Available online at http://journals.usamvcluj.ro/index.php/promediu ProEnvironment ProEnvironment 8 (2015) 476 - 480 Original Article Biosorption of Inorganic Mercury in Aqueous Solution by some Aromatic Plants VEREȘTIUC Paul Cristinel1, Oana Maria TUCALIUC1*, Gheorghe NEMȚOI2 1Al.I.Cuza 2Al.I. University of Iasi, Faculty of Geography and Geology, Carol I Blvd., no. 20 A, 700505 Iasi, Romania Cuza University of Iasi, Faculty of Chemistry, Carol I Blvd., no. 11, 700506 Iasi, Romania Received 12 February 2015; received and revised form 20 June 2015; accepted 28 June 2015 Available online 1 September 2015 Abstract Contamination of ecosystems with heavy metals is one of the major problems all over the world. Most of these metals are present in the environment as a consequence of anthropogenic activities. Aromatic and medicinal plants have an increasing economic importance and are used with success in pharmaceutic and food industry. Products based on natural substances enjoy an increasing value. Some aromatic plants produce specific secondary metabolites, which can detoxify some of toxic metals. Five aromatic plants (Salvia officinalis, Petroselium crispum, Artemisia dracunculus, Mentha chrispa, Origanum vulgare) commonly known as sage, parsley, tarragon, mint and oregano were used to remove inorganic mercury from aqueous solution. A sorbent was obtained from each plant leafs. Experiments were carried out to determine the adsorption efficiency at a known pH and at a 180 seconds preconcentration time using linear sweep voltammetry. The results in this study demonstrated that the cathodic discharge of mercury ions from mercury (II) aqueous solutions can be pointed out by a relevant current pick, whose height, is dependent on the quantity of plants. The study suggest that some of the plants hold great potential to be an effective biosorbent for removal of mercury and other heavy metals from contaminated waters with good efficiency and low cost. Keywords: mercury (II), aromatic plants, biosorption, linear sweep voltammetry. 1. Introduction Mercury is and its compounds have been in use for several millennia and the applications range broadly from cosmetics, medicinal treatments, dentistry, paints to electrical apparatus and batteries. Mercury is liquid at room temperature and mercury compounds are toxic, volatile and readily dispersed through the atmosphere [6]. Mercury is widely considered to be among the highest priority environmental pollutants of continuing concern on the global scale [16]. This metal is among the most highly bioconcentrated trace metals in the human food chain, and many national and international organizations have targeted mercury for emission control [9]. The term of heavy metals defines metals with specific weight higher than 5 g/cm3 [4]. Mercury has natural sources such as volcanic activity, soil and rock weathering and evaporation from oceans. Between 70-80% of the Hg resealed in the environment comes from anthropogenic sources such as metal smelting, mining, cement production, waste incineration and other industries [11]. * Corresponding author. Tel: +40-755-156581 Fax: +40-332-881671 e-mail: [email protected] 476 VEREȘTIUC Paul Cristinel et al./ProEnvironment 8(2015) 476 - 480 It is generally accepted that the major risks to human health arise from the neurotoxic effects of mercury: memory disturbance, tremors, deafness, respiratory distress, renal failure, all of them are reunited as symptoms of Minamata disease [8]. To grow and complete the life cycle, plants must aquire not only macronutrients (N, P, K, S, Ca), but also essential micronutrients as Fe, Zn, Mn, Ni or Cu. Accumulation of these micronutrients does not exceed their metabolic needs. In contrast, some metal hyperaccumulator plants can accumulate exceptionally high amounts of nonessential metals (in the thousands of ppm) [15]. Salvia officinalis (sage) has been reported to have a wide range of biological activities, such antioxidant, antibacterial, hypoglycemic and antiinflammatory properties [2]. Petroselium crispum (parsley) has been claimed to be antimicrobial, antiseptic, astringent, gastrotonic, antispasmodic, usually employed as food flavour [5]. Artemisia dracunculus (tarragon) has a culinary and traditional medicinally use, known to improve a malfunctioning digestive system [13]. Mentha chrispa (mint) posseses antioxidative, antimicrobial and hepatoprotective activity due to phenolic components [7]. Origanum vulgare species are a rich source of carvacrol, a component of particular biological importance: it is known for its antibacterial and antifungal activities, antispasmodic effects and radical scavenging effect [3]. Good capacity of mercury adsorption was observed in other studies for Coriandrum sativum [10], Ricinus communis [1] or Bambusoideae subfamily [12]. The aim of the present work was to investigate the capacity of mercury adsorption by five different aromatic plants using linear sweep voltammetry. 2. Material and Method For the study, dried leafs of five aromatic plants (Salvia officinalis, Petroselium crispum, Artemisia dracunculus, Mentha chrispa, Origanum vulgare) commercially used were purchased and milled afterwards. A quantity (P) of 2 mg, 4 mg, 6 mg, 8 mg, 10 mg, 12 mg and 14 mg was used in order to determine the capacity of mercury adsorption. For this, an aqueous solution was obtained using tap water with a pH value of 7.79 to which was added 4 mL of HgCl2 with a concentration of 2.736 x 10-4 M. Each quantity of leafs was introduced into 30 mL of aqueous solution for a time of 30 minutes at a temperature of 25°Celsius. Further, the vegetal material was separated from the aqueous solution using filter paper. The aqueous solutions obtained after separation was investigated using linear sweep voltammetry. The linear sweep voltammetry was performed using the electrochimical combine VoltaLab 32. The satureted calomel electrode was used as the reference electrode, while the platinum wire was used as auxiliar electrode and as working electrode was utlized a carbon paste electrode. The working carbon paste electrode had an adsorption surface of 19.63·10-2 cm2. 3. Results and Discussions Studying the electrochemical behavior of mercuric ion it was noticed that the different current peak of the plant sorbent shown in Figs 1 - 5, mercury adsorption is directly proportional with the plant quantity introduced in the tap water, at a concentration of 2.736 x 10-4 M. It also proves that the processes that are taking place are slow and quasi-irreversible. Different accumulation potentials were tested with the aim to find the best reduction potential for mercury (II). Potentials from 500 mV to -500 mV were applied. The peak currents increases when reduction potentials were changed from 500 mV to 200 mV. The peak current values of the sorbent were stabilized within the potential range of 50 mV and 150 mV. Salts of divalent mercury are readily soluble in water, and, by this, highly toxic. The extreme high affinity of mercury (II) to sulfhydryl groups of amino acids as cysteine and methionine in enzymes explains its high toxicity [14]. The preconcentration time was established after testing the preconcentration process at 30 s, 60 s, 90 s, 120 s, 150 s and 180 s. after this time, no significant variation was noticed. For a better accuracy of the result a precocentration of 180 s was used for the determinations. The biosorption efficiency of mercury (II) increased rapidly during the first 5 minutes and remained nearly constant after 30 minutes. The mercury sorption was relatively fast suggesting that the system reached the final equilibrium plateau within 30 minutes. The increase of contact time beyond 30 minutes has no significant effect on biosorption efficiency. Most of mercury sorption was during the first 10 minutes. Other parameters such as surface charge capacity, composition of plant sorbent, metal affinity and experimental conditions play a role in the adsorption mechanism. Figs. 1 - 5 show the current peak of mercury (II) removal as a function of initial concentration with 2 mg to 14 mg of plant sorbent (pH 7.79 and 30 minutes). 477 VEREȘTIUC Paul Cristinel et al./ProEnvironment 8(2015) 476 - 480 Figure 1. Linear cathodic voltammograms of mercury adsorption by oregano at different quantity of plants Figure 2. Linear cathodic voltammograms of mercury adsorption by minth at different quantity of plants Figure 3. Linear cathodic voltammograms of mercury adsorption by sage at different quantity of plants Figure 4. Linear cathodic voltammograms of mercury adsorption by parsley at different quantity of plants Figure 5. Linear cathodic voltammograms of mercury adsorption by tarragon at different quantity of plants Figure 6. Adsorption of aromatic plants at different quantity of plants 478 VEREȘTIUC Paul Cristinel et al./ProEnvironment 8(2015) 476 - 480 This electrochemical behavior of plant sorbent leads to the following dependence equations for the cathodic peaks, as a expresion of the discharge of mercuric ion on the carbon paste electrode, in all investigation plants: 1. Oregano: I (mA) = -0.00297 + 0.1037 P – 1.03287 P2 (R = 0.99465); 2. Minth: I (mA) = -0.0105 + 2.11661 P – 0.23882 P2 (R = 0.99692); 3. Sage: I (mA) = -0.00713 + 0.26413 P – 2.96068 P2 (R = 0.97652); 4. Parsley: I (mA) = -0.0121 + 0.24772 P – 0.2838 P2 (R = 0.99936); 5. Tarragon: I (mA) = -0.00617 + 0.21172 P – 1.99687 P2 (R = 0.99085); where P is the quantity of plant sorbent in mg from 34 mL aqueous solution. 4. Conclusions In this study it was demonstrated that the cathodic discharge of mercury ions from mercury (II) aqueous solutions can be pointed out by a relevant current pick, whose height, is dependent on the quantity of plants. Best results of mercury adsorption were obtained during the first 10 minutes while the increase of contact time beyond 30 minutes has no significant effect on biosorption efficiency. The current peak of the plant sorbent in mercury adsorption was directly proportional with the plant quantity introduced in the tap water. The cathodic discharge of mercury of the mercury ion on tap water it is a slow process, quasiireversible. The best results in mercury adsorption was given in ther following order: oregano > tarragon > sage > minth > parsley. Furthermore, it can be concluded that oregano leveas hold great potential to be an effective biosorbent for removal of mercury and other heavy metals from contaminanted waters with good eficiency and low cost. Acknowlegments. 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