In recent years, pollution of soil, water and air has become a
serious problem not only in Vietnam but also in many parts of the
world in which the water pollution is more serious problem.
"Water blooming" is the development of microalgae outbreak,
especially cyanobacteria in fresh water bodies and often cause the
harmful effects on the environment such as: the water turbidity and
pH are increase, the levels of dissolved oxygen is reduce due to the
respiration or degradation of algae biomass and especially, the fact
that most cyanobacteria produce the toxicity high. The preventing
and minimizing the development of cyanobacteria is an important
environmental issue that need to pay the attention. The many
methods have been used such as: chemistry, mechanics, biology,
etc., but they are ineffective and expensive, affecting ecosystem
and conducting is difficult, especially in large water bodies.
Therefore, the search and development of new effective solutions
without secondary pollution and friendly with the environment are
increasingly focused research. Nanotechnology is the technology
relating to the synthesis and application of materials with
nanometer sizes (nm). At nanoscale, the material has many
advantage features such as: size is smaller than 100 nm, larger
surface to volume ratio, crystalline structure, high reactivity
potential, creating the effect of resonance Plasmon surface; high
adhesion potential and the nanomaterial was applied in various
fields such as: medical, cosmetics, electronics, chemical catalyst,
environment. For the above reasons, the thesis is proposed as:
“Synthesis of silver, copper, iron nanoparticles and their
applications in controlling cyanobacterial blooms in the fresh
water body” was selected to researched.
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TRAN THI THU HUONG
SYNTHESIS OF SILVER, COPPER, IRON
NANOPARTICLES AND THEIR APPLICATIONS IN
CONTROLLING CYANOBACTERIAL IN THE FRESH
WATER BODY
Major: Environmental Technique
Code: 9 52 03 20
SUMMARY OF ENVIRONMENTAL TECHNIQUE
DOCTORAL THESIS
HaNoi - 2018
MINISTRY OF EDUCATION
AND TRAINING
VIETNAM ACADEMY OF
SCIENCE AND TECHNOLOGY
GRADUATE UNIVERSITY SCIENCE AND TECHNOLOGY
---------------------------
The thesis was completed at the Graduate University of Science
and Technology, Vietnam Academy of Science and Technology
Scientific Supervisor 1: Assoc. Prof. Dr. Duong Thi Thuy
Scientific Supervisor 2: Dr. Ha Phuong Thu
Reviewer 1:
Reviewer 2:
Reviewer 3:
The dissertation will be defended protected at the Council for
Ph.D. thesis, meeting at the Viet Nam Academy of Science and
Technology - Graduate University of Science and Technology.
Time: Date month . 2018
This thesis can be found at:
- The library of the Graduate University of Science and Technology.
- National Library of Viet Nam.
1
INTRODUCTION OF THESIS
1. The necessary of the thesis
In recent years, pollution of soil, water and air has become a
serious problem not only in Vietnam but also in many parts of the
world in which the water pollution is more serious problem.
"Water blooming" is the development of microalgae outbreak,
especially cyanobacteria in fresh water bodies and often cause the
harmful effects on the environment such as: the water turbidity and
pH are increase, the levels of dissolved oxygen is reduce due to the
respiration or degradation of algae biomass and especially, the fact
that most cyanobacteria produce the toxicity high. The preventing
and minimizing the development of cyanobacteria is an important
environmental issue that need to pay the attention. The many
methods have been used such as: chemistry, mechanics, biology,
etc., but they are ineffective and expensive, affecting ecosystem
and conducting is difficult, especially in large water bodies.
Therefore, the search and development of new effective solutions
without secondary pollution and friendly with the environment are
increasingly focused research. Nanotechnology is the technology
relating to the synthesis and application of materials with
nanometer sizes (nm). At nanoscale, the material has many
advantage features such as: size is smaller than 100 nm, larger
surface to volume ratio, crystalline structure, high reactivity
potential, creating the effect of resonance Plasmon surface; high
adhesion potential and the nanomaterial was applied in various
fields such as: medical, cosmetics, electronics, chemical catalyst,
environment... For the above reasons, the thesis is proposed as:
“Synthesis of silver, copper, iron nanoparticles and their
applications in controlling cyanobacterial blooms in the fresh
water body” was selected to researched.
2. The objectives of the thesis
Research, fabricate and determine the characteristic of three
nanomaterials (silver, copper and iron) and evaluate the ability to
inhibit the cyanobacteria of nanomaterials in fresh water bodies.
3. The main contents of the thesis
- Fabricate and determine the characteristic of three
nanomaterials: silver, copper and iron.
2
- Investigate the ability to inhibit and prevent cyanobacteria of
three nanomaterials.
- Assess the safety of materials and their application.
- Experimental application of materials at laboratory-scale with
the Tien lake water sample.
5. The structure of the thesis
The thesis is composed of 149 pages, 10 tables, 62 figures, 219
references. The thesis consists of three parts: Introduction (3 pages);
chapter 1: Literature review (42 pages); chapter 2: Methodology (16
pages); chapter 3: Resutl and discussion (59 pages); Conclusion and
recommendation (2 pages).
CHAPTER 1. LITERATURE REVIEW
1.1. Introduction of nanomaterial
1.2. Introduction of Cyanobacteria and Eutrophication
1.3. Introduction of the methods to treat the toxic algae
contamination
CHAPTER 2. METHODOLOGY
2.1. The research subjects
2.2. The equipment is used in study
2.3. The methods for synthesis of materials
2.3.1. Synthesis of silver nanomaterial by chemical reduction
method
The silver nanomaterial was synthesized by chemical reduction
method, ion Ag
+
in the silver salt solution is reducted to Ag
0
by the
reducing agent NaBH4.
2.3.2. Synthesis of copper nanomaterial by chemical reduction
method
The copper nanomaterial was synthesized by chemical
reduction method, ion Cu
2+
in the copper salt solution is reduced to
Cu
0
by the reducing agent NaBH4.
2.3.3. Synthesis of iron magnetic (Fe3O4) nanomaterial by
simultaneously precipitation method
The iron magnetic (Fe3O4) nanomaterial was synthesized by
simultaneously precipitation method of Fe
2+
and Fe
3+
salts by
NH4OH.
2.4. The methods for determining the characteristic of material
structure
3
The morphology of the three nanomaterials is determined by a
number of methods such as: TEM, SEM, IR, XRD, UV-VIS, EDX.
2.5. The experimental setup methods
The experimental setup methods such as: culture of algae,
selection of nanomaterials, evaluation of the material toxicity, the
evaluation of the influence of nanomaterial sizes and the safety of
nanomaterials on microalgae and the experiment with the Tien lake
water sample were setup.
2.6. The methods of evaluating the effect of nanomaterials on
the growth of microalgae
To evaluate the effect of nanomaterials on the growth of
microalgae, the following methods such as: OD, chlorophyll a, cell
density, the methods for analysis of some environmental quality
indicators (NH4
+
, PO4
3-
) and SEM, TEM were used.
2.7. The method of statistical analysis
CHAPTER 3. RESUTL AND DISCUSSION
3.1. Synthesis of nanomaterial
3.1.1. Synthesis of silver nanomaterial by chemical reduction
method
3.1.1.1. Effect of the concentration ratio NaBH4/Ag
+
The UV-VIS spectrophotometer (Fig 3.1) showed that the
nanosilver colloid was absorbed at the wavelengths about 400 nm
and the synthesized efficiency of silver nanoparticles was
maximum achieved at a ratio 1:2. TEM images (Figure 3.2)
showed that silver nanoparticle size was less than 20 nm.
Figure 3.1. The UV-VIS spectra
of nanosilver colloid depends on
the NaBH4/Ag
+
concentration
ratios
Figure 3.2. The TEM images of
nanosilver colloid depends on
the BH4
-
/Ag
+
concentration ratio
M3 M4 M5
M1 M2
4
3.1.1.2. Effect of stabilizer concentration chitosan
The UV-VIS measurements in Figure 3.4 showed that the
nanosilver colloid is absorbed at the wavelengths 402-411 nm. The
TEM image of the silver nanoparticles depends on the
concentration of chitosan shown in Figure 3.5. The optimum
chitosan concentration of nanosilver colloid fabricating was chosen
as 300 mg/L.
Figure 3.4. The UV-VIS spectra
of nanosilver colloid depends on
chitosan concentrations
Figure 3.5. The TEM images
of nanosilver colloid depends
on the chitosan concentrations
3.1.1.3. Effect of citric acid concentration
The UV-VIS measurements in Figure 3.7 showed that the
nanosilver colloid is absorbed at the wavelengths 402-411 nm. At
the rate of [Citric]/[Ag
+
] = 3.0 the silver nanoparticles obtained
were of the most uniform, small size and less than 20 nm, the TEM
measurement is shown in Figure 3.8.
Figure 3.7. The UV-VIS
spectra of nanosilver colloid
depends on acid concentration
Figure 3.8. The TEM images of
nanosilver colloid depends on
the [Citric]/[Ag
+
] concentration
M6 M7
M8 M9 M10
M11 M12 M13
M14 M15 M16
5
Figure 3.9. The HR-TEM of nanosilver colloid was tested at
optimal ratio
The structure of silver nanoparticle at the optimum ratio indicates
that they have a typical hexagon crystal structure of metallic
nanoparticles. The HR-TEM images in Figure 3.9 showed that the
crystals has got Fcc (Face-centered cubic) structure. The silver
nanomaterial at the conditions such as: the ratio of NaBH4/Ag
+
is
1/4, the [Citric]/[Ag
+
] is 3.0 and a concentration of chitosan
stabilizer is 300 mg/L were synthesized to experimented the effect of
material on the growth of the studied subjects in the thesis.
3.1.2. Synthesis of copper nanomaterial by chemical reduction
method
3.1.2.1. Effect of the concentration ratio NaBH4/Cu
2+
The results in Figure 3.10 show that, in the XRD spectrum
appears the three peak with the intensity match for the standard
spectra of the copper metal at the side (111), (200), (220)
corresponding to angle 2θ = 43.3; 50.4 and 74.00 belong to the
Bravais network in the fcc structure of the copper metal.
Figure 3.10. The XRD pattern
of CuNPs were tested in
NaBH4/Cu
2+
concentration
Figure 3.11. The SEM images
of CuNPs in NaBH4/Cu
2+
ratio
The SEM measurements (Fig 3.11) of the material were
performed to determine the distribution of the copper particles and
M1 M2
M3 M4 M5
6
the TEM measurement for determine the size of copper
nanoparticles (Fig 3.12).
Figure 3.12. The TEM images
of CuNPs in NaBH4/Cu
2+
ratio
Figure 3.13. The XRD
spectrum of CuNPs was tested
by Cu
0
concentration
The TEM image results showed that, when the NaBH4/Cu
2+
concentration ratio is 1: 1 and 1.5: 1, the size of synthesized copper
nanoparticles are bigger than 50 nm. The nanoparticles are
distributed rather uniformly with a size about 20-50 nm when the
NaBH4/Cu
2+
ratio is 2 : 1. The nanoparticles are clumped together,
unevenly distributed with the size nanoparticle > 50 nm when the
NaBH4/Cu
2+
ratio is 3: 1 and 4: 1 and match with the SEM results.
To respone the objective of this thesis, the M3 sample
(NaBH4/Cu
2+
ratio is 2: 1) was chosen as the representative sample.
3.1.2.2. Effect of Cu
0
concentration
XRD spectrum in Figure 3.13 showed that the of copper
nanoparticles presents the characteristic peaks of copper
nanomaterial. The characteristic peaks on the schematic have the
sharpness intensity and the wide range of the absorption peak
relatively narrow. In addition, the XRD spectrum of the material
also shows the characteristic peaks of CuO, Cu2O crystals.
The SEM (Fig 3.14) measurement results showed that, the
copper nanoparticles form of the unequal size distribution when the
concentration of Cu
0
increases. At concentrations of Cu
0
is 2g/L,
the copper nanoparticles are distributed rather uniformly with the
size at 20-40 nm. When the concentration of Cu
0
increases to 3;
4g/L, the synthesized copper particles will clump together and
form of the particle sizes >50 nm; at Cu
0
concentration is 6, 7 g/L,
M1 M2
M3 M4 M5
7
the nanoparticles distributed unevenly and match for the TEM
measurement (Fig 3.15).
Figure 3.14. The SEM image of
copper nanomaterial was tested at
Cu
0
concentration
Figure 3.15. The TEM image
of copper nanomaterial was
tested at Cu
0
concentration
a) b)
Faculty of Chemistry, HUS, VNU, D8 ADVANCE-Bruker - Cu-51
01-085-1326 (C) - Copper - Cu - Y: 16.13 % - d x by: 1. - WL: 1.5406 - Cubic - a 3.61500 - b 3.61500 - c 3.61500 - alpha 90.000 - beta 90.000 - gamma 90.000 - Face-centered - Fm-3m (225) - 4 - 47.2416 - I/Ic PDF 8.9 - F4
1)
File: ThuyVCNMT Cu-51.raw - Type: 2Th/Th locked - Start: 1.000 ° - End: 79.990 ° - Step: 0.030 ° - Step time: 0.3 s - Anode: Cu - WL1: 1.5406 - Generator kV: 40 kV - Generator mA: 40 mA - Creation: 06/10/2016 3:54:39 P
Left Angle: 42.490 ° - Right Angle: 44.350 ° - Obs. Max: 43.281 ° - d (Obs. Max): 2.089 - Max Int.: 1890 Cps - Net Height: 1668 Cps - FWHM: 0.231 ° - Raw Area: 852.6 Cps x deg. - Net Area: 440.4 Cps x deg.
L
in
(
C
p
s
)
0
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500
600
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1300
1400
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2-Theta - Scale
1 10 20 30 40 50 60 70 80
d
=
2
.0
8
9
d
=
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.8
0
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d
=
1
.2
7
8
c)
Figure 3.16. The detail characteristics of the N1 copper
nanomaterials sample: (a) SEM image, (b) TEM image, (c) XRD
spectrum
The structure of copper nanomaterial at selected ratio showed
that, the formed copper nanoparticles have the rather
homogeneous surface (SEM image, Fig 3.16a), the uniformly size
in the range of 30 - 40 nm (TEM image, Fig 3.16b) and have the
Fcc structure with diffraction peaks of the netface (111), (200) and
(220) corresponding to angle 2θ = 43.3; 50.4 and 74.00 with high
intensity (XRD spectrum, Fig 3.16c). This material sample is
suitable with the objective of the thesis and were choosen for
further experiment.
N1 N2
N3 N4 N5
N1 N2
N3 N4 N5
8
3.1.3. Synthesis of magnetic solution nanomaterial by co-
precipitation method
3.1.3.1. Effect of the CMC stabilizer concentration
The tested result of morphological, size and the dispersion of
material in the ratio of CMC stabilizer and precursor (Fe3O4)
respectively were 1/1; 2/1; 3/1; 4/1 and 1/2 by the SEM and
methods shown in Figure 3.17 and 3.18. The SEM result showed
that the concentration of CMC in the solution is high, the
ferromagnetic nanoparticles are unevenly and the particle size is
big, the accumulation of nanoparticles is easy to occur. At the rate
of CMC/Fe3O4 is 2/1, the obtained ferromagnetic nanoparticles are
uniformly sized and less 20 nm.
Figure 3.17. The SEM image of
magnetic solution nanostructure
tested in ratios of CMC/Fe3O4
Figure 3.18. The TEM image of
magnetic solution nanostructure
tested in ratios of CMC/Fe3O4
The TEM results showed that the nanoparticle size varies
considerably when the CMC concentrations changed. When the
Fe3O4/CMC is 2:1, the obtained nanoparticles were the smallest,
most uniform and less than 20nm within the superparamagnetic size
range. Therefore, the material sample has a Fe3O4/CMC ratio of 2:1
(encoded sample is FC21) selected to tested for the further factors.
3.1.3.2. The result of infrared measurement of the material
Figure 3.19. The infrared spectrum
of Fe3O4 (a), CMC (b), FC21 (c) and
spectrum of three samples (d)
Figure 3.20. The
magnetization hysteresis
result of material FC21
9
The observation in Figure 3.19 showed that the IR spectrum of
ferromagnetic nanoparticles have peaks similar with CMC and
Fe3O4, this proves that the structure of CMC is not broken by the
material synthesis conditions. Therefore, the co-precipitation
method for synthesis of material is suitable for purity as well as
efficiency.
3.1.3.3. The magnetization hysteresis result of material
The result of saturate magnetization hysteresis measurement in
Figure 3.20 showed that ferromagnetic nanoparticles are in the
form of superparamagnetic. The saturate magnetization of Fe3O4
and FC21 is 68 emu/g and 49 emu/g, corresponding to the content
of magnetic phase of the material. The result proves that the
surface interaction of the magnetic phase with the polymer
decreased the saturate magnetization and suitable with the results
of the TEM analysis.
3.2. Evaluating the ability of growth inhibition and prevent
microalgae by synthesized nanomaterials
3.2.1. Study on the selection of concentrations of three types of
nanomaterials
Table 3.1. The screening results of removal M. aeruginosa KG
cyanobacteria of fabricated nanomaterials
No. Samples
Experimental
concentration (mg/L)
The growth
inhibition of
cyanobacteria
1 Ag nano 3, 5 and 10 +++
3 Cu nano 3, 5 and 10 +++
5 Fe3O4 nano 5, 10, 100, 150 and 200 -
6 Control 0 -
Notes: +++: Very strong inhibitory effect, ++: Strong inhibitory effect, +:
Normal inhibitory effect, -: Non inhibitory effect.
Figure 3.21. Effect of nanomaterials on growth of cyanobacteria M.
aeruginosa KG after for 7 days.
10
The concentration screening tests were conducted to rapidly
assess inhibition effect to M. aeruginosa KG for 7 days. The
results in Table 3.1 and Figure 3.21 showed that the two silver and
copper nanomaterials inhibited the growth and development of
cyanobacteria M. aeruginosa KG after 6 days (Table 3.1 and Fig
3.21a, b), whereas that the ferromagnetic nanomaterial were not
effective against M. aeruginosa KG (Table 3.1 and Fig 3.21c).
3.2.2. Effect of silver nanoparticles on growth and development
of cyanobacteria M. aeruginosa KG and green algae C. vulgaris
3.2.2.1. Effect of silver nanoparticles on growth and development
of cyanobacteria M. aeruginosa KG
The experiments were conducted with the concentrations of
silver nanoparticles increasing from 0; 0.001; 0.005; 0.01; 0.05; 0.1
to 1 ppm in 10 days. The evaluation parameters include: optical
density (OD), chlorophyll a and cell density at 0, 2, 6 and 10 days
(Fig 3.22a, b). The toxicity of silver nanoparticles on growth of the
cyanobacteria M. aeruginosa KG as measured by the concentration
of supplementary material into the culture medium that affected
50% of the individuals (EC50) was 0.0075 mg/L.
Figure 3.22. Effect of silver
nanomaterial on growth of the
cyanobacteria M. aeruginosa
KG after 10 days was
measured by (OD) (a),
chlorophyll a (b)
Figure 3.23. Effect of silver
nanomaterial was measured by
the cell density (a) and the
growth inhibition efficiency on
cyanobacteria M. aeruginosa
KG (b)
The cell density and chlorophyll a showed that, the cell density
and biomass in the control sample increased from the first day (D0)
(110,741 ± 6,317 cells/mL and 1.98 ± 0.06 μg/L, respectively) to the
end of experiment (D10) (5,475, 556 ± 541,274 cells/mL and 23.4 ±
2.96 μg/L, respectively) (Fig 3.23a). All five tested concentration
ranges are toxic to cyanobacteria M. aeruginosa KG. The growth
11
inhibition efficiency (Fig 3.23b) > 75% appears in only 4 tested
concentrations from 0.01; 0.05; 0.1 and 1 ppm.
The SEM image result of cell surface structure after 48h exposed
to silver nanoparticles at the concentration of 1 ppm is shown in
Figures 3.24a (the control sample) and 3.24b (the sample exposed to
the concentration of 1ppm silver nanoparticles). In the control sample,
the morphological of cyanobacteria M. aeruginosa KG cells
maintained a round and had a spherical shape with a smooth exterior
surface (Fig 3.24a). In the experimental sample, the cells were
changed to with a distorted and shrunk cell after exposure to silver
nanoparticles (Fig 3.24b). It is said that the silver nanoparticles have
significantly altered the morphology of the cell.
Figure 3.24. Scanning Electron
Microscopy (SEM) micrograph of
M. aeruginosa KG
Figure 3.26. Transmission
Electron Microscopy (TEM)
micrograph of M. aeruginosa KG
The SEM combined with EDX analysis was used to
characterize the chemical composition and the location of AgNPs
on the cell surface of M. aeruginosa KG. The EDX result in Figure
3.25 showed that the silver nanoparticles appear on the surface of
the cyanobacteria M. aeruginosa KG with 0.37% Ag by weight.
The TEM image in the control sample (Fig 3.26a), the M.
aeruginosa KG ultrastructure image had clearly cell wall and the
organelle lie neatly in the cell. When exposed to silver
nanoparticles at a concentration of 1ppm after 48 hours, the
cyanobacteria cells were destroyed (Fig 3.26b). It is proved that the
silver nanoparticles was affected to structure of the cyanobacteria
M. aeruginosa KG cell.
Elements % Weight % Element
C K 38.69 55.90
O K 30.59 33.18
Na K 1.95 1.47
Al K 6.02 3.87
Cu L 11.82 3.23
Ag L 0.37 0.06
a) b) a) b)
12
Totals 100.00
Figure 3.25. The EDX spectrum and the element composition
appear on the cell surface of M. a