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Proceedings of International Symposium on Advances in Metallurgy & Materials (ISAMM’19) September 24-26, 2019 Department of Metallurgy and Materials Engineering Pakistan Institute of Engineering and Applied Sciences Islamabad

International Symposium on Advances in Metallurgy & Materials

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Page 1: International Symposium on Advances in Metallurgy & Materials

Proceedings of

International Symposium on

Advances in Metallurgy & Materials

(ISAMM’19)

September 24-26, 2019

Department of Metallurgy and Materials Engineering

Pakistan Institute of Engineering and Applied Sciences

Islamabad

Page 2: International Symposium on Advances in Metallurgy & Materials

ii

Patron Prof. Dr. Nasir Majid Mirza Rector PIEAS

Organizing Committee

Chief Organizer:

Prof. Dr. Mirza Jamil Ahmad

Secretary

Dr. Zafar Iqbal

Members:

Prof. Dr. Gul Bali shah

Prof. Dr. Hasan Bin Awais

Prof. Dr. Mazhar Mehmood

Dr. Muhammad Tauseef Tanvir

Dr. Fahad Ali

Ms. Tayyaba Ghani

Dr. Syed Mujtaba-ul-Hassan

Dr. Naeem Ul Haq Tariq

Dr. Rub Nawaz Shahid

Hafiz Shoaib Mehboob

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International Speakers

Prof. Norani Muti Mohamed

Centre of Innovative Nanostructures and Nanodevices

Universiti Teknologi PETRONAS (UTP), Malaysia

Prof. Yunfa Chen

Deputy Director

Institute of Processing Engineering, Chinese Academy of

Sciences, China

Prof. Massimo F. Bertino

Associate Director

Nanocharacterization Core Facility

Virginia Commonwealth University, USA

Prof. Abbas Saeed Hakeem

King Fahd University of Petroleum & Minerals

Saudi Arabia

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Contents Synthesis and Release of Ibuprofen Loaded Zein/Gelatin Nanofiber Scaffolds for Potential Application in

Burn Wounds .............................................................................................................................................. 1

An Approach towards the Surface Treatment of Natural Fiber to Improve Its Compatibility with Polymer

Matrix ......................................................................................................................................................... 6

Lead Ion Removal Using AACH Derived Alumina ...................................................................................... 15

Synthesis, Characterization, and Antimicrobial Properties of Al-Cu-Fe-B Quasicrystals .......................... 20

Page 5: International Symposium on Advances in Metallurgy & Materials

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Synthesis and Release of Ibuprofen Loaded Zein/Gelatin Nanofiber

Scaffolds for Potential Application in Burn Wounds

Murk Saleem1,2, Umaima Saleem1, Abdul Qadir Ansari1,2, Farooq Ahmed2, Zeeshan Khatri1,3*, Ick

Soo Kim2

1Center of Excellence in Nanotechnology and Materials, Mehran University of Engineering and

Technology, Jamshoro 76060, Pakistan 2Department of Biomedical Engineering, Mehran University of Engineering and Technology, Jamshoro-

76060, Pakistan 3Nano Fusion Technology Research Lab, Division of Frontier Fibers, Institute for Fiber Engineering

(IFES), Interdisciplinary Cluster for Cutting Edge Research (ICCER), Shinshu University, 3-15-1, Tokida,

Ueda, Nagano 386-8567, Japan

Abstract: To promote healing of damaged tissues due to burn injuries, antimicrobial fence can be helpful and

shall expedite the recovery. Nanotechnology based fibrous mats are being widely studied for their functionality as

drug carriers. Preparation of the electrospun polymeric mats of antimicrobials agents is upraised in this article.

Nano fibrous mats from pure zein, pure gelatin and their blend with Ibuprofen were prepared using co-electrospinning

method. The resulting electrospun nanofibrous mats are preferred in wound healing materials due to their effect of

exudation and thus in keeping the wound dry and protected from microbial activity. Beside as protecting

antimicrobial layer the prepared mats also serve as a drug carrier. This article also details the drug release from

these carrier mats; moreover it also provides characteristic details of fibrous mats through standard methods of

characterization including uv-vis. SEM and FTIR.

Introduction

Intact of person’s epidermis is desirable for protection against infection, protection of body substance

homeostasis and thermoregulation. Burn injury results in damage of the skin barrier and enables bacterial

infection.[1]. Currently, to prevent wound infection extensive studies are carried on the use of

biocompatible nanomaterials as antimicrobial agents Microorganisms are the main factor that cause

infection to open wounds and invade inside the body tissues and cause internal infections [2]. Using

biocompatible antimicrobial agents that exbibit the advantage of nano-sized scaffolds as wound fence will

provide good antimicrobial activity to promote wound healing [3]. Electrospun biopolymeric nanofibers

are being studied as effective wound dressing materials [4,5,6]. Zein is the plant protein which is

biodegradable as well as biocompatible and is considered for various approaches for instance drug carrier,

supply system [7] wrapping of food material and scaffolds for tissue engineering [8]. Zein nanofibers are

easily fabricated by simple electrospinning process. Gelatin shows great activation of macrophages and

good haemostatic effect.[9][10] The main advantage of this work is using strong antimicrobial effects and

drug delivery property of nanofibers polymeric mats of antimicrobial agents like Zein and Gelatin by

incorporating Ibuprofen for better and enhanced wound management.

Experimental Work

The gelatin is one of processed formation of a polymeric protein, collagen which is an alternative to the

protein to collagen. it is easily available at a considerably lower cost and helps in retaining many of the

advantages of the collagen such as the excellent biodegradability, biological origin and biocompatibility.

The electrospinning of the gelatin and the gelatin poly blend and its characteristics have been used for the

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wound dressing. The material Zein comprises of the proline, glutamine and hydrophobic amino acids. It is

also quite rich in proteins which is available in the proteinaceous bodies by the endosperm of the corn

kernels. The use of the films and coatings is due to the hydrophobic proteins. It is a GRAD polymer that

was approved by the United States FDA. It can be used for the drug delivery and for making of the particular

systems. The use of zein has been quite proficient in producing edible films and capsules. The NPS present

within the zein proteins is used for preparation and the encapsulation of the drugs and bioactive compounds

such as coumarin and ivermectin.

Two sample solutions were prepared 1. Zein/gelatin and 2. Zein/ gelatin with ibuprofen. The solutions were

separately filled in a syringe with capillary tip of 0.6mm inner diameter. The fibers of solutions used were

deposited continuously and were collected on the collector surface (15cm away from the needle tip with an

angle of 10o for about 3 to 3.5 hours. The collected samples were remained at room temperature for utter

drying.

Table 1: Solution—Zein/Gelatin and Zein/Gelatin with Drug.

Gelatin (g)

Formic Acid (g)

Zein(g)

DMF(g)

Ibuprofen(g)

Total Weight

of polymer

Stock (g)

0.3 0.7 0.38 0.62 --- 2

0.3 0.7 0.38 0.62 0.068 2.068

Sample Characterization

Outside structure of Zein and Gelatin nanofibers were acquired through Zeiss Ultra Plus Field released

examination of Electron Microscope. Samples were gold coated and examined at the voltage of 2Kv. The

FTIR Spectra was used to analyze the chemical structure of nanofibers with or without drug were analyzed

through Thermo Scientific iS10 FT-IR. The release behavior of Ibuprofen from the nanofibrous mats in

PBS solution was analyzed using UV-Vis spectrophotometer. In order to examine spreading conduct of

IBU from zein and gelatin nanofiber, known IBU concentrations of 150ppm, 125ppm, 100ppm, 75ppm and

50 ppm in PBS solution were used to prepare calibration curve of IBU using UV-Visible

Spectrophotometer. 30mg of IBU loaded Z/G nanofibrous sheet (containing 3.0mg of drug) was kept in 30

ml PBS at 37°C and was stirred smoothly and continuously. A 1ml aliquot was withdrawn every 5 minutes

and accessed under the UV-vi, so that every new sample should reflect cumulative drug spread. Each time

an aliquot was withdrawn was replaced with 1ml fresh pbs to avoid change in volume.

Results and Discussion

Chemical Structure of electrospun nanofibers

FT-IR spectra of samples was analyzed to conform the presence of drug and also to identify any chemical

reaction between nanofibrous mats and IBU exist.

Fig. 1 represented the characteristic absorption band at 1656 cm-1 2351 cm-1, 2950 cm-1 and 3304 cm-1 is

related to Carbonyl, NH3, CH and NH stretching. The band at 676 cm-1 C-O-H bending. The NH

deformation is shown at 1548 cm-1. FT-IR spectra of zein and gelatin and Z/G loaded with IBU also showed

peaks at same bands with molecular bending and stretching.

Page 7: International Symposium on Advances in Metallurgy & Materials

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0 2000 4000

Ab

so

rba

nc

e (

A.U

)

Wavenumber (cm-1)

Zein and Gelatin

Z/G with Drug

676

1548

1656

23512950

3304

Fig.1 FTIR- zein/gelatin and zein/gelatin with ibuprofen

Fig. 2 SEM of zein/gelatin with ibuprofen

Morphology of electrospun nanofibers

The surface morphology and diameter distribution of zein/gelatin nanofibers loaded with ibuprofen are

presented in Fig. 3 with average diameter of 493.77nm.

Page 8: International Symposium on Advances in Metallurgy & Materials

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0.30 0.35 0.40 0.45 0.50 0.55 0.60

0

1

2

3

4

5

6

7

8

Fre

qu

en

cy(s

-1)

Diameter (um)

Diameter (um)

Fig. 3 Diameter distribution of nanofibrous mat

Release behavior of nanofibers

The highest peak of IBU was recorded at ∼264nm. The release of drug was started after 45 mins on stirring

of sheet in pbs solution. The IBU (drug) released completely from nanofibrous sheet in 2hours. After 2hours

there was no release of drug as no change in absorbance was observed.

Fig. 5 Release of Ibuprofen from nanofibrous sheet

Conclusion

The SEM images of drug loaded Zein/Gelatin nanofibers presented bead-free morphology with an average

diameter of 493.7 nm. The resulting composite nanofibrous mats showed no chemical reaction with each

other and with the encapsulated drug with good compatibility in terms of release behavior. FTIR spectra

inferred Gelatin and zein are highly miscible with each other along with IBU. Peaks showed drug do not

y = 0.0006x + 0.1301R² = 0.9353

0

0.05

0.1

0.15

0.2

0.25

0 20 40 60 80 100 120 140

Ab

sorb

ance

(A

U)

Time

Drug Release

Page 9: International Symposium on Advances in Metallurgy & Materials

5

react with polymers. The release of drug from resultant nanofibers showed complete release within 2 hours

which represents it remain effective for minimum 2 hours and promote antimicrobial activity.

References

1. Forson, O. A., Ayanka, E., Olu-Taiwo, M., Pappoe-Ashong, P. J., & Ayeh-Kumi, P. J. (2017).

Bacterial infections in burn wound patients at a tertiary teaching hospital in Accra, Ghana. Annals

of burns and fire disasters, 30(2), 116–120.

2. P.T.S. Kumar, V.K. Lakshmanan, T.V. Anilkumar, C. Ramya, P. Reshmi, A.G. Unnikrishnan,

S.V. Nair, R. Jayakumar, ACS Appl. Mater. Interfaces 4 (2012) 2618–2629.

3. L.R. Lakshman, K.T. Shalumon, S.V. Nair, R. Jayakumar, S.V. Nair, J. Macromol. Sci. A 47 (2010)

1012–1018.

4. K.N. Kontogiannopoulos, A.N. Assimopoulou, I. Tsivintzelis, C. Panayiotou, V.P. Papageorgiou,

Int. J. Pharm. 409 (2011) 216–228.

5. M. Jannesari, J. Varshosaz, M. Morshed, M. Zamani, Int. J. Nanomed. 6 (2011) 993–1003. U.

Dashdorj et al. / International Journal of Biological Macromolecules 80 (2015) 1–7 7.

6. J.T. Lin, C.H. Li, Y. Zhao, J.C. Hu, L.M. Zhang, ACS Appl. Mater. Interfaces 4 (2012) 1050–1057.

7. X.M. Liu, Q.S. Sun, H.J. Wang, L. Zhang, J.Y. Wang, Biomaterials 26 (2005) 109–115

8. S.J. Gong, H.J. Wang, Q.S. Sun, S.T. Xue, J.Y. Wang, Biomaterials 27 (2006) 3793–3799.

9. P. J. ROSE , in ``Encyclopedia of Polymer Science and Engineering'', 2nd Edn, Vol. 7, H. M. Mark

(Ed.), (John Wiley & Sons, New York, 1989) p. 488.

10. K. TOM IHATA , K. BURCZAK , K. SHIRAKI and Y. IKADA , in ``Polymers of Biological and

Biomedical Importance'', edited by S. W. Shalaby, Y. Ikada, R. S. Langer, J. Williams (ACS

Symposium Series 540, 1994) 275.

11. Rowan, M. P., Cancio, L. C., Elster, E. A., Burmeister, D. M., Rose, L. F., Natesan, S., … Chung,

K. K. (2015). Burn wound healing and treatment: review and advancements. Critical care (London,

England), 19, 243. doi:10.1186/s13054-015-0961-2.

12. R. Jayakumar, M. Prabaharan, P.T.S. Kumar, S.V. Nair, H. Tamura, Biotechnol. Adv. 29 (2011)

322–337

13. A.R. Unnithan, G. Gnanasekaran, Y. Sathishkumar, Y.S. Lee, C.S. Kim, Carbohydr. Polym. 102

(2014) 884–892.

14. Q.R. Jiang, N. Reddy, Y.Q. Yang, Acta Biomater. 6 (2010) 4042–4051.) ……. (H.J. Wang, L. Di,

Q.S. Ren, J.Y. Wang, Materials 2 (2009) 613–635.

15. B.H. Kong, Y.L.L. Xiong, J. Agric. Food Chem. 54 (2006) 6059–6068.

16. K. Kanjanapongkul, S. Wongsasulak, T. Yoovidhya, J. Appl. Polym. Sci. 118 (2010) 1821–1829.

17. Ritger P L and Peppas N A 1987 A simple equation for description of solute release II. Fickian and

anomalous release from swellable devicesJournal of Controlled Release 5 37–42

18. Gouda R, Baishya H and Qing Z 2017 Application of mathematical models in drug release kinetics

of carbidopa and levodopa ER tablets J Develop Drugs 6 1–8

19. Dash S, Murthy P N, Nath L and Chowdhury P 2010 Kinetic modeling on drug release from

controlled drug delivery systems Acta Pol Pharm. 67 217–23

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An Approach towards the Surface Treatment of Natural Fiber to

Improve Its Compatibility with Polymer Matrix

Muhammad Moeez Mughal, Muhammad Wasim Akhtar*, Muddassir Ali Memon, Muhammad

Moazam Baloch

Department of Metallurgy and Materials Engineering, Mehran University of Engineering and

Technology, Jamshoro 76062, Pakistan.

*[email protected]

Abstract: Herein, we investigate the effect of chemical treatment on sisal fiber through silanization. Natural

fibers are hydrophilic due to the presence of hydroxyl groups; however, the polymer matrix is hydrophobic in nature.

The properties of composites are affected by incompatibility of natural fibers and polymer matrix. Surface

modification of natural fibers is the best alternative to minimize this bottleneck. Initially; the natural sisal fiber was

dispersed in acidic medium for the removal of impurities and increases the fiber surface roughness. Subsequently; the

acetylated sisal fiber was treated again with a 3-aminopropyltriethoxy silane (APTES) solution for grafting the silanol

groups onto the surface of sisal fiber. The FTIR and XRD results reveal the lignin and hemicellulose contents were

removed after surface modification, which enhances its crystallinity, and morphological characteristics of the sisal

fiber.

Keywords: Surface modification, sisal fiber, acetylation, FTIR, APTES.

Introduction

Plant and vegetable-based natural fibers abundantly used in different fields in modern developments. These

natural fiber possess various physico-chemical properties good processability, abrasive to wear,

biodegradability, stiffness, low density, high strength to weight ratio, eco-friendly, ease of recycling, and

renewability[1]. The synthetic fibers show excellent properties; therefore, it is extensively used as a

reinforcing agent for polymer and other materials. There are various drawbacks of synthetic fibers in

compare to natural fibers that includes, ecological, its processability, not recyclable, and high

manufacturing costs[2]. Due to numerous advantages of using plant-based fiber over synthetic fibers, Sisal

fiber is abundantly found in the earth's crust and utilized as a reinforcement material for many applications.

The sisal fiber possesses good strength, malleability, durability, ability to stretch, chemical affinity,

resistance towards the acidic environment, good stiffness, and availability. It is used in the field of

construction for making the mold sheets[3]. The structure of sisal fiber is very complex because various

constituents are attached to the cell walls including cellulose, hemicellulose, and lignin. These constituents

are strongly affected by the physico- mechanical and chemical properties of sisal fiber[4].

Sisal fiber is hydrophilic in nature because it extracts from the “Agava Sisalana” plant that are

lignocellulosic, which carries strong hydroxyl groups. However, most polymers are found in hydrophobic

nature. The interface between fiber and polymer are crucially important to improve the properties of

composites. A proper interface generates interconnective networks and better interlocking between fiber

and polymers, results in enhanced properties of the composites[5]. Grafting is one of the possible routes to

attached desired moiety on the surface of fiber. These functional moieties are certainly helpful to improve

the interference between fiber and polymers. Several methods of surface modification have reported and

show its importance which includes chemical[6], physical[7], and biological treatments[8]. Many reports

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published earlies shows the chemical treatment of lignocellulose fiber for the improvement of fiber-matrix

adhesion. Mercerization is the simplest, effective, and easiest way for the modification of fiber surface. The

oil palm empty fruit bunch OPEFB fiber and mesocarp fiber was chemically treated with different mediums

to improve its properties. The overall results show that silane treated OPEFB fiber has shown maximum

tensile strength and thermal stability. The mesocarp fiber shows minimum strength than that of OPEFB

fiber, due to the high cellulose content of OPEFB fiber[9]. The surface treatment of micro fibrillated

cellulose (MFC) was done by various coupling agent of silane and then incorporated into the epoxy matrix

to make the composite. This type of chemical treatment is altered the character of MFC from hydrophilic

to hydrophobic. However, the crystallinity structure of the cellulose microfibrils was not affected after this

treatment. The homogeneous dispersion and stronger adhesion between microfibrils and matrix were

noticed in SEM micrographs, which resulted in better mechanical properties of composite[10]. Author used

several concentration of NaOH solution (0.25%, 0.5%, 1%, 2% 5% and 10%). The excellent mechanical

properties achieved up to 2% NaOH solution, the tensile properties decreased slightly by increasing the

NaOH concentration. Previous studies highlighted the surface treatment of natural fiber and natural fiber

composites. The researcher reported that untreated and silane treated natural fiber achieved less water

absorption with alkali-treated natural fiber[11]. Kalyana highlighted the surface modification of dharbai

fiber-reinforced polyester composites through alkali treatment (KOH). The regression analysis was adopted

for determining the relationship between the dependent and independent variables; the dependent variables

(tensile strength, flexural strength, and impact strength), independent variables (solution concentration%

and soaking time). It is reported that alkali (KOH) treatment was effective for altering the compatibility of

dharbai fiber reinforced polymer composites[12].

Functionalization of plant-based fiber was carried out with different mediums for the improvement of

physico-mechanical properties. It should be worthy to investigate that chemically treated sisal fiber with

homopolymer matrix showed excellent mechanical properties, respectively. The modified sisal fiber-

reinforced composites with homopolymer possess better mechanical properties (tensile strength and

hardness) and water absorption with copolymer matrix. In comparison, with other chemically treated

reinforced composites. KOH treated sisal fiber-reinforced composites showed better mechanical properties.

The tensile strength 32.70 MPa in compare to other chemically treated composites[13].

In this paper, the sisal fiber was acetylated by innovative and effective methods. Sisal fiber is treated with

acidic environment for the removal of hemicellulose and lignin content. Later, the acid-modified sisal fiber

treated with silane coupling for grafting the silane moiety on the surface of fiber. The surface-modified

fiber is very much effective and helpful for advanced applications.

Experimental

Materials

Sisal fiber was used as a reinforcing material and obtained from the agricultural site, in Pakistan. The silane

coupling agent of (3-aminopropyltriethoxy silane) (APTES) was supplied from Sigma Aldrich. Sulfuric

acid, nitric acid, and glacial acetic acid from Dae-Jung chemicals Co. Ltd, was used for the silanization of

fiber treatment.

Surface modification of sisal fiber

In a typical process, the 02 gm of pristine sisal fiber was homogeneously dispersed with a molar mixture of

HNO3 and H2SO4 in three neck round bottom flask. The reactor was placed in a water bath for 3 hours at

80°C for continuous stirring. The solution was drained out; then the fibers were dried in oven at 80°C for

24 hours. Before treating the acetylated sisal fiber with (APTES), Initially; the (APTES) was pre-

hydrolyzed at room temperature for the formation of silanol groups. The solution of 3-APTES with absolute

Page 12: International Symposium on Advances in Metallurgy & Materials

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ethanol of 95% and 5% of distilled water was first hydrolyzed at 12 hours at room temperature. The few

drops of glacial acetic acid were added into hydrolyzed silane solution for adjusting the PH between 4-5.

Subsequently, the acetylated sisal fiber was added into the hydrolyzed silane solution and placed at hot-

plate magnetic stirrer at 80°C for 12 hours. The silanized sisal fiber was collected and cooled down at room

temperature, and wash with DI H2O and ethanol solvent to remove unreacted silane. Finally, the fibers were

dried at 70°C in the oven for overnight.

Characterization

The infrared spectroscopy (FTIR, PerkinElmer spectrum two) was used for the determination of functional

groups of pristine, acetylated, and modified sisal fiber. The crystallinity index and phase structure of the

sisal fiber was analyzed through X-ray diffraction (XRD) technique at 40 kV and 30 mA with Cu Kα

radiation (λ = 1.54 Å) were recorded from 10°-45° (2θ) (Bragg’s angle) at a scanning speed of 0.6/ min.

The morphological behavior of pristine, acetylated and modified fiber was characterized through scanning

electron microscope (SEM, JEOL JSM-6380LV, Japan at 5–10 KeV). An energy dispersive X-ray (EDX)

was used to determine the elemental constituents of pristine, acid-treated and surface-modified sisal fiber

by using JEOL JSM SEM instrument with attached EDX facility.

Results and Discussion

Surface modification of natural fiber is one of the useful paths that can improve the surface characteristics

and morphological behavior of natural fibers .It helps to develop strong oxygenated groups that are useful

to interface between fiber and polymer. The sisal fiber is chemically treated with acidic solution for the

separation of cellulose chain from the intricate natural fiber. The pristine sisal fiber possesses white color

naturally. After the acid treatment, the fiber changes its color from greyish white to yellow. Finally, the

yellow color of acid-treated sisal fiber is changed to yellowish-brown color, this is an indication of

substitution of hydroxyl present in acetylated fiber with silanol moieties in silane treated fiber as shown in

Fig.1[14]. The surface-modified sisal fiber has been studied by FTIR spectroscopy as shown in Fig.2. The

pristine sisal fiber shows the broad band at around 3300-3500 cm-1 related to OH vibration stretching. The

transmittance bands at 1740 cm-1 and 1245 cm-1 belong to the carbonyl C-O and C=O stretching vibration

of the linkage of carboxyl acid and ester groups which is present in raw sisal fiber naturally[15]. The band

at 1430 cm-1 resembles CH2 symmetric bending present in cellulose, and the band at 1630 cm-1 corresponds

to the presence of water in the natural fibers[16]. The band at 1080 cm-1 is associated due to hydrogen

groups[17]. However, the FTIR spectra of surface-modified sisal fiber shows various bands at around 870

cm-1, 1130 cm-1, 1640 cm-1, 2853 cm-1 and 2920 cm-1. The band at 2853 cm-1 and 2920 cm-1 are due to CH2

vibration stretching[18]. The two strong absorption bands at 870 and 1130 cm-1 indicates the -Si-O- bond

and -Si-O-Si- bond[19]. This band confirms the grafting of hydrolyzed silane on the surface of sisal fiber.

Fig: 1: Pictorial image of sisal fiber: (a) Pristine, (b) acid-treated, and (c) surface-modified sisal fiber

Page 13: International Symposium on Advances in Metallurgy & Materials

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The crystallinity index of pristine, acid-

treated, and surface-modified sisal fiber was

studied through X-ray diffractometers (XRD)

analysis. The XRD pattern of all fibers is

displayed in Fig.3. All fibers display a similar

nature of XRD patterns. The pristine fiber

shows the diffraction patterns of (110) and

(110) located at 2θ= 15° angle[20]. These

diffraction planes indicate that fiber contains

an amorphous nature. However, after surface

modification, the crystallinity index is

improved[21]. The crystallographic patterns

of the cellulose phase found at 2θ= 22.3° and

34.9° angle, which corresponds to the

diffraction planes of (200) and (004)[22].

Ouajai et al. highlight the diffraction patterns

of the cellulose structure of these reflected

planes. The natural sisal fiber is mainly

composed of about 59% crystalline region,

and the remaining phase of 41% is

amorphous. Owing to this; chemical treatment

is improved the crystallinity index due to a

decrease in impurities. It should be noted

that crystallinity index was determined to

show the order of crystalline plane instead

of crystallinity regions[23]. The

crystallinity index of pristine and acid

treated sisal fibers are calculated by Segal empirical method[24]. The results of crystallinity index

of pristine and acid-treated sisal fibers are summarized in Table 1. The overall results of chemical

composition and structural changes verified the silane groups are coupled on the surface of sisal fiber, and

it is also modifying its crystallinity index. Depicted the enhancement in crystallinity index after

Fig: 3: XRD spectra of (a) pristine, (b) acid-treated, and (c)

surface-modified sisal fiber

Fig: 2: FTIR spectra of (a) Pristine, (b) acid-treated and (c) surface-modified sisal fiber and magnified spectra of surface

-modified sisal fiber

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10

modification or acylation. The above results confirm the attachment of silanol groups on the surface of

sisal fiber, while retaining its crystallinity.

Table 1: Crystallinity index of pristine and acid-treated sisal fiber

he morphology of sisal fiber is examined through Scanning electron microscope as illustrated, in Fig.4. It

is observed in natural fiber that several bundles of nodes due to a large proportion of lignin and

hemicellulose phase, which is mainly composed onto the surface of natural fibers as shown; in Fig.4(a)[25].

Fig.4(b); reveals the rough and stiff structure due to acid-treatment. It happened due to removal of lignin

Samples Ic (%)

Pristine sisal fiber 49.13

Acid-treated sisal fiber 62.04

Fig: 4: SEM images of (a) pristine, (b) acid-treated, and surface-modified sisal fiber

Fig: 5 (a) EDX spectra of pristine sisal fiber and (b-d) carbon, and oxygen mapping image of pristine

sisal fiber

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11

and hemicellulose content during the acetylation process. After the surface modification, the fiber surface

reveals the presence of macroscopes fibrillation and rougher surfaces. The silanol moieties generate after

the hydrolyzation process. Afterward, the formation of covalent bonds and H-bonds occurs, while the

breaking of silanol groups. Thus, OH groups of acetylated sisal fiber interact into these bonds as

demonstrated; in Fig.4(c)[26]. Fig. 5-7 shows the EDX analysis of sisal fibers, and their elemental values

depicted in Table 2.

Table 2: Elemental analysis of pristine, acid-treated, and surface-modified sisal fiber

Fig. 5 showed the presence of carbon and oxygen as are the most dominant constituents of lignocellulose

fibers structure. The C and O elements are also recorded in acid-treated and silane modified sisal fiber as

shown, in Fig. 5-6. After the surface modification of sisal fiber, the concentration of carbon and oxygen is

reduced due to the removal of the lignin and hemicellulose phase, which is further confirmed by the

elemental mapping of surface-modified sisal fiber is presented Fig. 7. The presence of the Si in silane

modified sisal fiber confirmed the attachment of silanol moiety on the surface of fiber[27]. The SEM, along

with EDX results confirm the surface modification and grafting of silanol functional moieties on the surface

of sisal fiber. The modified fiber is beneficial for homogenously dispersed fiber in the polymer matrix.

Element Pristine sisal

fiber

Acid-treated

sisal fiber

Surface-modified

sisal fiber

C 51.88 49.61 49.50

O 48.12 50.39 49.38

Si ----- ----- 1.12

Total 100 100 100

Fig: 6: (a) EDX spectra of acid-treated sisal fiber and (b-d) carbon, and oxygen mapping image of

acid-treated sisal fiber

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Conclusion

In conclusion, the wet chemical method was adopted for the surface modification of plant-based sisal fiber.

The surface modification technique generates the possible silanol moieties on the surface of sisal fiber. The

FTIR, and XRD results validated the massive changing after functionalization, which improves its

crystallinity, and provide route for homogenous dispersion in the polymer matrix. The SEM results showed

more stiff and robust structure or sisal fiber after surface modification of sisal fiber. The modified natural

fibers are very effective and beneficial for future development of advanced composite materials.

Acknowledgement

This work was funded by the Mehran University of Engineering & Technology, Jamshoro. The authors also

extend gratitude to Engr. Umair Aftab for his valuable advice and suggestion for his valuable discussions.

References

1. Haque, R., et al., Fibre-matrix adhesion and properties evaluation of sisal polymer composite.

Fibers and Polymers, 2015. 16(1): p. 146-152.

2. Krishna, K.V. and K. Kanny, The effect of treatment on kenaf fiber using green approach and their

reinforced epoxy composites. Composites Part B: Engineering, 2016. 104: p. 111-117.

3. Ramesh, M., K. Palanikumar, and K.H. Reddy, Comparative evaluation on properties of hybrid

glass fiber-sisal/jute reinforced epoxy composites. Procedia Engineering, 2013. 51: p. 745-750.

4. Ibrahim, I.D., et al., Impact of surface modification and nanoparticle on sisal fiber reinforced

polypropylene nanocomposites. Journal of Nanotechnology, 2016. 2016.

5. Akram Khan, M., et al., Characterisation studies and impact of chemical treatment on mechanical

properties of sisal fiber. Composite Interfaces, 2011. 18(6): p. 527-541.

Fig: 7: (a) EDX spectra of surface-modified sisal fiber and (b-e) carbon, oxygen, and

silicon mapping image of surface-modified sisal fiber

Page 17: International Symposium on Advances in Metallurgy & Materials

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6. Mokaloba, N. and R. Batane, The effects of mercerization and acetylation treatments on the

properties of sisal fiber and its interfacial adhesion characteristics on polypropylene. International

Journal of Engineering, Science and Technology, 2014. 6(4): p. 83-97.

7. Mishra, S.K., Advanced Techniques for Surface Engineering of Industrial Materials. 2002.

8. Orue, A., A. Eceiza, and A. Arbelaiz, Pretreatments of Natural Fibers for Polymer Composite

Materials, in Lignocellulosic Composite Materials. 2018, Springer. p. 137-175.

9. Sreekala, M., M. Kumaran, and S. Thomas, Oil palm fibers: Morphology, chemical composition,

surface modification, and mechanical properties. Journal of Applied Polymer Science, 1997. 66(5):

p. 821-835.

10. Lu, J., P. Askeland, and L.T. Drzal, Surface modification of microfibrillated cellulose for epoxy

composite applications. Polymer, 2008. 49(5): p. 1285-1296.

11. Sgriccia, N., M.C. Hawley, and M. Misra, Characterization of natural fiber surfaces and natural

fiber composites. Composites Part A: Applied Science and Manufacturing, 2008. 39(10): p. 1632-

1637.

12. Sundaram, S.K. and S. Jayabal, Regression modeling and particle swarm optimization of

mechanical properties of potassium hydroxide pretreated Dharbai fiber-reinforced polyester

composites. Proceedings of the Institution of Mechanical Engineers, Part L: Journal of Materials:

Design and Applications, 2016. 230(1): p. 105-115.

13. Oladele, I.O., J.A. Omotoyinbo, and B.O. Adewuyi, Mechanical and Water Absorption Properties

of Sisal-Fibre-Reinforced Polypropylene Composites for Ceiling Applications. West Indian Journal

of Engineering, 2014. 37(1).

14. Bikiaris, D., et al., Use of silane agents and poly (propylene‐g‐maleic anhydride) copolymer as

adhesion promoters in glass fiber/polypropylene composites. Journal of Applied Polymer Science,

2001. 81(3): p. 701-709.

15. Paluvai, N.R., S. Mohanty, and S. Nayak, Unsaturated polyester‐toughened epoxy composites:

Effect of sisal fiber on thermal and dynamic mechanical properties. Journal of Vinyl and Additive

Technology, 2017. 23(3): p. 188-199.

16. De Rosa, I.M., et al., Morphological, thermal and mechanical characterization of okra

(Abelmoschus esculentus) fibres as potential reinforcement in polymer composites. Composites

Science and Technology, 2010. 70(1): p. 116-122.

17. Lu, X., et al., The preparation of self-reinforced sisal fiber composites. Polymers and Polymer

Composites, 2004. 12(4): p. 297-308.

18. Głowińska, E. and J. Datta, Bio polyetherurethane composites with high content of natural

ingredients: hydroxylated soybean oil based polyol, bio glycol and microcrystalline cellulose.

Cellulose, 2016. 23(1): p. 581-592.

19. Launer, P.J., Infrared analysis of organosilicon compounds: spectra-structure correlations.

Silicone compounds register and review, 1987. 100.

20. Liu, Y. and H. Hu, X-ray diffraction study of bamboo fibers treated with NaOH. Fibers and

Polymers, 2008. 9(6): p. 735-739.

21. Sousa, F.W., et al., Evaluation of a low-cost adsorbent for removal of toxic metal ions from

wastewater of an electroplating factory. Journal of environmental management, 2009. 90(11): p.

3340-3344.

22. Oudiani, A.E., et al., Crystal transition from cellulose I to cellulose II in NaOH treated Agave

americana L. fibre. Carbohydrate Polymers, 2011. 86(3): p. 1221-1229.

23. Ouajai, S. and R. Shanks, Composition, structure and thermal degradation of hemp cellulose after

chemical treatments. Polymer degradation and stability, 2005. 89(2): p. 327-335.

24. Pickering, K.L., et al., Optimising industrial hemp fibre for composites. Composites Part A:

Applied Science and Manufacturing, 2007. 38(2): p. 461-468.

25. Mwaikambo, L. and M. Ansell, Mechanical properties of alkali treated plant fibres and their

potential as reinforcement materials II. Sisal fibres. Journal of materials science, 2006. 41(8): p.

2497-2508.

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26. Singh, B., M. Gupta, and A. Verma, Influence of fiber surface treatment on the properties of sisal‐polyester composites. Polymer Composites, 1996. 17(6): p. 910-918.

27. Mohan, T. and K. Kanny, Chemical treatment of sisal fiber using alkali and clay method.

Composites Part A: Applied Science and Manufacturing, 2012. 43(11): p. 1989-1998.

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Lead Ion Removal Using AACH Derived Alumina

Asma Ameer1, Syed Mujtab ul Hassan 1, Syed M Husnain 2, Jamil Ahmad 1, Faisal Shahzad 1,

Zafar Iqbal 1, Mazhar Mehmood 1

1 Department of Metallurgy and Materials Engineering, Pakistan Institute of Engineering and Applied

Sciences (PIEAS), Nilore, Islamabad, Pakistan

2 Chemistry Division, Directorate of Science, Pakistan Institute of Nuclear Science and Technology

(PINSTECH), Islamabad

Abstract: High surface alumina whiskers were synthesized in this study via hydrothermal route for the active

removal of lead ions. Alumina whiskers were produced by calcining ammonium aluminum carbonate hydroxide

(AACH) whiskers at three different temperatures i.e. 700oC, 900oC and 1100°C. XRD and SEM were used for

the characterization of AACH as well as alumina whiskers. XRD revealed the formation of γ phase at 700°C and

900oC, while at 1100oC, a mixture of and phases was formed. SEM images showed the whisker-like

morphology of both AACH and alumina. Highest removal efficiency was found in the case of alumina calcined

at 700oC. Effect of contact time on removal efficiency was also studied and 60 minutes was selected as an

equilibrium time for adsorption. It was found that alumina calcined at 700oC has more potential to remove lead

ions due to its higher surface area.

Keywords: AACH whiskers, γ alumina, adsorption

Introduction

Scarcity of drinkable water is one of the most serious issues of the world today. According to a report, every

third person in the world has fallen prey of this problem [1]. Pakistan lies at 80th position out of 122 nations

with respect to the quality of drinking water. A report by International Monetary Fund (IMF) says that

Pakistan could run dry by 2025 if no proper measures are taken. Therefore, availability of drinkable water

is a top concern in Pakistan [2]. One of the major hazardous heavy elements in drinkable water is lead

which, if accumulated in our body excessively, leads to anemia, cancer, mental retardation, renal and kidney

diseases etc. [3]. Other sources of lead are leaded gasoline, paint, children jewelry and toys, food cans

sealed with lead solder, batteries, radiators and color of inks [4]. In order to remove lead from contaminated

water adsorption is an efficient method. It is an easy-to-use, economical and environment-friendly process

[3].

Alumina is a widely used ceramic material due to its excellent mechanical and physicochemical properties.

As a result, it is used as catalyst support [5], in sensors [6] and as adsorbent material [7]. Alumina exists in

eight polymorphic forms including cubic (η), tetragonal (δ), hexagonal (α), monoclinic (θ), orthorhombic

(κ), tetragonal (γ), cubic (χ) and hexagonal (β) crystal structures [8].

Various materials have been investigated for use as ion adsorbent from water. Some of the examples are

carbon nano tubes (CNTs) [3], silica oxide encapsulated natural zeolites [9], hydroxyapatite (HAP) [10],

dendrimers, mesoporous silica, chitosan-based nano absorbents [11] and alumina/iron oxide nano-

composites [12] etc. Among these, alumina nanostructures have much potential for adsorption of lead.

Various methods have been reported for synthesis of alumina nanostructures, e.g., sol gel [13],

hydrothermal method [14], combustion method [15] and ultrasonic flame pyrolysis [16]. Adsorption of lead

by alumina nanostructures synthesized through sol gel [13] and combustion method [15] has been

investigated but as far as authors know there exists no study on the adsorption of lead by alumina synthesized through hydrothermal route.

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Experimental Work

Aqueous solution of aluminum nitrate and urea was made by mixing these chemicals in distilled water. The

mixture was then poured into a hydrothermal reactor. The reactor was put into an oven. Temperature was

set at 120°C and time for hydrothermal treatment was 24 hours. The resulting solution was washed by

filtration followed by drying to get the AACH powder. AACH powder was calcined at 700oC, 900oC,

1100oC to get alumina powder. Lead nitrate was used to prepare the stock solution for lead which was

further diluted for the experimentation. Adsorbent dose for the experiment was 1 g/L and pH was set at 4.

Atomic Absorption spectroscopy was used to find the lead concentration before and after adsorption.

Results and Discussion

Fig. 2 (a) shows the XRD pattern of AACH and it is evident that pure AACH was formed through

hydrothermal process. Fig. 2 (b) exhibits XRD patterns of AACH samples calcined at 700°C, 900°C and

1100°C. With an increase in temperature, degree of crystallinity is found to enhance. At 700°C, diminished

peaks of γ-phase are observed along with a hump around 2 = 23o indicating the presence of an amorphous

phase with some crystalline fraction. This type of structure is expected to have less density, higher surface

area and surface energy which is of crucial importance for ion removal capability. It is because the

crystallization is expected to result in densification. As the calcination temperature is increased to 900oC,

peaks of-phase become sharper, while at 1100°C, much sharper peaks of θ and α-alumina are seen

indicating high degree of crystallinity and thus enhanced densification.

The other important parameter is morphology which may give an indication about the surface area. AACH

is in the form of whiskers. If after calcination to form alumina, the whisker-like morphology is not

destroyed, it may be a sign that little densification has taken place and that the porous structure formed

during decomposition of AACH is maintained. Fig. 3 shows the SEM images of AACH and alumina

calcined at 700°C, 900°C and 1100°C (from a-d respectively). From these images the whisker-like

morphology of alumina formed is clearly visible. The aspect ratio of these whiskers is about 10:1. This

Fig. 1: Hydrothermal route for alumina powder synthesis

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whisker-like morphology is still maintained after calcination leading to the conclusion that little

densification occurred during calcination.

Fig. 2: XRD patterns for AACH (a) and alumina (b) calcined at 700 °C, 900 °C and 1100

°C

Fig. 3: SEM micrographs for AACH (a) and alumina calcined at 1100°C (b), 900°C (c) and 700°C (d)

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Adsorption study of AACH calcined at three temperatures, i.e., 700°C, 900°C and 1100°C was studied as

shown in Fig. 4. The removal efficiency was calculated by the following formula:

R.E. = (C0 - Ce) / C0 * 100

Where C0 is the initial metal ion concentration and Ce is the equilibrium ion concentration after adsorption.

It was observed that removal efficiency was highest in case of calcination at 700°C. The possible reason of

decrease in adsorption with increase in calcination temperature may be the decrease in surface area. AACH

transforms to alumina by decomposition reaction, in which about 63 % of mass is lost. This leaves behind

a porous structure with significant surface area. As the calcination temperature is enhanced, the porosity

decreases. Due to highest removal efficiency, 700°C temperature was selected for further adsorption study.

Contact time experiments were performed to study the kinetics and to get an optimum time of adsorption

for lead on -alumina. For lower contact times, the removal efficiency was very low. As the contact time

was increased, more and more adsorbent sites were occupied by the lead ions. After a certain time, all the

adsorbent sites would be filled by the adsorbate and further increase in contact time would not increase the

efficiency. The optimum time for this experiment, in which all the sites were occupied, was 60 minutes and

after this no significant increase in removal efficiency was observed.

It is important to notice that a maximum removal efficiency of about 22% was observed for the sample

calcined at 700oC with a contact time of 60 minutes.

Conclusions

Alumina whiskers were synthesized through hydrothermal route using low cost precursor and low

calcination temperature. Among the samples calcined at three different temperatures, (i.e., 700oC, 900oC

and 1100oC), the highest removal efficiency was observed in case of alumina calcined at 700 °C due to its

higher surface area which makes alumina an attractive adsorbent for lead removal.

0

5

10

15

20

25

30

35

40

45

50

23.5

%

8.6

%

26.4

%

1100900700

R.E

. (%

)

Temperature

11 22 33 44 55 66 77 88 990.0

4.4

8.8

13.2

17.6

22.0

26.4

30.8

35.2

39.6

R.E

. (%

)

Time (min)

Bare Alumina

Fig. 4: Effect of calcinations temperature and contact time on removal efficiency

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References

[1] R. e P. Schwarzenbach, T. Egli, T. B. Hofstetter, U. von Gunten, and and B. Wehrli, “Global Water Pollution and Human Health,” annual Rev. Environ. Resour., no. November, 2010.

[2] A. Azizullah, M. Nasir, K. Khattak, P. Richter, and D. Häder, “Water pollution in Pakistan and its impact on public health — A review,” Environ. Int., vol. 37, no. 2, pp. 479–497, 2010.

[3] Ihsanullah et al., “Heavy metal removal from aqueous solution by advanced carbon nanotubes: Critical review of adsorption applications,” Sep. Purif. Technol., vol. 157, pp. 141–161, 2016.

[4] R. Zhang, V. L. Wilson, A. Hou, and G. Meng, “Source of lead pollution, its influence on public health and the countermeasures,” Int. J. Heal. Anim. Sci. Food Saf., vol. 2, no. 1, pp. 18–31, 2015.

[5] K. Maeda et al., “Synthesis of thermostable high-surface-area alumina for catalyst support,” J. Mater. Sci. Lett., vol. 9, no. 5, pp. 522–523, 1990.

[6] E. C. Dickey, O. K. Varghese, K. G. Ong, D. Gong, M. Paulose, and C. a Grimes, “Room Temperature Ammonia and Humidity Sensing Using Highly Ordered Nanoporous Alumina Films,” Sensors, vol. 2, pp. 91–110, 2002.

[7] X. Q. Zhang, Y. Guo, and W. C. Li, “Efficient removal of hexavalent chromium by high surface area Al2O3rods,” RSC Adv., vol. 5, no. 33, pp. 15896–15903, 2015.

[8] S. D. M. and G. M. P. T. C. Chou, T. G. Nieh, “MICROSTRUCTURES AND MECHANICAL PROPERTIES OF THIN FILMS OF ALUMINUM OXIDE,” Scr. Metall. Mater., vol. 25, no. 1, pp. 2203–2208, 1991.

[9] Z. Wang et al., “Silica Oxide Encapsulated Natural Zeolite for High Efficiency Removal of Low Concentration Heavy Metals in Water,” Colloids Surfaces A Physicochem. Eng. Asp., 2018.

[10] A. Avram, O. Horovitz, F. Goga, and M. Tomoaia-cotisel, “Hydroxyapatite for removal of heavy metals from wastewater,” no. December, 2017.

[11] E. Vunain*, A. Mishra*, and B. Mamba, “Dendrimers , mesoporous silicas and chitosan-based nanosorbents for the removal of heavy-metal ions : A Review,” Int. J. Biol. Macromol., 2016.

[12] M. M. A. El-latif, A. M. Ibrahim, M. S. Showman, and R. R. A. Hamide, “Alumina / Iron Oxide Nano Composite for Cadmium Ions Removal from Aqueous Solutions,” vol. 2013, no. April, pp. 47–62, 2013.

[13] S. Tabesh, F. Davar, and M. R. Loghman-Estarki, “Preparation of γ-Al2O3 nanoparticles using modified sol-gel method and its use for the adsorption of lead and cadmium ions,” J. Alloys Compd., vol. 730, pp. 441–449, 2018.

[14] J. Ahmad et al., “Formation of porous α -alumina from ammonium aluminum carbonate hydroxide whiskers,” Ceram. Int., no. July, pp. 0–1, 2018.

[15] A. Rahmani, H. Z. Mousavi, and M. Fazli, “Effect of nanostructure alumina on adsorption of heavy metals,” DESALINATION, vol. 253, no. 1–3, pp. 94–100, 2010.

[16] K. Varatharajan, S. Dash, A. Arunkumar, R. Nithya, A. K. Tyagi, and B. Raj, “Synthesis of nanocrystalline α-Al2O3 by ultrasonic flame pyrolysis,” Mater. Res. Bull., vol. 38, no. 4, pp. 577–583, 2003.

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Synthesis, Characterization, and Antimicrobial Properties of

Al-Cu-Fe-B Quasicrystals

Aqab Zahoor1 , Taha Aziz1, Soumble Zulfiqar2, Naeem ul Haq Tariq1, Hafiz Rub Nawaz

Shahid1, Fahad Ali1, Khurram Shehzad3, Saquib Izhar4, Adrees Safdar4, Mazhar Mehmood1,

Hasan Bin Awais1

1Department of Metallurgy and Materials Engineering, Pakistan Institute of Engineering and Applied

Science, Islamabad, Pakistan

2School of Biological Sciences, University of the Punjab, Lahore, Pakistan

3Pakistan Institute of Nuclear Science and Technology, Islamabad, Pakistan

4Atomic Energy Mineral Center, Lahore, Pakistan

Abstract: Al65Cu23Fe11B quasicrystalline powder was synthesized, characterized and investigated with respect to

potential antimicrobial applications. Al65Cu23Fe11B quasicrystals were synthesized by high energy ball milling.

Antimicrobial surface of Al65Cu23Fe11B quasicrystaline powder sample was prepared by leaching in 5 wt% of Na2CO3.

Aluminium dissolved from icosahedral surface and produced a uniform layer of Cu and Fe. The techniques XRD,

SEM, EDX, and ICP were used to characterize the powder samples of quasicrystaline. Addition of boron produces

the Cu island morphology on the leached surface of quasicrystals. The antimicrobial properties of powder quasicrystals

were investigated by disk diffusion test by using Kocuria rosea and Enterobacter aerogenes. Leached quasicrystals are

showing zone of inhibition. So the leached quasicrystals can be good alternative materials for contact killing of

bacteria.

Keywords: Quasicrystal, thermal spray deposition, milling, disk diffusion test, contact killing

Introduction

Copper and silver surfaces rapidly kill bacteria when they come in contact with Cu or Ag and the process

is called contact killing [1]. Microorganisms have inherent capability to stay alive on frequently contact

surfaces which assist their accusation and move from surface to human being. In 2002, it was founded that

1.7 million of people United State hospital got infection per annum and 90,000 die out of them. According

to the estimation of the U.S. Centers for Disease Control and Prevention (CDC), the yearly costs of medical

concern for treating infectious diseases in the U. S. are about $120 billion [2]. A lot of studies have been

carried out on antimicrobial properties of Cu and its alloy [3-7]. However, the antimicrobial properties of

Cu containing quasicrystalline materials have yet to be explored. Unique structure of quasicrystals was first

observed in 1984 by Dan Shechtman [8]. Quasicrystals possess icosahedral symmetry, that is considered to

be forbidden in crystalline solids along with 5-fold, 8-fold, 10-fold, and 12- fold symmetries [9-11]. Due to

the complex structure of the quasicrystals, they do show unique set of properties including low thermal and

electrical conductivity[12, 13], high hardness [14], low coefficient of thermal expansion [15], low

coefficient of friction and wettability[16], good corrosion resistance[17, 18], and (in some cases)

biocompatibility[19]. The production of quasicrystals can be done through many different routes depending

up on the required final quasicrystalline morphology. Quasicrystals in powdered form can be fabricated

Corresponding author. E-mail address: [email protected]

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through ball milling [20] and also with subsequent annealing at an appropriate temperature[20]. This study

is concerned with the antimicrobial properties of the Al-Cu-Fe-B using Kocuria rosea and Enterobacter

aerogenes microorganisms. K. rosia is gram positive microorganism which have rounded shape and found

in urinary tract infection (UTI) [21]. Enterobacter aerogenes is gram negative bacteria with rod- shaped

morphology and causes opportunistic infection [22].

Experimental Work

Al65Cu23Fe11B quasicrystals were synthesized by mechanical milling followed by annealing. The powder

of aluminum (99% purity UNI-Chem), copper (99% purity Alfa Aesar), iron (99% purity PRS Panreac) and

boron (95% purity Sigma Aldrich) with nominal composition of Al65Cu23Fe11B (atomic %) (ACFB) were

taken in a RETSCH PM-200 planetary ball mill for mechanical alloying. The powder was milled for 50 hrs

and milling media (hardened steel balls) to powder ratio was set to be 1:10. The rotating speed ‘ωd’ was set

to 250 rpms. The cool down time was set to 5 minutes after every 15 minutes of continuous milling. The

milled powder was filled in die up to 80 % of its volume and cold pressed. The load applied during the cold

pressing was 4 tons. The dwell time for cold pressing was kept to 15 minutes. After the cold pressing

operation, die was transferred to the vacuum hot press where annealing performed at 680°C for 5 hrs. ACFB

quasicrystalline phase obtained from hot press was ground and leached in 5 wt% of Na2CO3 for 4 hrs. Then

suspensions of the leached ACFB powder samples were made in aqueous solution with the concentration

of 2.5 mg /µl. The antimicrobial properties of leached ACFB was investigated by agar diffusion test [23].

Kocuria rosea and Enterobacter aerogenes were used for determining the zone of inhibition of leached

ACFB. XRD was performed using D8 Bruker machine with Cu K-α.

Results and Discussion

The antimicrobial properties of ACFB quasicrystals were investigate by agar diffusion test. Alkaline

solution is used to prepare the antimicrobial surface. The structure of synthesized ACFB powder samples

were determine by X-ray diffraction (XRD) technique using Cu K-α as a source. Fig. 1 represents that

structure ACFB is icosahedral and remain intact after leaching. Minor phase of Fe3B phase is identified

before leaching. This phase can form by a reaction between iron and born which are present in the precursor

powder. Leaching does not change the icosahedral structure of quasicrystalline materials and from the

surface which contain Cu and iron.

The SEM images of ACFB quasicrystals were taken by using secondary electrons. Fig. 2 is showing the

SEM image of ACFB before and after 4hrs of leaching in alkaline solution. The image before leaching

shows a smooth surface because it is an un-leached surface. After leaching, it is quite easy to spot the

differences on the surface of the leached and the un-leached quasicrystal. The leaching process has removed

some of the aluminium and its oxide form the surface. There are islands visible on leached SEM images

which are very likely to be composed of copper and iron.

The true compositional nature of islands formed on the surface of the leached quasicrystals was confirmed

using energy dispersive spectroscopy (EDS) analysis. Table 1 is showing EDS analysis of ACFB samples

before and after 4hrs of leaching in 5 wt % of Na2CO3 alkaline solution. The results reveals that un-leached

sample has an aluminium rich surface. This is also consistent with the actual composition of the

quasicrystal. This, however, makes the quasicrystal a less effective antimicrobial agent. This is due to the

fact that copper, which is active specie in antimicrobial properties, is not present in large amount on the

surface in comparison with aluminium. On the other hand when quasicrystal sample is leached in 5 wt% of

Na2CO3 solution, the EDS result show that the quantity of copper on the surface is almost doubled. This

relative increase in copper quantity is attributed to the preferential leaching out of the aluminium in 5 wt%

Page 26: International Symposium on Advances in Metallurgy & Materials

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of Na2CO3 solution. This EDS result does confirm that copper rich islands forms on the leached quasicrystal

surface. This formation of islands on the surface is essential to the antimicrobial properties of the

quasicrystal. Fig. 3 is showing the effect of leaching on surface.

Fig. 1: Powder X-ray diffraction patterns of mechanically milled ACFB and leached for 4 hrs in 5 wt % of Na2CO3

Fig. 2: SEM images of spray deposited ACFB (a) and leached for 4 hrs (b) in 5 wt % of Na2CO3.

(a) (b

)

Page 27: International Symposium on Advances in Metallurgy & Materials

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Fig. 3: Effect of leaching on surface

Table 1: Result of EDS analysis of ACFB quasicrystals

Element Before leaching (Atomic %) After leaching (Atomic %)

Fe 8.3 19.8

Cu 37.0 57.5

Al 54.7 22.7

Inductive coupled plasma-optical emission spectroscopy (ICP-OES) analysis was conducted to study

the role of boron on leaching characteristics of ACFB. Table 2 shows the result of ICP-OES analysis

performed on the remaining alkaline solution of ACFB quasicrystals after 4 hrs of leaching. Addition of

boron stabilizes the quasicrystal and helps protect copper and iron during the leaching operation. Therefore,

boron doped quasicrystal will form copper rich leached surface.

Table 2: ICP-OES results from the leaching experiment

The antimicrobial properties of leached ACFB quasicrystals were determine by agar diffusion test.

Kocuria rosea and Enterobacter aerogenes microorganisms used for agar test. Fig. 4 shows the zone of

inhibitions of leached ACFB quasicrystals. Zone of inhibition is due to presence of Cu island on the leached

surface of ACFB [1].

Element ACFB / µg ACF / µg

Al 33694 28117

B 232 0

Cu 47 65

Fe 103 141

Page 28: International Symposium on Advances in Metallurgy & Materials

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Fig. 4: Zone of inhibitions Kocuria rosea (a) and Enterobacter aerogenes (b) of leached ACFB quasicrystals

Conclusions

XRD results show that icosahedral ACFB quasicrystals were successfully synthesized and the icosahedral

structure does not change during leaching in Na2CO3 alkaline solution. The surface after leaching becomes

Cu and Fe rich. Amount of Cu present on surface plays a vital role in antimicrobial properties. Leached

quasicrystals show antimicrobial properties so they have potential to serve as antimicrobial surface.

Acknowledgements

I would like to express my very great appreciation to Dr. Syed Mujtaba ul Hassan and Dr Mirza Jamil

Ahmad for their constructive suggestions during development of this research work.

References

1. Grass, G., C. Rensing, and M. Solioz, Metallic copper as an antimicrobial surface. Appl. Environ.

Microbiol., 2011. 77(5): p. 1541-1547.

2. U.S. Centers for Disease Control and Prevention webpage. Nov. 20.

3. Noyce, J., H. Michels, and C. Keevil, Use of copper cast alloys to control Escherichia coli O157

cross-contamination during food processing. Appl. Environ. Microbiol., 2006. 72(6): p. 4239-

4244.

4. Kelly, P., et al., Comparison of the tribological and antimicrobial properties of CrN/Ag, ZrN/Ag,

TiN/Ag, and TiN/Cu nanocomposite coatings. Surface and Coatings Technology, 2010. 205(5): p.

1606-1610.

5. Kubacka, A., et al., Tailoring polymer–TiO2 film properties by presence of metal (Ag, Cu, Zn)

species: Optimization of antimicrobial properties. Applied Catalysis B: Environmental, 2011.

104(3-4): p. 346-352.

6. Kubacka, A., et al., UV and visible light optimization of anatase TiO2 antimicrobial properties:

Surface deposition of metal and oxide (Cu, Zn, Ag) species. Applied Catalysis B: Environmental,

2013. 140: p. 680-690.

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7. Ren, G., et al., Characterisation of copper oxide nanoparticles for antimicrobial applications.

International journal of antimicrobial agents, 2009. 33(6): p. 587-590.

8. Shechtman, D., et al., Metallic phase with long-range orientational order and no translational

symmetry. Physical review letters, 1984. 53(20): p. 1951.

9. Bendersky, L., Quasicrystal with one-dimensional translational symmetry and a tenfold rotation

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