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Air pollution Analysis: Nickel paste on Multi-walled carbon nanotube= s as novel adsorbent for the mercury= removal from air

 =

 Ali Ebrahimi<= b>a,* b

a,* Occupational Health Engineering Department, School of Public Health, Qom University of Medical Sciences, Qom, Iran.

b Environmental Engineering, Faculty of Natural Resources, Islam= ic Azad University, Bandar Abbas Branch, Bandar Abbas, Iran =

Email: a_ebrahimi2010@yahoo.com

 = ;

Abstract

Mercury as a hazardous material can be released in the air and caused renal failure= and CNS problems in humans. In this study, mercury vapor removed from air based= on nickel-coated on multi-walled carbon nanotubes (Ni-MWCNTs) as a novel sorbe= nt at room temperature. By procedure, the amalgamation of mercury with Ni-MWCN= Ts was achieved by the solid-gas phase removal method (SGPR). In bench-scale setup, the mercury vapor generated and mixed with purified air with electro= air cleaner and moved to sorbent at  optimized flow rate. After thermal desorption of Ni-MWCNTs at 200 oC, the mercury vapor flowed= to quartz glass cell with argon gas and determined by cold vapor atomic absorp= tion spectrometer technique (CV-AAS). In optimized conditions, 25 mg of Ni-MWCNTs and MWCNTs with different size from 30-100 nm was used and the adsorption capacity of sorbents was obtained 194 mg g-1 and 64 mg g-1, respectively. The efficient recovery was obtained at optimized conditions s= uch as, the temperature of 25-40 and flow rate of 200 mL min-1.  Due to results, the surface of Ni-MWCNTs had good potential for the removal= of mercury vapor from the air and can be used as a low cost and efficient sorb= ent in the industrial workplace.

 

Keywords: Mercury, Rem= oval from air, Nickel coated on multi-walled carbon nanotubes, Adsorption, Solid-gas phase removal.

 

 

1.  Introduction

     Mercury was ranked as a hazardous material for human health and animals such black fish and extra concentration cause dangers disease in human body [1,2]. Mercury is a toxic element and has no essential biological function in human body and normal r= ange was reported less than 20 µg L−1 and 2 µg L−1 in urine and blood serum, respectively by ACGIH. Organic and inorganic mercury occurs in= fishes, foods, vegetables, waters and air [3]. It is emitted to the atmosphere from= chlor-alkali factory, sea, chemical process, coal, oil combustion for energy generation,= and metal mining, The contribution of industrial sources for mercury and other = heavy metals emissions to the atmosphere, rivers and fish and humans [4]. Human exposure to mercury evaluated and studied in occupational and environmental= health [5]. Mercury generated from chemicals, petrochemical and electrical industr= ies [6].  The mercury exposure caused m= any health problems in human body such as, central nervous system defects, erythrism, arrhythmias, cardiomyopathies, and kidney damage. Necrotizing bronchitis and pneumonitis arising from inhalation of mercury vapor can res= ult in respiratory failure [5, 6]. Mercury is listed and suggested as one of the hazardous air pollutants in the 1990 and recently many methods was used for mercury removal from air [7]. The air sampling and analysis methods was used for mercury determination by the national institute for occupational safety= and health (NIOSH) and the occupational safety and health administration (OSHA), respectively(NIOSH 6009). The main disadvantages of these methods related t= o interference by other metal compounds and organic mercury in air.  the sample tube be The fragile of sample= tube, low adsorption capacity, impurities and contamination of reagents used for sample preparation, the use of nitric acid and hydrochloric acid, as well as being time consuming, the mercury loss during sample preparation, operator skills and  the costs of solid sorb= ent tubes caused to consider as  a weak procedure[8, 9]. Many Nano carbon compound such as carbon nanotubes (MWCNTs, SWCNTs), graphene and mesoporous silica nanoparticles (MSN) was syntheses a= nd used as a sorbent for removal of mercury from air. Carbon nanotubes are uni= que wall porous structures with nanometer diameter and can be simply removed mercury from air with two type's single walled carbon nanotubes (SWNTs) and multiple walled carbon nanotubes (MWNTs) [16]. MWCNT and SWCNT were used in many published papers for mercury removal from air/gas. Adsorption of mercury was achieved by montmorilloni= te powder modified with Copper Compounds or amorphous of MoS3 pasted on Ti= O2 was used for removal metals from gas/air . Also, the bimetallic sorbents such as P= d–Fe and catalytic compounds such as Ce–Mn/TiO2 applied for Hg0<= /sup> removal in air [10-15]. In fact, CNTs with chemical and physical properties have good potentially in m= any applications such as, nanotechnology, electronics, optics, water, chemistry, environment and other fields of materials science [16-20]. Low diameter (nm= ), low weight, thermal conductivity and high surface area, thermal resistance, high tensile strength and a very high Young modulus caused to introduce as novel adsorbent in many science [21-22]. Also, these compounds also have be= en used for absorb the gases and metal cations and volatile organic compounds = [23-27]. The carbon nanotubes have a good repeatability in high temperature, So, CNTs introduce a favorite sorbent for mercury removal from air by thermal desorp= tion method [28, 29], Also, the health effect of  exposure to solvents, acids and other ch= emical methods were reduced by proposed method. Recently, different instruments coupled with techniques was reported for mercury analysis by researchers, a= ctivated carbon from mixed recyclable waste modified by phosphonium-based ionic liquid (IL-ACMRW) based on  Induct= ively Coupled Plasma- mass spectroscopy (ICP-Ms) was used for mercury removal from wastewater.  Inductively coupled plasma atomic emission spectroscopy (ICP OES), high-performance liquid chrom= atography coupled hydride generation atomic absorption spectrometry (HPLC-HG-AAS), hydride generation atomic absorption spectrometry (HG-AAS), hydride generation atomic absorption spectrometry coupled mercury concentration (HG-AAS-MC3000). In this work, Ni-MWCNTs and MWCNTs was removed the mercury vapor from air due to their unique physicochemical properties.  Strong chemical i= nteractions between Ni and Hgo (Hg→Ni-MWCNTs) caused to increase remov= al efficiency of sorbent by SGPR. The reusabl= e of Ni-MWCNTs can be considered as a cost effective sorbent. =

 =

2.&n= bsp; Experimental<= /span>

2.1.=   Material and Methods

         All reagents s= uch as, Sodium borohydride, nitric acid, sodium hydroxide and hydrochloric acid were prepared from Sigma Aldrich. Mercury standard solutions were prepared = from a stock solution of 1000 mg L-1 in 1% ultra-pure nitric acid. Working standard solutions were freshly prepared by dilution of stock and intermediate standards. Sodium borohydride (NaBH4) prepared fres= h daily. 3.0 g of NaBH4 and 3.0 g of sodium hydroxide (NaOH) were mixed and diluted = by deionized water (DW) up to 500mL. Deionized water obtained from a water purification system (Millipore, Bedford, MA, USA) was used for preparing all solutions. All containers (quartz crucibles, plastic tubes) were cleaned wi= th detergent and treated successively by the hydrochloric acid and rinsed with deionized water. Argon was used as the pure gas (99.99%).  The present research is an experimental study and it includes stages such as preparation of  the various concentrations of mercury vapor, adsorption of mercury vapor in various concentration, time, temperature optimized as well as retention time of adsorbed mercury by multi-walled carbon nanotubes. The atomic absorption spectrometer (GBC) Model (AAS–932 Puls) with cold vapor technique (CV-AAS/H= G3000) has been used for the analysis of samples. Instrumental parameters for cold vapor atomic absorption spectrometry are shown in Table 1.  The mercury concentrations were prepared= from 1 µgL-1 to 50 µgL-1. The Ni-MWCNTs (25 mg) as solid p= hase was used and placed in a glass tube with length of 5 cm and the internal and external diameters of 5 and 8 mm respectively. Then, end-capping with some = silica /cotton was performed to prevention of humidity. MWCNTs were provided by Na= no department of RIPI, Tehran. Also, all solutions and materials were purchased from Merck, Germany.

Table 1. Conditions of cold vapor atomic absorption spectrometry (CV-AAS) for mercury

Parameters                                               =                                     Value   

5 mA

253.7 nm

0.5 nm

Cold vapor=

HCL

400 k Pa

100 mL/min

 35 mL/min

Lamp Current

Wavelength<= /p>

Band pass

Flame Conditions

Lamp

Argon gas pressure=

Gas flow to the mixer block

Gas flow to the separator

 

 

 

 

 

2.2. Synthesis of nickel coated on MWCNTs

The Ni-MWCNTs= has prepared as follows, 2.0 g of  the = pure MWCNTs was added to 50 mL of DW with 0.25 g of Sodium sulfosuccinate esters ( NaO3SCH(CO= 2R')CH2CO2R )as a surfactant by low heating at 300 rpm stirring speed. The nickel nitrate (0.5 g) was added to the Final solution without heat in 200 rpm stirring speed. Then, ammonia solution (2 mL) was added to solution and dil= uted with DW up to 200 mL with stirring in 20 min at 300 rpm speed. Then finally= , 10 mL of formalin slowly was added for five minutes as a reducing agent. The s= ynthesis of Ni-MWCNTs nanoparticles was obtained by increasing the speed of Stirring after addition formalin for 10 min (800 rpm). The extra  formalin and ammonia on Ni-MWCNTs clean= ed by DW washing after filtration by Whatman filter. In addition, oxidation of th= e Ni-MWCNTs nanoparticles was prevented by washing with Ethanol.

2.3. Experimental Procedure   

      In bench scale set up, the air was pu= rified with electro air cleaner (EAC, Canada, model= EAHEPA600M-3) by HEPA. The HEPA = act for efficient removing particles under 300 nm (99.97%) from air. Then, the = pure air of EAC = passed thro= ugh polyethylene tubes and entered to polyethylene bag (1 Li) by a SKC pump. All of the gas lines were PE tub= es and those that enter to PE bag were covered with heating jackets capable of controlling the temperature at 50 °C to prevent water vapor and mercury vap= or from condensing.  In SGPR, trace of elemental mer= cury vapor in air was prepared by aqueous standard solution of mercury (1-50 µgL= -1). The aqueous standard solutions entered to hydride generator system and merc= ury vapor generated in a continuous flow rate. The system was designed by a peristaltic pump that can be pumped standard solutions of mercury, tin chlo= ride as reducing agent and ionized water into a mixer continuously. Peristaltic = pump rotation rate was 1.5 rounds per second or 90 rpm. The solution mixed thoro= ughly in reaction tube and then pushed into a liquid–gas separator where the merc= ury vapor is separated from the liquid using an inert carrier gas. The mercury vapor mixed with pure air and flowed to Ni-MWCNT by flow rate 100-300 ml mi= n-1. After adsorption mercury by Ni-MWCNTs, the remained air stored in polyethyl= ene bag 1(1 L). The air into air bag was determined by CV-AAS and MC3000 (gold trap). After thermal desorption of MWCNT, the mercury vapor flowed with Ar = gas and stored in another bag (bag 2, 1L) and mercury determined by CV-AAS and = MC 3000.  The pilot plan for mercury removal from air was shown in Figure= 1.

Fig. 1. Scheme of pilot plan for mercury removal fr= om air

3. Results and Discussion=

3.1. Scanning electron microscopy images from c= arbon nanotubes

The scanning electron microscopy (SEM) and Transmis= sion electron microscopy (TEM) images of MWCNT and Ni-MWCNTs was sho= wn in figures 2 and 3, respectively. Elemental analysis conditions showed that Ni-MWCNTs included 8% nickel and 90% carbon. Mercury was removed by sorbent 0.55% by Ni-MWCNTs (Table 2).

 =

                      Fig. 2. SEM (L) and TEM (R) = images of multi-walled carbon nanotubes

 

Fig. 3. SEM (L) and TEM (R) = images of Nickel coated on multi-walled carbon nanotubes<= span style=3D'font-family:"Times New Roman","serif";mso-ascii-theme-font:major-b= idi; mso-fareast-font-family:Calibri;mso-hansi-theme-font:major-bidi;mso-bidi-th= eme-font: major-bidi'>

Tab= le 2. Ene= rgy Dispersive X-Ray Analysis of = Ni-MWCNTs (EDX) for mercury removal=

Elt

Line

Int

Error

K

Kr

W%

A%

ZAF

Ox%

Pk/Bg

<= b>Class

LConf

HConf

Cat#

C<= /b>

Ka

676.1

80.3865

0.4213

0.2945

48.21

90.22

0.6107

0.00

37.86

47.66

48.76

0.00

Ni

La

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>1269.7

6.5990

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.4792

0.3350

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>41.14

8.57

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.8142

0.00

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>26.05

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>40.79

41.48

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.00

Au=

La

7.0

0.5642

0.0839

0.0586

9.29

1.06

0.6307

0.00

2.41

8.25

10.34

0.00

Hg

Ma

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>47.1

6.5990

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.0157

0.0110

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>1.36

0.55

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.8077

0.00

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>3.20

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>1.30

1.42

<= span style=3D'font-size:9.0pt;line-height:200%;font-family:"Times New Roman","= serif"; mso-ascii-theme-font:major-bidi;mso-hansi-theme-font:major-bidi;mso-bidi-= theme-font: major-bidi'>0.00

 

3.= 2: Adsorption efficiency for different amounts = of MWCNTs

The adsorption efficiency with 25 mg of Ni-MWCNTs and MWCNTs was examined for 0.01-0.1 = mg of mercury concentration by SGPR. According to the results, the adsorption efficiency for Ni-MWCN= Ts was more than 95% as compared to MWCNTs (less than 70%). Also the RSD had diffe= rent value from 5 to 8%. The results showed that the good recoveries for mercury removal by two sorbents were achieved in low and high mercury concentration (Table 3).

Table 3. Recovery o= f adsorption for different concentration of mercury from low to high rang= e   (n=3D10; Mean SD of results ± 0.0032)

25 mg of NI-MWCNTs= =

(  Recovery=

RSD%=

Found  desorption

Pilot concentratio= ns(mg)=

94.4

97.5=

95.3

97.4

97.6

0.67=

0.00944

0.01

0.02=

0.03=

0.05

0.1

0.52

0.0195<= /span>

0.73

0.0286<= /span>

0.81

0.0487<= /span>

0.76=

0.0976

25 mg of MWCNTs=

65.4

74.0

68.6

77.6

68.3

0.74=

0.00654

0.01=

0.02

0.03

0.05

0.1=

0.63

0.0148<= /span>

0.73

0.0206<= /span>

0.54

0.0388<= /span>

0.59=

0.0683

3.3: Adsorption capacity of Ni- MWCNTs and MWCNTs

 In batch system, 10 mg L-1 of mercury standard solution (Merck) selected and injected in closed special glass (CSG) after put into Ni- MWCNTs and MWCNTs= as sorbents in CSG. After heating, the temperature increased up to 80 OC for 10 min. The mercury was vapored and absorbed on sorbents. The results showed us, the absor= ption capacity (AC) of Ni- MWCNTs and MWCNTs for mercury removal was obtaine= d 194.7 mg g-1 and 64.4 mg g-1, respectively (Fig. 4). In temperature of 50oC for 10 min, AC was decreased about 8% but af= ter 20 min AC was similar to proposed procedure.

 

Fig. 4: The absorption capacity (AC) of mercury va= por in Ni- MWCNTs and MWCNTs (n=3D10).

 

3.= 4: Determine the optimum time and temperature for desorption

 

For optimization of temperature, the rate of desorption at different temperatur= es was studied by SGPR. The maximum of desorption rate= s on the Ni-MWCNTs was achieved in 160-250°C. So, 200°C was selected as an optim= um temperature for desorption point by Ni-MWCNT. Based on the optimum temperat= ure and after several experiments, the results showed that the best time for desorption high efficiency was about 2.33 min with average desorption effic= iency equals to 94.5 - 98.2% by peak area mode (Fig. 5).

 

Fig. 5. The effect of time d= esorption of Ni-MWCNTs and MWCNTs by SGPR (n=3D10).=

 

3.5. Adsorption/desorption efficiency

 Removal efficiency and linear regression between the mean values of the mass adsorption and desorption by Ni-MWCNTs = and MWCNTs have been shown in Figure 6. The mercury concentration (0.02-0.1 mg = L-1) was used for calculating of removal efficiency by proposed procedure. Based= on Figure 6 the removal efficiency of Ni-MWCNTs (25 mg) was more than MWCNTs (= 25 mg) as compared to adsorption/desorption procedure for mercury removal from air by 200= ml min-1.

            Fig. 6. The linear regression of adsorption / desorption for Ni-MWCNTs and MWCNTs

3.6. Repeatability and retention time

The retention time evaluated for 0.02-0.1 mg of mercury concentration for Ni-MWCNTs and MWCNTs in different temperature. For calculation of retention time, the two ends of sorbents tube with Ni-MWCNTs and MWCNTs were kept at zero 0°C and 25°C.=  After various times, carbon nanotubes we= re desorbed in optimum conditions (200°C and 10 min) and then, this procedure followed in different times (1-5 weeks). The results showed us, the main ma= ss of mercury in sorbent tubes was similar to primary mercury concentration af= ter 3 weeks by desorption procedures (0°C). But, in room temperature, only Ni-MWCNTs were stable mass after 1 week. So, Ni-MWCNTs is suitable sorbent for mercury removal from air  and saving in room temperature. The adsorption / desorption  procedure = for Ni-MWCNTs and MWCNTs was repeated based on  proposed method and  after  flashing point , 25 and 27 usage times <= span style=3D'mso-spacerun:yes'> was achieved as an optimum point for Ni-= MWCNTs and MWCNTs, respectively.

 

3.7.=   Discussions  <= /span>

Acc= ording to the results, Ni-MWCNTs were able to absorb mercury from air by SGPR. The atomic absorption spectrometer (GBC) Model (AAS–932 Puls) with cold vapor technique (HG3000) was used for determination of mercury in air, liquid and gas. Previous studies have been researched to attract mercu= ry vapor in gas/air [23-27]. In this study, the Ni-= MWCNTs with average diameter of (less than 100 nm) were used to form a stationary phase (sorbent) of gla= ss tubes containing a length of 10 cm, internal diameter of 4cm and external diameter of 6 cm [8, 9]. Shirkhanlo= o et al. used silver nanoparticles in glassy balls. They showed that silver nanoparticles (AgNPs) had good removal efficiency for mercury from air but = it was more expensive as compared to our study. Also silver nanoparticles can = be oxidizing by air, so storage is very hard in room temperature as compared to <= span style=3D'font-size:12.0pt;line-height:200%;font-family:"Times New Roman","s= erif"; mso-ascii-theme-font:major-bidi;mso-fareast-font-family:Calibri;mso-hansi-t= heme-font: major-bidi;mso-bidi-theme-font:major-bidi'>Ni-MWCNTs [7].  The average absorption rate and = absorption capacity (AC) of mercury mass in different concentrations was increased by increasing the mass of nanotubes. In this study, the adsorption capacity of mercury for the Ni-MWCNTs (Ni→Hg) was obtained 194 mg g-1 which was higher than other published methods (less than 170 mg g-1) and MWCNTs (64 mg g-1)<= span style=3D'font-size:12.0pt;line-height:200%;font-family:"Times New Roman","s= erif"; mso-ascii-theme-font:major-bidi;mso-fareast-font-family:SimSun;mso-hansi-th= eme-font: major-bidi;mso-bidi-theme-font:major-bidi;mso-font-kerning:1.0pt;mso-fareas= t-language: ZH-CN;mso-bidi-language:FA;mso-bidi-font-weight:bold'>. This amount is more t= han the adsorption capacity of adsorptions such as activated carbon. [30]. According to results in optimized conditions, it seems that the factors such as, concentration of mercury in = air, the mass of sorbents, air flow rate, surface area, temperature, and type of= the adsorbent effected on the adsorption efficiency of  mercury from air  up to 80%. Also, the other parameters su= ch as layout of the sorbent tube, length, diameter, O2 and H2O in air, had low affected less than 20%. The  optimum  point  for  <= /span>concentration  and  temperature  desorption  was  <= /span>obtained 1-50 µgL-1 and  200 °C, respectively. In other studies that designed on the activated carbon, graph= ene and carbon nanotubes, similar to proposed method [31, 32]. After one month,= the retention time of mercury on Ni-MWCNTs, at temperature of 0°C was obtained = 98.8% ± 1.05 was near to initial concentration amount. Many papers were used CNTs sorbents for removal mercury from air. The

 

4. Conclusions

In present work, a novel sorbent based on Ni-MWCNTs= was used for mercury removal from air by SGPR. By proposed procedure, the Ni-MW= CNTs were synthesized and put on quartz glass cell. By labora= tory bench scale set up, mercury generated in chamber and flowed to sorbent and = by amalgamation procedure mercury removed from artificial pure air.  After optimizing conditions, the adsorpt= ion and desorption point for Ni-MWCNTs was obtained 20-45oC and 200<= sup>oC, respectively. The results showed us, the efficiency of mercury removal from= air was more than 95% and less than 65% for Ni-MWCNTs a= nd MWCNTs, respectively. The removal recovery was decreased less than 5 = % in present of O2 and H2O by SGPR method. So, the Ni-MWCN= Ts introduced as novel sorbent with high efficiency for mercury removal from a= ir in flow rate of 200 mL min-1 which was acted by physical and chemical adsorption mechanism.

 

5. Acknowledgements

This study was supported by Iran= ian petroleum industry health research institute and RIPI.

 

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                           Research Art= icle, Issue xxx

 

&nbs= p;

Analytical Methods in Environmental Chemistry Journal                   =           

 

 

 

 

à= Corresponding Author: Ali Ebrahimi

E-mail addresses: Ali.Ebrahimi.ohe@gmail.com<= /p>

https://doi.org/10.xxxx/j.amecj.2018.xx.xxx

 

 

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