Synthesis of silver Nanoparticles using Azadirachta indica (Neem) extract and usage in water purification
N.Namratha*
and Monica P.V.
Department of Chemical Engineering, SSN
College of Engineering, Kalavakkam, Chennai, 603 110,
India
*Corresponding Author E-mail:- namrathassn@gmail.com,
monicavasan@gmail.com
ABSTRACT
Nanotechnology is a developing field while reducing the matter on
atomic and molecular scale sized between 1 to 100 nanometre in one dimension. This technology recently
attracted various branches of application due to the dissimilar behaviour of
the bulk material when reduced to its nano-size. One
such application is the use of the nano structured
material as adsorbents or catalysts to remove the toxic and harmful substances
from air water. In this paper, the green synthesis of Silver Nanoparticles using Azadirachta indica (Neem) extract at room
temperature is discussed along with the application of anti bacterial
properties in water treatment. An aqueous solution of silver nitrate (AgNO3)
was treated with neem leaf extract and the formation
of crystalline structure was confirmed using UV spectrometer and X-ray
diffraction analysis. The Scanning and Transmission Electron Microscope results
confirmed that the morphology and size of the nanoparticles
were strongly dependent on number of process parameters such as reactants
concentration, reaction pH, mixing ratio of reactants and interaction time of
the reactants etc. To develop a filtrate system for water purification, the
synthesized nanoparticles were coated on Polyurethane
foams (PU) by overnight exposure to the aqueous solution. Several rounds of
washing and air drying resulted in stable PU foam with uniform coating. The
morphology of the foam was not altered after coating. The common bacteria
Escherichia coli of 105 colony-forming units (CFU) per mL
were prepared to be used as input water. The coated PU filter was soaked in
this water for about 10 minutes and the analysis of the output water had shown
the reduction in bacterial population. As the drinking water contamination with
E-Coli is predominant in third world countries and the low cost of Neem extract due to it abundant availability and also the
green synthesis without any toxic chemical will find great application in water
treatment.
KEYWORDS: Silver nanoparticle, Azadirachta indica (Neem), Water purification, Polyurethane foam.
1. INTRODUCTION:
A variety
of synthesis techniques have been developed including chemical reduction of
silver ions in aqueous solutions, with or without stabilizing agents, thermal
decomposition in organic solvents and chemical and photo reduction in reverse
micelles. These methods are not only expensive and also involve toxic,
hazardous chemicals which may pose potential environmental and biological
risks. The use of leaf extracts, bacteria and fungi for the synthesis of silver
nanoparticles offers numerous benefits as they are
compatible for biological application with zero chemical toxicity on the
application and environment. They are eco-friendly and well-suited for
pharmaceutical and biomedical applications as they do not contain toxic
chemicals in the synthesis process.
This kind
of environmentally sustainable synthesis process has led to few bio-mimetic
approaches which refer to applying biological principles in materials formation
such as bio reduction. Numerous
inorganic nanomaterials have been synthesized by bio
reduction processes using various microorganisms like Pseudomonas stutzeri, Verticillum, Fusarium oxysporum, Aspergillus flavus etc. The usage of botanical materials for the
synthesis of nanoparticles shall be advantageous
over other biological processes since the tedious process of maintaining the
microbial culture is avoided. Moreover this method is cost effective over chemical
and physical methods and environment friendly. Since there is no need to use
high pressure, energy, temperature and toxic chemicals, the technology is very
simple. Neem leaves extract was chosen for the present
study, because-
(i) Neem is a quite commonly available plant and
abundant in nature
(ii) Excludes addition of external stabilizing
agent during synthesis and
(iii) It offers synergistic effects to enhance
the antimicrobial properties of the synthesized silver nanoparticles
(one of the major end uses).
The UV spectroscopy analysis proved that
the formed particles were silver nanoparticles in the
wavelength ranging from 405 nm to 425 nm. The X-ray diffraction analysis
confirmed the formation of crystalline silver nanoparticles.
The Scanning and Transmission Electron Microscopy techniques revealed that the
morphology and size of the nanoparticles were
strongly dependent on the process parameters like reductant
concentrations, reaction pH, mixing ratio of the reactants and interaction time
of the reactants. Since water medium is the common breeding ground for many
pathogens, the presence of bacteria is the main indication of water contamination. It is recommended that any water
intended for drinking should not contain fecal contamination and the total coliform counts shall be reduced. The removal or
inactivation of pathogenic microorganisms is the last step in the treatment of
water. In conventional methods, chemical and physical agents, such as chlorine
and its derivatives, AgNO3, ultraviolet light and radiation, are commonly used.
The application of nanoparticles for water
disinfection is relatively new. This will be a cutting edge technology because
of the high reactivity due to the large surface to volume ratio of nanoparticles. This single aspect will play a crucial role
in water purification as drinking water is an essential commodity for the well
being and the survival of the society. An attempt is made through this study to
establish the antibacterial properties of the polyurethane foam coated with synthesised silver nanoparticles.
The common
polyurethane (PU) foams can be coated with Silver nanoparticle by overnight
exposure of the foams to nanoparticle solutions.
Cyclic washing and air-drying yields uniformly coated PU foam. The coating of Nanoparticles is stable on
the foam and is not leached by continuous water contact. These coated foams can
be used as a water filter. E. coli,
the most common bacteria in the drinking water was chosen in this study as indicators of fecal contamination. The
input water had a bacterial load of 105 colony-forming units (CFU)
per mL in which contact time of PU foam in water was
of the order of 10 minute, the output count of Escherichia coli got significantly reduced. The
low cost and high efficiency and the simplicity of this technology will be be of great attraction
in developing countries for countering waterborne diseases and public
health.
2.
EXPERIMENTAL:
2.1. Synthesis
of silver nanoparticles:
The Fresh Neem leaves were thoroughly washed and finely cut and again
washed with distilled water. 25 g of the leaves were added to 100 mL of deionised water and boiled
for one hour in a water bath. The mixture was filtered to obtain aqueous
extract of 20 % concentration. The prepared neem leaf
broth was interacted with 0.01 M AgNO3 solution at 1:4 mixing ratio
to make up 100 mL volume in 250 mL
Erlenmeyer flask for synthesis of silver nanoparticles.
Dilute Ammonium Hydroxide (NH4OH) was used to maintain the pH of the
reaction mixture in the range of 8. The flask was kept for 4 h in rotary shaker
at 80 rpm to achieve homogenous reaction. The dry powders of the silver nanoparticles were obtained after 4 h of reaction period.
The colour change from silver nitrate solution to
reduced silver nanoparticles is indicated in Fig.1.. The broth containing
silver nanoparticles was centrifuged at 7,000 rpm for
15 min. Thereafter, the particles were re-dispersed in sterile distilled water
to get rid of any uncoordinated biological molecules. The same process was
repeated three times to ensure better separation of free entities from the
metal nanoparticles. The purified particles were
dried using a hot air oven up to 70oC. Solid silver nanoparticles obtained are shown in the Fig.2. A rough
prediction of the reaction that takes place during the process has been given
as Neem broth + AgNO3 solution → Ag nanoparticles
2.2.
Fabrication of silver-coated polyurethane foams:
Polyurethane
(PU) foams of 10cm x 10cm x 5mm size was washed by deionised
water, dried and then soaked in silver colloidal solutions for a day. In order
to eliminate the adsorbed substances and impurities the sheets were washed
repeatedly with water. It was found the coatings of nanoparticles
were stable on the foam and not washed away by water on repeated washing. Also,
the morphology of the foam was retained even after coating. The binding of nanoparticle was due to its interaction with the nitrogen
atom of the PU. The following reaction takes place when PU foam is soaked in Ag
nano solution:
- NH-(C=O)-O- + Ag → -N- Ag+-(C=O)-O-
2.3.
Microbiological Experimentation:
The
contaminated water was analysed and found to contain
following bacteria like E.coli, staphylococcus,
clostridium, streptococcus species like dysnteriae, pyogenes, salmenela species, proteus
species, pseudomonas species, and shigella species. E.coli, Staphylococcus aureus
(gram positive bacterium) and Pseudomonas aeruginosa
(gram negative bacterium) were selected as major indicators of bacterial contamination of water. Nutrient broth was
used as the growing medium for the microorganisms. Bacteria were grown
aerobically in nutrient broth at 30oC for 15 h. The cultures were
centrifuged, the cells were washed and suspended in distilled water, reaching a
final concentration of 1 x 105 to 1 x 106 CFU/mL.
2.4.
Test Tube Analysis:
For the test tube analysis, 20 mL of E.Coli, Staphylococcus aureus and Pseudomonas aeruginosa
cells each suspended in sterile water was taken in sterilized falcon test tubes
separately. 10cm x10cm x 5mm pieces of the foam was put into the tubes. These
tubes were incubated in an orbital shaker at 30°C and 100 rpm. After 30 min,
the foam samples were taken out from the tubes. The liquids were collected at
the end of incubation; plating was done with this treated water by serial
dilution method for 100, 10-3 and 10-5
dilutions with trytpic soy agar (TSA). Plating was
also done for the initial CFU count and with uncoated PU-treated solution. For
every dilution, 10 µL of the solution were plated. Plating was done by the wet
plate method. The bacterial colonies were counted after 48 hours of incubation
at 30°C.
3.
RESULTS AND
DISCUSSIONS:
3.1. Characterization
of silver nanoparticles:
a)
XRD Analysis
X-Ray
Diffraction analysis is the most useful method by which X-Rays of a known
wavelength are passed through a sample to identify the crystalline structure.
The X-Rays are diffracted by the lattice of crystal to give a unique pattern of
peaks of 'reflections' at different angles and of different intensity, just as
light can be diffracted by a grating of suitably spaced lines. The phase
identification of the silver nanoparticles was also
carried out by X-ray diffraction method. The sample was grounded using a mortar
and pestle into powder. X-ray powder diffraction measurement was carried out by
using Philips X`Pert MPD powder diffractometer
with long fine focus Cu anode operated at 40 KV and 30 mA
in Bragg-Brentano geometry.
Fig.3 XRD analysis of the silver nanoparticles
The X-Ray detector moves around the sample
and measures the intensity of these peaks and the position of these peaks
[diffraction angle 2θ]. The highest peak is defined as the 100% peak and
the intensity of all the other peaks are measured as a percentage of the 100%
peak. The powder XRD data were obtained in the 2q range from 10° to 80° in step-scan
mode with 2q step of 0.02°. The X-ray diffractometer was calibrated by means of external silicon
standard, SRM 640a. The diffraction pattern indicated
that the sample is the silver nanoparticles. The
conversion of silver nitrate to silver nanoparticle
was greater than ninety percent and smaller peaks contributed to neem extract impurity. The XRD pattern of the mixture is
shown in the Figure.3.
b)
TEM Analysis
The silver nanoparticles synthesised from
AgNO3 solution and Neem leaf broth was analysed for its size in TEM. Mostly spherical and near spherical
shapes of silver nanoparticles can be observed for
interaction time 4 h in 20 nm size range. The image of the silver nanoparticles is shown in the Figure.4.
Fig.4
TEM images of the silver nanoparticles
c) SEM
Analysis
To gain further insight into the features
of the silver nanoparticles, analysis of the sample
was performed using SEM method. The freeze-dried silver nanoparticles
were mounted on specimen stubs with double-sided adhesive carbon tape, coated with Au/Pd
alloy to make the surface conducting in a sputter coater (BAL-TEC SCD-005), and examined under a
Philips XL-30 SEM at 12-16 kV with a tilt angle of 45o. Scanning
electron microscopy provided the morphology and size details of the silver nanoparticles. The experimental results showed that the
diameter of prepared nanoparticles were in the range
of 20 nm to 100 nm. The SEM image of the silver nanoparticles
is given in Fig.5.
Fig.5 SEM image of a single silver nanoparticle
d) UV
Analysis
Figure.6
shows the UV spectra of the silver colloid in the range 400 nm – 425 nm. UV
absorption spectra has proved to be quite sensitive to the formation of silver
colloids because silver nanoparticles exhibit an
intense absorption peak due to the surface Plasmon (it describes the collective
excitation of conduction electrons in a metal) excitation. The absorption band
in visible light region (350 nm – 550 nm, Plasmon peak at 425 nm) is typical
for silver nanoparticles. The Plasmon peak and the
full-width of half-maximum (FWHM) depends on the extent of colloid aggregation.
To monitor the stability of silver colloid, the absorption of the colloid was
measured after different periods of time. There was no obvious change in peak
position for a month, except for the increase of absorbance. As the particles
increase in the size, the absorption peak usually shifts toward the red
wavelengths. The stable position of absorbance peak indicates that newly formed particles do not aggregate.
Fig.6 UV Spectra of Silver Nanoparticles
There are
two types of PUF material shown in Fig.7.. The first
picture (Fig.7A.) shows pure polyurethane foam and it is white in colour. The second picture (Fig.7B.) is silver nanoparticles coated polyurethane foam and the colour changes from white to golden yellow.
(A) (B)
Fig.7. Pure
polyurethane (PUF) (A) and PUF coated with silver nanoparticles
(B).
4.
Microbiological
Results:
After a contact time of 30 min
with silver nanoparticles coated PU, the bacterium
quantity detected was zero in the treated water. For E. Coli, Staphylococcus aureus and Pseudomonas aeruginosa
strains, the output count was nil for all the dilutions. The water treated with
the Control sample (pure PU) showed substantial growth on the plates. Initial
water sample (input) showed overgrowth in almost all the cases. The bacterium
count was decreased in the output water after passing through the coated foam
for E. coli, Staphylococcus aureus and Pseudomonas
aeruginosa. This was checked for input loads of 1
x 105 and 1 x 106 CFU/mL. There
was no growth below the PU coated with nanoparticles
while growth was seen in case of pure PU, which again confirms the
antibacterial property of PU coated with silver nanoparticles.
Figure 8A shows the bacterial growth seen in water treated with pure PUF.
Figure 8B and 8C show the immersion of Silver nanoparticles
coated PUF and the growth of bacteria in that treated water.
Fig.
8:
(A) Bacterial growth seen after plating treated water with pure PUF; (B) FALCON
test tube containing silver nanoparticles coated PUF
in contact with bacterial water; (C) Zero bacterial growth seen in treated
water with silver coated PUF after plating
The
following table gives an idea about the antibacterial effect of silver coated
polyurethane foam on various kinds of bacteria
Table.1.
Reduction in bacterial counts in PU foam coated with silver nanoparticles
S No |
Bacterial strains |
Polyurethane foam (PU)* |
|
Pure PU |
Coated PU |
||
1. |
Staphylococcus aureus
(Gram positive bacterium) |
6.0 x 106 CFU / ml |
Nil |
2. |
Pseudmonas
aeruginosa (Gram negative bacterium) |
1.0
x 107
CFU / ml |
Nil |
3. |
Escherichia coli (Gram negative bacterium) |
3.0 x 106 CFU / ml |
Nil |
5. CONCLUSION:
The
following conclusions were drawn after the completion of the experiments.
a) It was
found that the shape and size of the nanoparticles
produced through bio reduction by Neem leaves extract
were strongly dependent on the process parameters like Neem
broth concentration, mixing ratio of Neem extract to
AgNO3 solution, interaction time and pH of the solution.
b) It was
determined that the minimum interaction time was about 4 hours to obtain the nanoparticles with nearly spherical shape of size below 50
nm.
c) It was
confirmed from XRD analysis that there was full conversion of silver nitrate to
silver nanoparticle and bio-organic components from Neem leaf broth acted as probable stabilizer for the silver
nanoparticles.
d) With 24
hours of soaking, the silver nanoparticles coating
was found to be stable with PU and did not get washed away after repeated
washing and drying.
e) For a
treatment of 30 minutes, the silver nanoparticles
were found to have the stable binding with PU and did not get mixed with water.
f) With the
input bacterial load of 1 x 105 – 1 x 106 CFU/mL, the performance of the material was checked for its
antibacterial properties and efficient removal and the bacterium count was zero
in the treated water.
g) It was found that the coated Pu can remove all types of bacteria i.e., gram positive and
gram negative bacteria.
h) The life
cycle of the coated PU was tested for 25 times and found to function with the
same efficiency.
i) The
method employed here is a biomimetic approach and the
chemicals involved in the synthesis of nanoparticles
are non-toxic, commonly available and cost effective.
As the
chemistry involved in the preparation of nanoparticle-coated
foams is very simple, it can be scaled up to industrial application without the
involvement of high pressure or temperature. These qualities make this
technology adaptable to underdeveloped nations where bacterial contamination is
the principal issue in drinking water.
Received on 14.09.2013 Accepted on 03.10.2013
© Asian Pharma
Press All Right Reserved
Asian J. Pharm.
Tech. 2013; Vol. 3: Issue 4, Pg 170-174