INTRODUCTION
Toxic heavy metal contamination of freshwater sources is a severe environmental and human health crises in Iraq, especially in such Governorates as Baghdad Governorate where industrial effluents and agricultural runoffs have direct effects on the Tigris River basin [1]. Primary concern are lead (Pb2+) and cadmium (Cd2+) as they are highly toxic, persistent and bioaccumulative in the food chain. The chronic exposure even as a trace level may result in serious neurological, renal, and developmental disorders [2]. The World Health Organization (WHO) has set very strict concentrations of these metals in drinking water: 10 0g/L of Pb2+ and 3 0g/L of Cd2+ [3].
Inductively coupled plasma mass spectrometry (ICP-MS) and atomic absorption spectroscopy (AAS) are both high sensitivity and accuracy conventional methods of analysis but are not always feasible in routine monitoring at low resource settings, since they are expensive to operate, demand a trained staff, and are not portable [4]. As a reaction to this, nanomaterial-based electrochemical sensors have become viable alternatives that have the benefit of miniaturization, cost-effectiveness, fast response, and on-site analysis [5].
Graphene oxide (GO) has received much interest as a sensing platform because of its high surface area, high electrical conductivity, and the presence of numerous oxygen-based functional groups which enable it to interact with metal ions strongly [6]. The mix of nanoparticles with gold nanoparticles (AuNPs) is shown to have better electron transfer kinetics, catalytic, and signal amplification, which are significant characteristics of ultrasensitive electrochemical detection [7]. Despite a number of GOAu based sensors being reported, not many have been strictly tested in real Iraqi water matrices and under a real field.
This paper fills this gap by designing and fully validating a new electrochemical sensor that uses a graphene oxide gold nanocomposite (GO -AuNC) immobilized on a screen-printed carbon electrode (SPCE). The sensor was used to measure Pb2+ and Cd2+ in 42 water samples taken in different locations within the Baghdad Governorate. Analytical performance was assessed based on ICH Q2(R1) guidelines and the performance was compared with ICP-MS. The work contributes to the Sustainable Development Goal 3 (Good Health and Well-being) as it allows the decentralized surveillance of water quality in resource-constrained settings.
MATERIALS AND METHODS
Chemicals and Reagents
Chemicals were of analytical grade. Purchases were made of lead(II) nitrate, cadmium(II) nitrate, potassium ferricyanide, potassium chloride, hydrogen peroxide (30%), graphite powder, and sodium nitrate (Sigma-Aldrich, Germany; and Merck, USA). The deionized water (18.2 M oh resistivity) was purchased through a Milli-Q purification system (Millipore, France).
Instrumentation
Electrochemical analysis was done on PalmSens4 potentiostat (PalmSens, Netherlands). Scanning electron microscopy (SEM, JEOL JSM-7610F) and X-ray diffraction (XRD, Bruker D8 Advance) were used to characterize them morphologically and structurally. Functional group analysis was done by Fourier- transform infrared spectroscopy (FTIR, PerkinElmer Spectrum Two).
Graphene Oxide -Gold Nanocomposite (GO -AuNC) Synthesis
Graphene oxide was prepared by a modified Hummers method by using graphite powder [9]. In a word, graphite (2 g) and NaNO3 (1 g) were introduced into concentrated H2SO4 (90 mL) at ice-cooling. KMnO4 (8g) was placed in the flask little by little keeping the temperature at 20 °C. The mixture was stirred. 35 °C, 2 h and deionized water (200 mL) added to stop oxidation, and H2O2 (30 mL) added. The suspension that resulted was centrifuged severally until one obtained neutral pH.
The nanoparticles of gold were prepared by reducing AuCl4 (1 mM) using trisodium citrate (1%), at 100 °C in a 15 min period [10]. GO Au nanocomposite was prepared by flocculating the GO dispersion (2 mg/mL, 50 mL) with HAuCl4 solution (1 mM, 10 mL) under ultrasonic stirring of 30 min and then dropwise adding NaBH OH (0.1 M, 5 mL) and the mixture was refluxed at 80 °C, 2 hours [11]. The last black dispersion was kept at 4 oC.
Sensor Fabrication
The transducer platform was an array of carbon electrodes screen-printed onto a carbon substrate (SPCEs, DRP-110, Metrohm DropSens, Spain). Electrochemical cleaning of electrodes Before modification, the electrochemical cleaning of electrodes was performed by cyclic voltammetry at 0.1M KCl between potentials of −0.2 and +1.0 V versus Ag/AgCl in 10 cycles [12]. Then the drop-cast of the dispersion of the GO-AuNC (1 mg/mL) onto the working electrode surface was left to dry at room temperature and under 2 h. The incised electrode (GO–AuNC/SPCE) was washed with deionized water.
Water Sampling and Preparation If samples were to be used, they had to be collected and prepared to ensure no contamination occurred.<|human|>Water Sampling and Preparation In the event that water samples were to be used, they must be gathered and prepared in a way that will not contaminate sample.
Four sources in Baghdad Governorate (Tigris River, n = 15, agricultural drainage canals, n = 12, industrial effluents, n = 8, and residential tap water, n = 7) were sampled by using 42 water samples between October and December 2025. Samples were preserved in acid-washed (polyethylene) bottles and acidified (pH < 2) with ultrapure HNO 3 and kept at 4 C until being analyzed following 48 h as specified in EPA Method 1640A [13].
Electrochemical Measurements
Quantitative analysis was done with the help of differential pulse voltammetry (DPV). The measurements were done in 0.1 M acetate buffer (pH 4.5) with the sample or standard solution in 10 mL. Optimized DPV parameters were as follows: potential window -1.2 to -0.2 V (vs. Ag /AgCl), pulse amplitude 50 m V, pulse width 50 ms, scan rate 20 m V /s [14]. The measurements were taken at 60 s of stirring, and the background was subtracted using empty signals of the buffer.
Method Validation
Analysis performance of the sensor was checked based on ICH Q2(R1) requirements [15]. The degree of linearity was evaluated at six levels of concentrations (0.1 to 50 7g/L). The limits of detection (LOD) and quantification (LOQ) have been determined as 3.3 /S and 10/S, respectively, where 3.3 is the standard deviation of the blank (n = 10) and S is the slope of the calibration curve. Precision was assessed as the intra and inter-day relative standard deviation (RSD, n = 6). Spike-recovery experiments were used to determine accuracy at 3 concentration levels (5, 15 and 30 0g/L). Bland Altman analysis was used to determine agreement with ICP-MS [16].
Statistical Analysis
The SPSS 28 software (IBM, USA) was used in the analysis of data. Mean concentrations between the sites of sampling were compared using one-way ANOVA with Tukey post hoc test (p < 0.05).
RESULTS AND DISCUSSION
Morphological and structural characterization were used to establish the successful attachment of gold nanoparticles (AuNPs) onto the graphene oxide (GO) sheets in the first occurrence. The imaging of scanning electron microscopy (SEM) showed the typical wrinkled and layered morphology of GO which gives it a high-surface-area scaffold, allowing it to prevent restacking and allow access to analytes. Regularly dispersed spherical AuNPs with an average diameter of 20-30 nm were evidently derivatized onto the GO surface as indicated in Fig. 1. This uniform distribution is paramount in maximization of electroactive sites and in reproducible sensor response.
Additional structural confirmation was done through X-ray diffraction (XRD). In Fig. 2, the diffractogram has two separate peaks: a wide reflection at 2 - 26.5 and a sharp and intense peak at 38.2, which is ascribed to the (002) plane of GO and the (111) crystalline plane of metallic gold in a face centered cubic structure respectively. The other impurity peaks are absent, and this proves the purity of the phase of the synthesized nanocomposite.
Fourier-transform infrared (FTIR) spectroscopy was used to give a complementary analysis of chemical bonding between GO and AuNPs. As Fig. 3 shows, the spectrum has typical functional group vibrations, with a high peak at 1720 cm-1. This low-wavenumber band is attributed to AuO stretching vibrations and it proves that there is some covalent or coordinative bond between oxygen functionality of GO and surface of AuNPs. This stabilization of the nanocomposite as well as electron transfer at the electrode-electrolyte interface.
Differential pulse voltammetry (DPV) was used to assess the electrochemical behavior of the GO2 AUNC/SPCE in a binary solution of Pb2+ and Cd2+. Fig. 4 shows two distinct and sharp reduction peaks at -0.58 V and -0.82 V (vs. Ag/AgCl), which are attributed to Pb2+ with Cd2+ respectively. The separations have reached a peak of 240 m V high enough to enable both of the metals to be quantified in the same scan without interference with each other- a very critical requirement in real world environmental monitoring.
Table 1 summarizes the parameters of analysis of the developed sensor. The approach showed a remarkable level of sensitivity whereby a two order of magnitudes (0.150 50 50) linear calibration curves covering both analytes were obtained. To determine the limits of detection (LODs), 0.032 μg/L and 0.041 μg/L were determined as the limits of detection of Pb2+ in the case of Pb2+and also the limits of detection of Cd2+ in the case of Cd2+. These values are not only much lower than the WHO maximum permissible amounts (10 μg/L of Pb2+and 3 00g/L of Cd2+) but also exceed a number of recently reported nanomaterial-based sensors, which highlights the synergistic action of the GO-AuNC structure in signal amplification and noise reduction.
The parameter of selectivity is a very important parameter when real-sample analysis is done where complex matrices have a large number of interferents that can potentially occur. The stability of the sensor was challenged with the presence of the common cations like Ca2+, Mg2+, Zn 2 and Cu2+ at 100 times excess concentration against the target analytes. Table 2 shows that signal deviation of both Pb2+ and Cd2+ did not exceed 5 per cent of the highest signal value, which also proves the high selectivity of the sensor. It is probably due to this selectivity, which is caused by preferential adsorption of Pb2+ and Cd2+ on the oxygen functional groups of GO in addition to the designed potential window which reduces the overlap of reduction signals of other metals.
The practical usefulness of sensor was proved with the help of the analysis of 42 real water samples, which were taken in various sources of Baghdad Governorate. The findings, summarized in Table 3 indicate an alarming trend of heavy metal pollution. Although there were no particles of either metal present in tap water samples (LOD), 73% of samples in the Tigris River and canals had quantifiable Pb2+ and Cd 2 +. Worryingly, all samples of industrial effluents were above the WHO standards and the mean results of Pb2+ and Cd2+ were 18.7 +4.5 2g/L and 12.3 +3.2 2g/L, respectively. These results are supported by latest environmental reports about uncontrolled industrial discharge in the area [19] and emphasize the necessity to have constant monitoring and regulation.
To prove the correctness and solidity of the approach, spike-recovery experiments were carried out on representative genuine samples. The recoveries were found to be between 96.3% and 103.7% at the three different concentrations (5, 15, and 30 μg/L) of Pb2+ and Cd2+ as indicated in Table 4 with the relative standard deviations (RSD) at all three levels being below 4.2%. These findings support the fact that there are no significant matrix effects and testify to the high accuracy and precision of the method even with complicated environmental samples.
The results of the sensor were also compared with the values of the inductively coupled plasma mass spectrometry (ICP-MS), which is a certified reference method in order to be verified independently. There was a good linear relationship (R2 = 0.994) and the Bland-Altman in Fig. 5 demonstrates that all the data are within the limits of agreement (95%). Table 5 gives the detailed comparison of the selected samples to further confirm that there is no systematic error and also to confirm that the two techniques match each other excellently.
The stability of operation and reproducibility of the sensor are essential to its applicability in the field. The GO–AuNC/SPCE had an excellent shelf life of 92.4 days according to Table 6, storage at 4 o C. In addition, inter-electrode re-producibility among ten self-manufactured sensors was fine with a minimal RSD of 4.7. This degree of uniformity is crucial to batch manufacturing and mass screening of the environment.
Last, practical workflow of the sensor including sample collection to results interpretation is schematically depicted in Fig. 6. The distribution of the hotspots of contamination follows Fig. 7 which is a geographic map of the sampling sites in Baghdad Governorate. In Fig. 8, we can see a photograph of the portable setup which is highlighted by its simplicity and its appropriate application by non-expert in a rural health center or in an environmental field station.
Taken together, these findings indicate that the GO-AuNC electrochemical sensor does not just have an analytical strength but it can also be applied in practice in terms of on-site monitoring of heavy metals in water resources of Iraq. Its ease of use, performance, and cost are superior to various techniques that labs are constrained by, thus making it an effective instrument of protecting a population in low-resource environments.
CONCLUSION
This paper has managed to clearly show how a novel electrochemical sensor incorporating a graphene oxide-gold nanocomposite (GO Gold nanocomposite) was rationally designed, fabricated and thoroughly validated to concurrently detect lead (Pb2+) and cadmium (Cd2+) in aqueous solutions at the ultrasensitive level. The sensor demonstrated outstanding analytical capabilities reaching sub-parts-per-billion (sub-ppb) detection limits (0.032 μg/L of Pb2+ and 0.041 μg/L of Cd2+) -values that are not only below the maximum allowable limits required by the World Health Organization but also exceed the sensitivity and practical sensitivities of many recently described nanomaterial-based sensors. The synergistic combination of the high surface area of graphene oxide and the high oxygen functionalities with the better electrocatalytic capabilities of gold nanoparticles not only made it possible to detect both metals in a single scan but it was also crucial because the well-resolved, interference-free detection was required in the real-world implementation. The accuracy of the method was rigorously verified based on the ICH Q2(R1) guidelines (recovery: 96.3 -103.7%), its precision (RSD < 4.2%), selectivity (against 100-fold excess of common ions) and stability (92.4% signal retention over 14 days). However, the best agreement with ICP-MS (R2=0.994 ) in the different water matrices of Iraqi waters, including Tigris River and industrial effluents, confirms its ability to be used as a field-portable substitute of a centralized laboratory analysis. The positive work of this sensor with 42 real water samples of the Baghdad Governorate showed the disturbing results of the pollution of Pb2+ and Cd2+ in the industrial discharge sites, and the concentration of these metals became much higher than the WHO safety levels more than six times. The results highlight a pressing need of easy to use, on-site monitoring instruments to enable environmental control and health intervention to the population living in the water-stressed areas of Iraq.
This work has a high value within the society more than its technical value. With its affordable (less than $5 per test), quick (less than 10 minutes), compact, and easy-to-use system, the GO--AuNC sensor enables local health departments, environmental departments and even primary care clinics to perform routine screenings of water quality without having to invest in costly infrastructure. This directly pushes Sustainable Development Goal 3 (Good Health and Well-being) forward by facilitating the evidence-based policymaking process by identifying some of the environmental health risks at an early stage.
Future directions will involve (i) creating a multiplexed variant that will be able to identify other priority metals (e.g., Hg2+, As3+), (ii) stabilizing the sensor with a smartphone-based readout system to transmit data in real-time, and (iii) to pilot a community-based monitoring network together with the Baghdad Health Directorate. In addition to this study being relevant to the nanoanalytical chemistry field, it offers a locally adaptable, scalable solution to an urgent societal health issue in Iraq and other resource-scarce environments.
CONFLICT OF INTEREST
The authors declare that there is no conflict of interests regarding the publication of this manuscript.
