Original papersOn-site detection of heavy metals in agriculture land by a disposable sensor based virtual instrument
Introduction
Lead and cadmium have been recognized as highly toxic heavy metals with serious effects on the human health (Kemper and Sommer, 2002). Unlike other pollutants, heavy metals tend to accumulate in environment because of their long-time chemical stability and nondegradable character. The heavy metals in soil can be absorbed by the crops and provoke a decrease in plant growth. Moreover, the accumulation of these pollutants in soil can enter the livestock or human bodies through food chain, which causes immediate or long-term poisoning. In recent years, the increasing demand for heavy metals screening has led to the need for rapid, decentralized analytical methods that can produce reliable results in field conditions (Pei et al., 2000, Metters et al., 2011).
Typical monitoring methods for trace metals in soil are realized by discrete collecting samples in field and transporting them to centralized laboratories for analysis. Several known techniques mainly based on spectroscopic principle, namely atomic emission spectroscopy (AES) Li et al., 2004, atomic absorption spectroscopy (AAS) Báez et al., 2007 and inductively coupled plasma mass spectrometry (ICP-MS) Li et al., 2015, have been exploited for heavy metal determination. However, these methods are not suitable for in field application due to either time-consuming procedures, or complex sample pretreatment, or requirement of professional technicians and complex instruments (He et al., 2008). Electrochemical stripping analysis (ESA) has long been recognized as a powerful technique for measuring trace metals due to its remarkable sensitivity, fast speed, satisfactory selectivity and low cost. Nowadays, ESA has been widely applied to the determination of trace metals in food, beverage, water and other matrices (Economou, 2010). However, there are only few studies for analysis of metals in soil samples, especially for on-site application (Cooper et al., 2007, Palchetti et al., 2005, Ping et al., 2013, Christidis et al., 2007, Beni et al., 2005, Kadara et al., 2003, Beni et al., 2004, Kadara and Ibtisam, 2008). The major limitations for field soil analysis can be considered as follows: (I) The reliable sensors. Conventional electrochemical sensors are bulky, expensive and inconvenient, which need long time and complicated pretreatment before its use. Recent advances in electronics and micro-fabrication technologies have enabled the fabrication of minimal, disposable and ready to use sensors that named screen printed electrodes (SPE). However, the SPE is still faced some problems for soil application. It is partly attributed to the extremely low levels of heavy metals in natural environment, which makes the SPE suffer from the insufficient sensitivity for soil analysis. Furthermore, because of the high concentrations of organic matter and inorganic colloids in soil, the SPE signals of trace metals is often altered or even suppressed due to the absorption of those impurities onto the electrode surface. Therefore, special attention for the improvement of both sensitivity and anti-fouling ability of sensors should be paid before the soil analysis (Kefala et al., 2004). (II) The suitable extraction methodology. There are a lot of protocols have been designed for extraction of heavy metals in soil. In those protocols, long time mechanical-agitation steps (i.e., several hours) and large volume of reagents are commonly employed, which are unsuitable for the field implementation. Recently, the ultrasound-assisted extraction (UAE) has been proved to be a promising alternative technique that combines with the merits of simplicity, speed, economy and low reagent consumption. Despite such remarkable advantages, but so far, the number of publications using UAE coupled with electroanalytical for the detection of heavy metals in soil is still very limited (Calle et al., 2013, Kazi et al., 2006, Hwang et al., 2007). (III) The appropriate instruments. As noted above, only few studies for analysis of heavy metals in soil by ESA have been explored. In addition, most of those are carried out on the commercial electrochemical workstations, which are bulky, complicated and unsuitable for the outdoor deployment. Christidis and Beni have reported their single-chip controlled portable analyzer for the in-field measurement of Pb, Cd or Cu (Christidis et al., 2007, Beni et al., 2005). Nevertheless, these instruments are limited by their weak data handing capability and deficient performance, which result in a relatively high limit of detection (PPM level). Recently, the developments of “virtual instrument (VI)” technique have made it possible to fabricate the flexible instruments that combine the complex functionality with compact and inexpensive hardware.
In this work, a comprehensive study of field-based usage of ESA for the rapid screening of lead and cadmium in “real” soil is presented. A disposable and integrated SPE was fabricated by screen-printing technology and further modified with Nafion polymer and bismuth film. To the best our knowledge, this is the first reported use of this sensor for the determination of heavy metals in soil. Besides, a high performance yet portable detection instrument was also developed by the virtual instrument technique. Compared with the commercially available device, the major benefit of this instrument is that the analysis methodology is embedded in the software so that a simple and non-specialist operation is achieved. Combined with the portable instrument, the disposable SPE sensor as well as the fast UAE protocol, a novel integrated technology for the on-site measurement of heavy metals in soil is proposed. This system can be easily operated in field conditions with the advantages of fast speed, high precision and sensitivity, low operational cost as well as minimum physical dimensions.
Section snippets
Soil sample preparation
The soil samples were collected from some regions with cultivated lands (China), which are near highways or industrial areas. The extraction process was operated as follows: First, dried soil samples were grinded in a pestle and mortar, and further sieved by a 200 um sieve. A portion (1 g) of soil was placed in an extraction tube with 40 ml of 0.11 M acetic acid was added. The mixed sample was then exposed to ultrasonic bath for 1 h. The power of ultrasound can increases the extraction rate in the
Electrode fabrication
Screen-printed electrodes were prepared by screen printing printer. The brief fabrication process is as follows: First, carbon ink is printed onto a flexible polyester substrate through a 200 μm screen mesh for a working electrode (disc of 3.0 mm diameter) and a counter electrode. Next, the silver/silver chloride ink is printed on substrate for the reference electrode. Last, the epoxy insulation paste is covered on the electrode strip except the electrical connection and sensing part. The
Overall design
The principle of instrument is based on differential pulse anodic stripping voltammetry (DPASV). Its analysis process divides into two steps: deposition and stripping. In the deposition process, a constant negative potential is placed onto the working electrode for a specified time, in which the heavy metal ions are deposited and “pre-concentrated” onto the electrode surface. In stripping process, a positive staircase pulse sweep potential is applied onto the working electrode (Fig. 2), in
Analytical performance of instrument
In order to test the analytical performance of developed system, a series of standard solution containing lead and cadmium at known concentration were determined. Deionized water containing 0.1 M (PH 4.5) acetate buffer was used as electrolyte (Hočevar et al., 2002). To achieve the best performance of instrument, several key experiment parameters, such as bismuth concentration, initial and final potentials, frequency, width and increment of pulse, were optimized by the one-factor-at-a-time
Conclusions
A novel measurement system for rapid detecting, identifying, and measuring concentrations of lead and cadmium in soil has been developed. The system integrates a fast sample pretreatment procedure with a disposable SPE sensor and a portable virtual instrument. In order to overcome the possible errors during the qualitative and quantitative process, the identification statistical algorithm and the chemometrics method have been applied. The results show that the system yields a reliable accuracy
Acknowledgements
This work was financially supported by the Shandong Provincial Natural Science Foundation of China (NO. ZR2015CM016), and National Natural Science Foundation of China (NOs. 61473179 and 31471641), and the Research Fund for the Doctoral Program of Higher Education of China (NO. 20120008110033).
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