted from kitchen garden soils in triplicate with the following procedure: 3 g of each representative sample was shaken with a soil/extractant ratio of 1/10 (w/v) using a rotor disc (10 rpm) for 2 h. The extract was separated from the solid residue by centrifugation (4,530 rpm, Rotanta 460 Hettich, Tuttlingen, Germany) for 20 min at room temperature. Afterwards, the solution was filtered over an acetate Millipore membrane (Millipore, 0.45 μm porosity, Minisart). The solution was then placed in a polypropylene container and stored at 4°C until metal analysis.

The three-step extraction procedure was used to determine Zn fractionation in the certified and contaminated agricultural soils (A1 to A10) [33]. Each of these steps was noted as being fraction F1, F2, or F3 (Table 1).

Table 1: Sequential extraction procedure (from Rauret et al. [33]).

Steps
Extracting solutions
Nominal target phases

1
Acetic acid 0.11 M
Fraction F1: exchangeable, water- and acid-soluble

2
Hydroxylamine + hydrochloric acid 0.50 M at pH 2
Fraction F2: reducible

3
Hydrogen peroxide 8.8 M, + ammonium acetate 1.0 M at pH 2
Fraction F3: oxidizable

Zinc and Fe concentrations were expressed as mg kg⁻¹ dry weight (DW). For this, the moisture content of each sample was established by drying a separate 1-g sample in an oven (Binder, Tuttlingen, Germany) at 105 ± 2°C until it reached a constant mass according to the NF ISO 11465 standard.

2.6. Statistical Analyses

The Mann-Whitney test (nonparametric statistical test) was used to find out the influence of Fe in the determination of Zn concentrations in the test solutions. For each extracting solution and background corrector, this test was carried out to determine significant differences among Zn concentrations according to the background corrector and certified or indicative values. All statistical tests were performed using Statistica 6.0 (Statsoft, Tulsa, OK, USA) for Windows. The level of significance was set at .

3. Results and Discussion

3.1. Analytical Performance and Spectroscopic Conditions

Analyses were carried out using each batch of solutions as reagent blanks. The figures of merit of both methods were established using each extracting solution [34] and are shown in Table 2.

Table 2: Calibration data for the determination of Zn.

Background corrector
Calibration range (μg L⁻¹)
Equation of calibration curves
LOD (μg L⁻¹)

D₂-FAASa
2–25
Abs = 0.47790 [Zn] + 0.00553R² = 0.9991
2.8

HSSR-FAASa
2–25
Abs = 0.44075 [Zn] + 0.00015R² = 0.9988
1.5

D₂-FAASb
2–25
Abs = 0.37643 [Zn] + 0.00030R² = 0.9993
6.5

HSSR-FAASb
2–25
Abs = 0.37154 [Zn] + 0.00074R² = 0.9992
1.9

D₂-FAASc
2–25
Abs = 0.42581 [Zn] + 0.00080R² = 0.9992
3.8

HSSR-FAASc
2–25
Abs = 0.31517 [Zn] − 0.00044R² = 0.9991
1.6

D₂-FAASd
2–25
Abs = 0.42600 [Zn] + 0.00038R² = 0.9973
2.6

HSSR-FAASd
2–25
Abs = 0.27455 [Zn] − 0.00029R² = 0.9981
0.7

D₂-FAASe
2–25
Abs = 0.36182 [Zn] + 0.00015R² = 0.9987
3.1

HSSR-FAASe
2–25
Abs = 0.32234 [Zn] − 0.00070R² = 0.9993
1.9

aIn water.

bIn 0.11 M acetic acid.

cIn 0.5 M hydroxylamine hydrochloride (F2).

dIn 1 M ammonium acetate pH = 2 (F3).

eIn HNO₃ 14%.

The calibrations covered Zn concentrations ranging from 2 to 25 μg L⁻¹ and were linear. The correlation coefficient ranged from 0.9983 to 0.9993, depending on the extracting solutions. In all experiments, the slopes of the calibration curves as well as the dynamic calibration ranges obtained with the HSSR method were slightly lower than those from the D₂ method. These results indicate that the HSSR method had the lowest sensitivity and imply that the limiting absorbance values are smaller than those for the D₂ method. As recorded for other elements [35], the cause of the calibration curve flattening is probably due to the high stray-light levels of the boosted-discharge hollow-cathode lamp. In contrast to the results obtained with the D₂ method, no roll-over (i.e., a decrease of absorbance at high concentrations) occurred for Zn in the extracting solutions with the HSSR method (Figure 1).

Figure 1: Analytical curve for Zn in 0.11 M acetic acid measured in FAAS with the HSSR method at 213.856 nm.

Limits of detection (LOD) were defined as the concentration equivalent to three times the reagent blank (water, acetic acid, hydroxylamine hydrochloride, ammonium acetate at pH = 2, nitric acid 14%; ). Using the HSSR method, the LOD values were the lowest (Table 2). For instance, LOD values in F1 and F3 fractions were 3.5-fold and 3.7-fold lower than those obtained with the D₂ method. Improvement of the LOD may be due to the reduction of the baseline noise and the better stability during the flame atomization of Zn when the HSSR method was used. The precision of this method was evaluated as the relative standard deviation (R.S.D) of 13 replicate determinations of Zn at 5 and 10 μg L⁻¹ and 0.5 and 1 mg L⁻¹ in each extracting solution. The R.S.D ranged from 0.12 to 1.37%, reflecting a good reproducibility of the background corrector effects with solutions at low level of Zn (in the same order of magnitude of the LOD). On the other hand, under the working conditions (dilute nitric acid) no interference related to the overlapping analytical line of Zn at 213.856 nm with NO molecular absorption bands in the air-acetylene flame was detected. This result is in accordance with phenomena reported by de Oliveira et al. [36].

3.2. Determination of Zn in Test Solutions

The effects of Fe on Zn concentrations in water were studied with the two configurations selected for background correction (Figure 2). An overestimation of Zn concentrations measured in spiked solutions with the D₂ method was observed for Zn at 0.01 mg L⁻¹, Zn at 0.5 mg L⁻¹ and Fe > 250 mg L⁻¹, and Zn at 1 mg L⁻¹ and Fe > 500 mg L⁻¹. Surprisingly, Zn concentrations in these solutions with Fe concentrations ranging from 0.5 to 100 mg L⁻¹ were lower than 1 mg L⁻¹, reflecting an overcompensation of the deuterium background correction. In contrast, Fe concentrations below 25 mg L⁻¹ did not cause any interference for deuterium corrector in the solution of Zn at 0.5 mg L⁻¹ (Figures 2 and 3). These results show that the under- and overcompensation of Zn concentrations using the deuterium corrector depended on Zn concentrations and Fe/Zn ratios.

Figure 2: Effect of Fe on the three concentrations of Zn (0.01, 0.5, and 1 mg L⁻¹) measured in water by FAAS at 213.856 nm with the D₂ and HSSR methods.

(a)

(b)

Figure 3: Effect of Fe in water on the signal of Zn at 0.5 mg L⁻¹ using (a) deuterium background correction (D₂ method) (b) high-speed self-reversal background correction (HSSR method).

While serious interferences can be observed with the D₂ method due to the low background correction (Figure 3(a)), the presence of Fe did not show a significant effect on Zn absorbance using the HSSR method (Figure 3(b)). As shown in Figures 2 and 3, experimental Zn concentration values were very close to the theoretical ones whatever the Fe concentration within the solutions. For instance, in the mixture of Zn and Fe at 0.01 mg L⁻¹ and 3,000 mg L⁻¹, respectively, the mean concentration of Zn measured using the HSSR method was  mg L⁻¹, reflecting the efficiency of this method to eliminate the Fe spectral interference in the course of Zn determination. Similar results were obtained in 0.11 M acetic acid-spiked solutions (Figure 4). However, the increase in the signal absorbance of Zn at low concentrations in the acid solutions was lower than that in the water, showing an effect of the solvent on the concentration measured with the D₂ method. In contrast, even at low Fe concentrations, this background correction appeared to be unsuitable for the determination of Zn in 0.5 M hydroxylamine hydrochloride solution, which is included in the SM&T program (Figure 5). Signal absorbance generally increases with the Fe concentration, leading to higher measured concentrations of Zn than those present in the solutions. Additionally, the Zn signal decreased to such an extent that it turned out to be lower than that related to the Zn concentration at 0.5 mg L⁻¹ indicating either an overcorrection due to the presence of Fe and/or a suppressive effect of chloride ions on the signal of Zn [37].

Figure 4: Influence of Fe on the three concentrations of Zn (0.01, 0.5, and 1 mg L⁻¹) measured in 0.11 M acetic acid by FAAS at 213.856 nm with the D₂ and HSSR methods.

Figure 5: Influence of Fe on the three concentrations of Zn (0.01, 0.5, and 1 mg L⁻¹) measured in 0.5 M hydroxylamine hydrochloride by FAAS at 213.856 nm with the D₂ and HSSR methods.

For each Zn concentration, interference effects of Fe were minimized and even avoided when a boosted hollow-cathode lamp was employed for the HSSR background correction. Moreover, the Mann-Whitney test results showed that Fe interferences were not significant when the Fe concentration was less than 3,000 mg L⁻¹ and the ratio of Fe/Zn was smaller than 300,000.

3.3. Application to Soil Samples

Depending on the physicochemical parameters of soils (pH, organic matter, and Fe contents), the possible migration of Zn to the depth of contaminated soils located in the studied area was considered [32]. Modeling to predict the solubility of Zn in soils is therefore very important for the management of polluted soils and industrial sites. In this way, the potential mobility and bioavailability of Zn are often evaluated using various extracting solutions including water and those used in the SM&T sequential extraction procedure. There are recurrent problems during the determination of this element by FAAS because of the large amounts of Fe in extracting solutions and the closeness (0.003 nm) between the two atomic absorption lines of Zn and Fe [26]. First of all, pseudototal Fe, Cu, and Zn concentrations in kitchen garden soil samples were determined after their microwave-assisted digestion (Table 3).

Table 3: Pseudototal Fe, Cu, and Zn concentrations (mean value ± standard deviation) measured in certified reference soil () and kitchen garden (KG) soil samples ().

Samples
Fe in this work (mg kg⁻¹)
Cu in this work (mg kg⁻¹)
Zn certified value (mg kg⁻¹)
Zn with the D₂ method (mg kg⁻¹)
Zn with the HSSR method (mg kg⁻¹)

BCR-483
26,642 ± 1,180a
403 ± 11c
987 ± 37b,c
939 ± 48
1,013 ± 59

BCR-701
36,975 ± 342d
43.8 ± 1.5e
454 ± 19f
474 ± 15
478 ± 7

KG1
22,496 ± 717

821 ± 10
808 ± 6

KG2
24,681 ± 799

513 ± 4
531 ± 7

KG3
23,628 ± 685

813 ± 15
958 ± 17

KG4
18,846 ± 578

867 ± 9
895 ± 1

KG5
20,026 ± 624

1,052 ± 21
1,051 ± 12

KG6
24,399 ± 790

1,398 ± 21
1,410 ± 24

KG7
18,851 ± 580

505 ± 3
522 ± 6

KG8
27,029 ± 890

4,502 ± 25
4,842 ± 54

KG9
31,440 ± 661

655 ± 5
667 ± 5

aFrom Kubová et al. [38], [Fe] = 26,700 ± 480 mg kg⁻¹.

bIndicative value from Rauret et al. [39], ().

cFrom Pueyo et al. [40], [Zn] = 1,026 ± 37 mg kg⁻¹; [Cu] = 373 ± 14 mg kg⁻¹ ().

dFrom Kubová et al. (2004) [38], [Fe] = 38,580 ± 220 mg kg⁻¹.

eCertified value: [Cu] =  mg kg⁻¹ ().

fFrom Pueyo et al. [40], [Zn] = 474 ± 10 mg kg⁻¹ ().

Measurements were performed by dilution of 1 : 10 aqua regia extracts with doubly distilled water except for KG8, for which a dilution of 1 : 20 was necessary. Zinc concentrations were in the range 0.56–2.90 mg L⁻¹ and Fe concentrations ranged from 15.8 to 37.7 mg L⁻¹. In almost all cases, Zn concentrations measured with the D₂ method were lower than those determined using the HSSR method, and significant differences () were obtained for KG2, KG3, KG4, KG7, KG8, and KG9. The mean concentration of Zn found in the BCR-483 material using the D₂ method was significantly lower than that measured by Pueyo et al. [40]. This result was attributed to an underestimation of the Zn concentrations related to overcompensation of the deuterium background correction observed in the Zn solution at 1 mg L⁻¹ spiked with Fe (Figure 2). In contrast, the values reported for both certified materials obtained with the HSSR method were very close to those found by Pueyo et al. [40] using ICP-MS with all precautions to prevent matrix interferences. As shown for the spiked Zn solutions, and compared to the certified or indicative values, the accuracy of the results can be explained by the efficiency of the HSSR method in correcting the background of Fe near the analytical line of Zn. In order to supplement this approach, the concentrations of Zn were measured using the two background correction systems in undiluted water extracts. Data are reported in Table 4. Depending on the Fe/Zn ratio (ranging from 7 to 2,481), the concentrations of Zn measured with the D₂ method were up to 40-fold higher than those obtained with the HSSR method. The magnitude of the difference between Zn concentrations in the water extracts from the KG2 soil sample with both background correction systems is in agreement with the results obtained using the spiked Zn solution at 10 μg L⁻¹ with a high Fe/Zn ratio. It reflects an undercorrection of the deuterium background system, providing an overestimation of Zn concentrations. In contrast, the Zn concentrations found in the water extracting solution from KG8 were not significantly different for the two background systems. From a statistical point of view, the high standard deviation value can explain this result but it seems clear that the low value for the Fe/Zn ratio (Fe/Zn = 7.16) is a more appropriate explanation.

Table 4: Water-extractable Fe and Zn concentrations (mean value ± standard deviation, ) in kitchen garden (KG) soil samples.

Samples
Fe (mg kg⁻¹)
Zn with the D₂ method (μg kg⁻¹)
Zn with the HSSR method (μg kg⁻¹)
Fe/Zn

KG1

3,1
2,4
31.6

KG2

2,481

KG3

1,1

7.0

KG4

3,9
3,2
21.9

KG5

9

KG6

5,7
4,8
23.3

KG7

1,0

53.2

KG8

18,2
16,7
7.1

KG9

4,7
4,2
24.9

Analytical studies were further carried out with the extracting solutions included in the 3 steps sequential extraction procedure proposed by the standards measurements and testing program (SM&T) of the European Union. The mean concentrations of Zn found with the D₂ and HSSR methods in the BCR-701 and BCR-483 certified materials, as well as the certified or indicative values for this analyte and Fe, are shown in Table 5. For both certified materials, significant differences () were found between Zn concentrations measured using the D₂ method and certified or indicative values. An exception was noted for the Zn concentration in the F3 fraction of the BCR-483 certified material. The greatest differences were observed in step 2, in which 0.5 M hydroxylamine hydrochloride was used to release the free Fe oxides [41]

Table 5: Certified and obtained Fe and Zn concentrations in BCR-701 () and BCR-483 () using the BCR three-step sequential extraction procedure.

Fraction
Metal
BCR-701
BCR-483

Certified value
Obtained value
Indicative valuea
Obtained value

D₂ method
HSSR method
D₂ method
HSSR method

mean ± U
mean ± SD
mean ± SD
mean ± U
mean ± SD
mean ± SD

(mg kg⁻¹)
(mg kg⁻¹)
(mg kg⁻¹)
(mg kg⁻¹)
(mg kg⁻¹)
(mg kg⁻¹)

F1
Zn
205 ± 6
238 ± 12
205 ± 13
441 ± 39
458 ± 11
442 ± 12

Fe
71 ± 1b
83 ± 1

36 ± 2b
36 ± 2

F2
Zn
114 ± 5
162 ± 13
123 ± 3
438 ± 56
463 ± 18
439 ± 20

Fe
7,698 ± 106b
7,732 ± 109

6,691 ± 198b
6,520 ± 219

F3
Zn

Fe
1,097 ± 53b
1,195 ± 45

1,153 ± 29b
1,164 ± 149

U: uncertainty (half-width of the 95% confidence interval); SD: standard deviation.

aFrom Rauret et al. [39].

bIndicative values from Kubová et al. [38].

As shown in Table 5, the high concentrations of free Fe in the F2 fraction led to an overestimation of Zn concentrations, reflecting an undercompensation of the deuterium background system. In contrast, FAAS measurements combined with the HSSR method yielded values were very close to the certified or indicatives ones, showing the efficiency of the method for correcting the Fe spectral interferences. The same general trends were observed for the distribution of Zn in contaminated agricultural soil samples (Table 6). Zinc concentrations measured with both background systems in the first fraction were very close to each other. An exception was observed with the A5 sample, which presented the highest Fe concentration. In contrast, differences between the concentrations of Zn in fractions F2 and F3 were up to 35%, mainly due to the order of magnitude of Fe concentrations in these fractions (from 494 to 3,498 mg kg⁻¹). Despite the high Fe concentration found in F2 of sample A10, it is important to note that the mean concentration of Zn was lower using the D₂ method than the HSSR method. Taking into account the liquid/solid ratio and the dilution factor, the concentrations of Zn and Fe were 0.99 and 6.6 mg L⁻¹, respectively. The result is consistent with the data presented in Figure 5 reflecting an underestimation of Zn at 1 mg L⁻¹ in presence of Fe from 2.5 to 10 mg L⁻¹ using the D₂ method. All of these results confirm that the HSSR method is an efficient background compensation of the spectral interferences caused by Fe during Zn measurements using FAAS.

Table 6: Fe and Zn concentrations at each step of the SM&T sequential extraction procedure.

Samples
Fractions

F1
F2
F3

Zn (mg kg⁻¹)
Fe (mg kg⁻¹)
Zn (mg kg⁻¹)
Fe (mg kg⁻¹)
Zn (mg kg⁻¹)
Fe (mg kg⁻¹)

D₂ method
HSSR method

D₂ method
HSSR method

D₂ method
HSSR method

A1
46.7
50.7
3.4
60.2
54.6
1,223
27.0
20.1
494.5

A2
132.6
120.5
18.9
143.8
138.3
1,361
114.5
111.7
1,357

A3
181.3
211.1
23.4
135.6
128.6
1,187
123.5
102.8
1,225

A4
117.0
124.0
18.5
138.0
130.3
1,398
136.9
119.3
1,115

A5
619.6
565.5
67.3
288.5
265.1
1,337
1,453
1,450
4,762

A6
108.7
111.8
0.6
205.6
177.7
1,220
77.7
65.4
638.8

A7
87.5
78.5
1.5
85.0
70.1
873.6
53.3
49.5
498.2

A8
35.2
33.9
0.2
288.1
277.2
1,800
95.7
85.0
1,046

A9
72.5
71.1
0.8
155.6
146.6
2,142
59.8
47.9
930.9

A10
147.0
152.5
18.9
397.7
409.8
2,626
347.8
334.1
3,498

3.4. Efficiency of the HSSR Method

As reported by Sweileh and El-Nemma [26], the determination of Zn in the presence of high concentrations of Fe (e.g., some geological samples, meteorites, or steels) is problematic using FAAS. From our investigations, the Zn-free solution containing 0.2%, 0.3%, and 2% Fe appeared to contain 0.13, 0.14, and 0.39 mg L⁻¹ of Zn, respectively. The last value is in agreement with the previously reported spectral interference of Fe in the determination of Zn [26] indicating that the deuterium background correction is not always suitable for compensating the Fe spectral interference in Zn. We determined the trace amounts of Zn in the 2% Fe solution with the proposed method. The results are summarized in Table 7. The reported values of Zn measured by FAAS with the D₂ method were greater than the Zn concentrations added in the Fe solution. In contrast, the Zn concentrations measured by FAAS with the HSSR method were very close to the added concentrations, proving the effectiveness of the proposed technique for correcting matrix effects and spectral interferences in FAAS.

Table 7: Determination of traces of Zn in 2% Fe solution by direct aspiration-FAAS using the D₂ and the HSSR methods.

Zn concentration added (mg L⁻¹)
Zn concentration found (mg L⁻¹)

D₂ method
HSSR method

0.5

0.75

1

1.5

Means and standard deviations for triplicate analyses.

4. Conclusions

The extractable concentrations of Zn (aqua regia, water, and sequential extractions) were determined by FAAS with two background correction systems. The first was based on the well-known deuterium background correction and the second involved the use of a single Zn hollow-cathode lamp pulsed with currents ranging from 10 to 300 mA with a frequency of 100 Hz. Depending on the extracting solutions, but also on the Zn concentration and the Fe/Zn ratio, it was demonstrated that background correction with a deuterium lamp led to significant errors (e.g., over- and underestimation). In contrast, the HSSR method appeared to be a more versatile technique for the compensation of spectral interferences caused by absorption line overlapping. The proposed method allowed Zn determination at the g L⁻¹ level in the presence of large concentrations of Fe with high stability and sensitivity. With a good LOD and R.S.D, this method shows promise for monitoring zinc concentrations in various Fe-containing samples without any pretreatment.

Standard

NF ISO 11464. Soil Quality—Pretreatment of samples for physicochemical analyses. AFNOR, 1994, 9 p.

NF ISO 11465. Soil Quality—Determination of dry matter and water content on a mass basis-gravimetric method. AFNOR, 1994, 4 p.

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