Statistical optimization, soft computing prediction, mechanistic and empirical evaluation for fundamental appraisal of copper, lead and malachite green adsorption

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Abstract

This paper describes an efficient and low cost material for treatment of Cu2+, Pb2+ and malachite green from aquatic environments. Aerated Autoclave Concrete (AAC) was used as a low cost bed and modified by chitosan to synthesize of AACsingle bondCH composite. Then, it was analyzed by the Energy Dispersive X-ray spectroscopy (EDX), X-Ray Fluorescence (XRF), Field Emission Scanning Electron Microscopy (FE-SEM) and Fourier Transform Infrared spectrophotometry (FT-IR) analysis. The key factors influencing on the removal percentage among each run including, sample's pH, amounts of adsorbent and contact time were optimized by the Central Composite Design in Response Surface Methodology (CCD-RSM). Based on the obtained results, the optimum conditions for the removal of both Cu2+ and Pb2+ are pH 5.8, amounts of adsorbent: 14 mg and 58 min contact time. Also, for MG, its maximum removal percentage obtained at pH 9.7, 13 mg adsorbent and 55 min removal time. In addition, the variations of adsorptive behaviors were scrutinized by Adaptive Network-based Fuzzy Inference System (ANFIS) based on Sugeno model with focusing on removal percentage predictions. Also, to evaluate the adsorption mechanism, Dubinin–Radushkevich (D-R), Langmuir, Temkin, Freundlich (two parameter equations) and Sips, Khan and Toth isotherms (Three parameter equations) were appraised and the outcomes demonstrate that the adsorptive reaction of Pb2+, Cu2+ and MG governed by the Freundlich isotherm with the maximum adsorption capacities of 78.12, 56.82 and 833.33 mg g−1, correspondingly. Likewise, outputs of the D-R and Temkin isotherms show that the physiosorption process is the main interaction of analytes with AACsingle bondCH composite. The consequences of the kinetic modeling illustrated that the adsorptive reaction of Cu2+, Pb2+ and MG followed by the pseudo second order adsorption kinetic. The geometry kinetic computing depicted that the adsorption/desorption rates don't have any interfering during reaction process. The advantages such as high efficiency, low cost, reusability and green aspect, make AACsingle bondCH composite as a high performance adsorbent for decontamination of Pb2+, Cu2+ and MG from water resources.

Introduction

Environmental pollution is one of the main threaten of human and animal health in the century 21. By developing of technologies, application of heavy metals in different fields increases dramatically. Lead (Pb) has widespread applications in batteries, alloys, pigments and cable sheathing [[1], [2]–3]; Copper (Cu) is the most applicable heavy metal with wide applications in electrical wire, industrial machinery, alloys, medicine, kitchenware and etc. [4]. Copper is an important constituent of enzymes and proteins responsible for growth, cardiovascular integrity, lung elasticity, neovascularization, neuroendocrine function, and iron metabolism [5]. At very high concentrations, it causes gastrointestinal mucosal ulcerations and bleeding, acute hemolysis and hemoglobinuria, hepatic necrosis with jaundice, nephropathy with azotemia and oliguria, cardiotoxicity with hypotension and central-nervous-system (CNS) manifestations (e.g., dizziness, headache, convulsions, lethargy, stupor, and coma) [5]. Also, in adults, Pb causes problems of the peripheral and central nervous systems, kidneys (e.g., renal failure), and reproductive organs (e.g., decreased sperm count) [5]. Malachite Green (MG) is an organic cationic dye using as an antibacterial agent. Its presence in water samples absorbing sunlight and disturbing the photosynthesis process of seaweeds. Therefore, the concentration of dissolved oxygen reduces which could be cause to the death of aquatics [6, 7]. Due to the high toxicity of lead and copper ions at high levels and also carcinogen effect of MG and other organic dyes for humans; their removal from water samples is highly demanded [[8], [9], [10], [11], [12], [13], [14], [15], [16], [17], [18], [19], [20]–21]. Among the analytical procedures for treatment of pollutants from aquatic environments; adsorption technique has great attendance due to its unique specifications such as spread variety of adsorbents, reaction speediness, simplicity of the procedure, low cost and ability to use of the adsorbent by its recovery [[22], [23], [24], [25]–26]. Aerated autoclave concrete (AAC) is one of the lightweight materials which consist of silica, sand, portland cement type 2, lime, quartz and aluminum powder [27]. Since light-weight materials reduce the weight of the structures, these compounds become great significance in constructions; therefore, they are suitable to replace with traditional bricks. Due to their widespread application in Iran, their waste also increases and it is more necessary to consider them for reutilization according to the integrated solid waste management (ISWM) [28].

Chitosan is an amino polysaccharide which produced from chitin by alkali deacetylation [29]. It has antibacterial properties and used as a natural antimicrobial agent in the cosmetic pharmaceutical, agricultural, and food industries. Moreover, because of different amino and hydroxyl compounds in its composition, biocompatibility and non-toxicity, it has been utilized for refining contaminations form water resources [30, 31]. Herein, aerated autoclave concrete coated chitosan (AACsingle bondCH) composite has synthesized as a cost effective, high efficient and rapid adsorbent for the removal of Pb2+, Cu2+ and MG. AAC powder was used as a bed and chitosan coated on its surface to synthesize AACsingle bondCH composite. The hydrogen bonding interaction of chitosan (N−H and O−H) with Osingle bondH and Si-O-Si groups of AAC adsorbent is the main interaction between chitosan and AAC. The synthesized adsorbent was characterized by the Field Emission Scanning Electron Microscopy (FE-SEM), Fourier Transform Infrared spectrophotometry (FT-IR), X-Ray diffraction analysis (XRD), Energy Dispersive X-Ray spectroscopy (EDX) and Brunauer–Emmett–Teller (BET) analysis. The parameters such as sample's pH, amounts of adsorbent and contact time were thoroughly investigated by the Central Composite Design in Response Surface Methodology (CCD-RSM) and Sugeno method in Adaptive Network-based Fuzzy Inference System (ANFIS). As such, the adsorption isotherms including Temkin, Langmuir, Dubinin–Radushkevich (D-R) and Freundlich (two parameter equations), Sips, Toth and Khan (three parameter equations) were examined and interpreted. Finally, the adsorption kinetic models including Geometry, Boyd, Pseudo first and second orders, plus, Intra-particle kinetic models were studied thoroughly and discussed.

Section snippets

Material

The consumed materials for the synthesizing of adsorbent and the pollutant solutions are illustrated according to Fig. 1.

Instrument

In this study, the analytical instruments for pollutants detection, adsorbent characterization and experimental adjustment equipment are presented in Fig. 2.

Synthesize of AAC-CH composite

The proposed algorithm for the preparation of AAC powder and AACsingle bondCH composite, is depicted in Fig. 3.

Holistic view of research methodology

Roadmap of the current investigation including pollutant removal, CCD-RSM optimization systems, decision tree data

Characterization of AAC-CH composite

For determining the composition of the AAC powder, XRF analysis was performed. The main chemical compositions of AAC powder are SiO2 (52.4%), CaO (22.3%), Al2O3 (3.6%) and Fe2O3 (1.48%). The outcome of the FT-IR spectrophotometry of AAC and AACsingle bondCH composite are depicted in Fig. 5. The peaks at 2877 cm−1 and 2921 cm−1 could be attributed to the Csingle bondH symmetric and asymmetric stretching, correspondingly. The broad peak at 3400 cm−1 is related to the stretching vibration of Nsingle bondH and Osingle bondH groups of

Conclusion

The present paper describes the synthesize of AACsingle bondCH composite for the removal of Pb2+, Cu2+ and MG from water samples. AAC wastes were treated and then coated by chitosan to synthesize of AACsingle bondCH composite. It was then characterized by the FT-IR spectrophotometry, FE-SEM images and EDX analysis. Response surface methodology based on the central composite design (RSM-CCD) was used to find the optimum condition for the removal of Pb2+, Cu2+ and MG. Moreover, ANFIS and RT soft computing algorithm

CRediT authorship contribution statement

Mohammad Eftekhari: Supervision, Conceptualization, Methodology, Resources, Data curation, Writing – original draft, Validation, Project administration, Funding acquisition. Mohammad Gheibi: Conceptualization, Methodology, Software, Writing – original draft, Validation, Formal analysis. Hossein Azizi-Toupkanloo: Investigation, Resources, Project administration. Zahra Hossein-Abadi: Investigation, Data curation. Majeda Khraisheh: Investigation, Writing – review & editing. Amir Mohammad

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: Authors declared that they have no conflict of interest

Acknowledgement

Authors wish to thanks the University of Neyshabur for its financial support (Grant number: 12523).

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