Lithuanian Journal of Physics, Vol. 51. No. 3, pp. 248–259 (2011)
© lietuvos mokslų akademija, 2011
GENERATION OF METAL NANOPARTICLEs BY LAsER ABLATION
V. Dudoitis, V. Ulevičius, G. Račiukaitis, N. Špirkauskaitė, and K. Plauškaitė
State Research Institute Center for Physical Sciences and Technology, Savanorių 231, LT-02300 Vilnius, Lithuania
E-mail: ulevicv@ktl.mii.lt
Received 2 June 2011; revised 11 July 2011; accepted 21 September 2011
he process of nanoparticle generation during nanosecond and picosecond laser ablation of various metals
(Ni, Al, W and stainless steel) in ambient air and argon gas was investigated. he number concentration of nanoparticles generated by laser ablation in argon gas was up to 100 times higher compared to the concentration
in ambient air. hree stable separate size peaks of nucleation, Aitken and accumulation modes of nanoparticles
were observed in case of argon gas, while in ambient air particles of a wide size spectrum (8–200 nm) were
generated. he natural precursors in ambient air can have an efect on size spectrum of the particles composed
of various chemical compounds with target material during the ablation process. he inluence of laser process
parameters and properties of investigated metals on the number concentration and size distribution of nanoparticles generated during ns- and ps-laser ablation was observed.
Keywords: nanoparticles, nanosecond and picosecond laser ablation, metals, size distribution, number
concentration, ambient air, argon gas
PACs: 52.38.Mf, 78.70.-g, 81.10.St
1. Introduction
Comprehension of the aerosol formation as inevitable process in laser micromachining technology is
established and the application of laser ablation in
production of nanoparticles is widely spread. However, characteristics of particles generated by laser
ablation are not fully known. herefore, the studies
of particle concentration and their size distribution
are hot topics in current laser ablation investigations recently [1–9]. Nanoparticle generation by
laser ablation is used for a variety of applications
such as biotechnology, electronic industry, etc. he
laser ablation is also an intensive source of submicron particle generation and their possible leakage
into ambient air therefore investigations of the particle formation kinetics in ambient air, during laser
processing are essential for the evaluation of potential generation of particle emission and their impact on human health [7]. For example, during laser processing particles formed of metals (e. g. iron,
aluminum), especially toxic (e. g. manganese, zinc)
or carcinogenic substances (e. g. chromium (VI)
compounds, nickel), might penetrate into a human
organism and cause health concerns [8, 9].
he physical process of particle generation begins with the absorption of laser irradiation in the
beam/material interaction zone. Depending on
the wavelength of the laser beam and the material
properties, kinetic energy is transformed into thermal (in metals 10–13 s) [10], which cuts of chemical
bonds in material. he phase transition occurs if
the energy threshold for that material is reached. As
a result, material can be melted, vaporized or sublimated and the particle generation process begins.
Both the particle concentration and size distribution depend on laser operating parameters such
as wavelength, pulse duration, energy and repetition
rate, beam scanning speed. [3, 7, 10, 11]. Studies show
that experimental conditions during laser ablation
could be established in order to control the particle size and distribution [1, 3]. Besides, the medium
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(ambient air, argon, water, etc.) in the ablation
chamber also plays an important part in the particle
formation process. It was experimentally estimated
that the mass of generated nanoparticles in ambient
air was up to 100 times higher than in water [3].
he aim of the study was to investigate the peculiarities of nanoparticle formation during laser ablation of diferent metals (nickel, aluminum, stainless
steel, tungsten) and to characterize the diference
of size distribution of the generated particles in
respect of the laser irradiation type (nanosecond,
picosecond) and media in the ablation chamber
(partially particle-free ambient air, argon gas).
2. heoretical background
During During the interaction of the laser beam and
material, the light absorption is a general physical
process [11–13]. he energy coupled into material
causes thermal heating, melting and vaporization of
material, plasma formation and particle emission.
In metals, free electrons interact with the intense
electromagnetic irradiation. he energy is instantly
absorbed by electrons and further distributed to
the lattice. he laser pulse duration τL is important
for understanding what happens with the energy in
the beam / material interaction zone.
is the
lattice heating time,
is the electron cooling
time, where Ce and Ci are electron and lattice thermal capacities, respectively, and γ is the electron–
lattice coupling parameter speciic to every material. Based on the two-temperature difusion model
by Chichkov et al. [13] the laser beam/material interaction can be described by electron and lattice
subsystem temperatures Te and Ti, respectively:
,
,
(1)
(2)
where Q(z) is the heat lux, S is the heat source (laser pulse).
For picosecond pulses, condition τe << τL << τi is
fulilled. he laser pulse duration is shorter than
the lattice heating time. Particles from the material
are removed partly by solid state – vapor transition
and direct breaking of chemical bonds. For picosecond pulses (Eq. (1)) the electron temperature Te
becomes quasi-stationary:
,
(3)
where ke is the electron thermal conductivity, α is
the absorption coeicient, Ia is the laser intensity
transmitted to the material, z is the depth of laser
beam penetration into material perpendicular to
the surface. In this case, lattice temperature Ti is
,
(4)
where T0 is the initial electron temperature.
Taking this into account Eq. (4) can be simpliied due to quasi-stationary condition of electron
temperature:
,
(5)
where t is the time ater the laser exposure. It means
that electron cooling temperature Te stays longer
than lattice heating temperature Ti ater exposure
to picosecond laser pulses. Electron cooling temperature Te at the end of the pulse is
.
(6)
Lattice heating temperature Ti at the end of the laser pulse is
,
(7)
where Fa is the absorbed laser luence, which is
Fa = IaτL. By using the condition of strong evaporation it can be described as
Fa ≥ Fth exp (αz),
(8)
where Fth is the threshold laser luence for evaporation.
Equations (6)–(8) describe how laser intensity,
material transmissivity and thermal capacities inluence the temperature of the electron and lattice.
In the second case for nanosecond pulses, condition τL >>τi >> τe is fulilled. Equations (1), (2) for
nanosecond pulses are:
,
(9)
where k0 is the conventional equilibrium thermal
conductivity of a metal and T represents general
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temperature of the subsystem, because in case of
ns-laser ablation Te = Ti = T.
he energy absorbed by electrons is fully transferred to the lattice during the laser pulse duration.
Material is heated due to the absorbed energy of
the lattice. In this case, solid material melts, the
beam/interaction zone spreads and particles are
evaporated from liquid state. Metals have good
thermal conductivity properties, thus increasing
energy loss due to lattice heating for nanosecond
pulses.
3. Experimental set-up
he experimental set-up is schematically shown in
Fig. 1. he main parts are: the laser, the galvoscanner for laser beam control and an ablation chamber, a diferential mobility particle sizer (DMPS)
(ELAS-05MC, working range: 10–200 nm) and the
condensation particle counter (CPC) (UF-02, cutsize at 4.5 nm). Both devices are developed at the
Institute of Physics (Lithuania) [14, 15].
Laser ablation was carried out using two diferent Nd : YAG lasers: nanosecond (ns) (Ekspla Ltd.,
NL640, λ = 1064 nm, 15 ns) and picosecond (ps)
(Ekspla Ltd., PL10100, λ = nm, 10 ps).
Materials chosen for the investigation were the
following metals: stainless steel, nickel, aluminum
and tungsten. he experiments were performed in
the ablation chamber at atmospheric pressure with
a constant low of partially particle-free ambient air
which was processed through a HEPA ilter. It cleaned
gas low from particles up to 5 nm. In case of argon,
the gas was delivered into the chamber from a pressurized tank at a constant low rate of 3 000 cm3/min.
he exhaust low was divided for the CPC and DMPS
measurements. In case of argon, only DMPS was
used. he aerosol low rate for DMPS was 2 l/min and
0.3 l/min and 0.3l/min [15] for CPC. he ambient air
temperature at the inlet was 25 ± 2 °C (the argon temperature was – 18 ± 1 °C, relative humidity 25–30%.
he movement of the laser beam was controlled
by a galvoscanner. During the experiments, a laser
beam was moving in the form of zigzag, illing a
square (5 × 5 mm2). It means that the faster moved
the beam, the less time it took to ill a square and
to start over ablating the same area again. he laser
beam focus diameter D and area S in the case of nslaser were D = 40±5 µm, S = 1.26·10–5 cm2; in the case
of the ps-laser D = 20±5 µm, S = 3.14 · 10–6 cm2.
he nanosecond laser process parameters were:
the average power 0.1–3 W, the pulse repetition
rate 1–40 kHz and the beam scanning speed 10–
1000 mm/s.
hose of the picosecond laser: the average power 0.1–2 W, the pulse repetition rate 50 or 100 kHz
and the beam scanning speed 10–1000 mm/s. For
data analysis of the size distribution of generated
Fig. 1. Experimental set-up for generated particle measurement.
V. Dudoitis et al. / Lithuanian J. Phys. 51, 248–259 (2011)
251
particles by laser ablation in ambient air the
Aitken classiication of atmospheric aerosol particle modes was used [16].
4. Results
Samples were placed into the chamber and it was
illed with the operating gas. he laser beam was
scanned over the sample surface and both techniques
were applied to measure the particles in the exhaust
gasses. During the experiments the particle size distribution was averaged from 3 to 8 measurements.
he geometric mean of the particle size diameter dp
and the standard deviation σg were calculated. Solid
curves in Figs. 2, 3, 5 were obtained by itting the data
using DistFit program [17].
Fig. 2. Particle size (Dp) distribution for the ns-laser
ablation of nickel in ambient air at 0.4 W, 10 kHz, 200
mm/s and 12.73 J/cm2.
Nickel. Particle generation data by ps- and nslaser ablation of nickel in ambient air are shown
in Figs. 2 and 3. As seen, the processes involved in
particle formation were partially diferent. Smallest particles of 8 nm size (nucleation mode) with
the concentration up to 5·104 cm-3 were observed
in case of the ps-laser. Particles generated in the
nucleation mode with the size of 18 nm and with
three times higher number concentration were
observed during ns-laser ablation as well (see Table 1). However, in case of the ns-laser ablation, a
wide size spectrum of particles from 10 to 180 nm
with a sharp peak only in the nucleation mode
was observed (Fig. 2). CPC data showed a growth
of the particle number concentration in time during the laser ablation (Fig. 4(a)).
Fig. 3. Particle size Dp distribution for the ps-laser ablation in ambient air: (a) nickel at 0.25 W, 100 kHz,
10 mm/s and 0.80 J/cm2; (b) aluminum at 0.6 W, 50 kHz,
10 mm/s and 3.82 J/cm2; (c) tungsten at 0.25 W, 100 kHz,
1 000 mm/s and 0.80 J/cm2.
Sharp peaks of the nucleation, Aitken and
accumulation modes at 8, 57 and 164 nm, respectively, were observed in the particle size
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Table 1. Maximum number concentration of generated particles during nanosecond (ns) and picosecond (ps) laser
ablation in diferent media, cm-3.
Aerosol particle modes in the atmosphere
Laser
Metals
Accumulation (130–
type
Nucleation (1–30 nm)
Aitken (30–130 nm)
200 nm)
In ambient air
(0.90 ± 0.17) × 105
(1.2 ± 0.2) × 105
Nickel (Ni)
ns
(peak at 61 nm)
(peak at 18 nm)
Nickel (Ni)
ps
(5.0 ± 0.2) × 104
(peak at 8 nm)
(1.60 ± 0.15) × 104
(peak at 57 nm)
Aluminum (Al)
ps
(1.6 ± 0.5) × 103
(peak at 20 nm)
(0.7 ± 0.3) × 103
(peak at 43 nm)
Tungsten (W)
ps
Nickel (Ni)
ns
Aluminum (Al)
ns
(1.13 ± 0.03) × 106
(peak at 21 nm)
Stainless steel (302)
ns
(1.86 ± 0.06) × 106
(peak at 17 nm)
Nickel (Ni)
ps
(1.8 ± 0.3) × 105
(peak at 8 nm)
Aluminum (Al)
Tungsten (W)
(1.8 ± 0.2) × 104
(peak at 31 nm)
In argon gas
(2.0 ± 0.6) \ × 105
(1.40 ± 0.03) × 106
(peak at 107 nm)
(peak at 20 nm)
(6.20 ± 0.15) × 104
(peak at 164 nm)
(1.1 ± 0.2) × 104
(peak at 186 nm)
(3.4 ± 0.3) × 105
(peak at 99 nm)
(5.8 ± 0.15) × 105
(peak at 182 nm)
(5.9 ± 0.3) × 105
(peak at 46 nm)
(2.9 ± 0.2) × 105
(peak at 166 nm)
ps
(1.7 ± 0.3) × 105
(peak at 79 nm)
(2.5 ± 0.7) × 105
(peak at 170 nm)
ps
(3.9 ± 0.4) × 105
(peak at 36 nm)
(2.5 ± 0.9) × 105
(peak at 131 nm)
distribution during the ps-laser ablation
(Fig. 3(a)). Particle number concentrations of
these modes were (5.0±0.2)·104, (1.6±0.15)·104
and (6.2±0.15)·104 cm-3, respectively. he CPC data
show an intensive particle generation process in
the irst minutes and a slow declining tendency in
time using a diferent laser beam scanning speed
(Fig. 4(b)). he highest nickel particle concentration (up to 1.2·105 cm-3) was generated in ambient
air using the ns-laser (Table 1).
Generation of particles was also performed
in the argon gas low. It was observed that generated nickel particles using both types of lasers had a narrow size distribution peaked at
20 nm with the high number concentration
(1.4·106 cm-3) and concentration lower by order of magnitude at 107 nm (2.0·105 cm-3) using
the ns-laser and at 8 nm (1.8·105 cm-3), at 46 nm
(5.9·105 cm-3) and at 166 nm (2.9·105 cm-3) using
the ps-laser ablation (Table 1). Generation of nickel particles by ps-laser ablation, as can be seen in
Figs. 5(a,d), was weaker compared to the ns-laser
ablation and caused a shit of the size distribution
peak from 20 to 46 nm and to a coarse particle
range (166 nm).
Aluminum. Generation of aluminum particles
by the ps-laser ablation in ambient air was ineficient. As seen in Fig. 3(b), generated particles
were of nucleation and Aitken modes. he highest
number concentration of generated particles was
in the nucleation mode at 20 nm (1.6·103 cm-3)
(Table 1). CPC data showed a rapid sink trend
of the particle number concentrations in time
(Fig. 4(e)).
he opposite situation was observed in case
of the aluminum particle generation in argon gas
using the ns-laser compared to the ps-laser. he
hughest number concentration of particles was
measured during the ns-laser ablation. he size
spectrum of generated aluminum particles using
the ns-laser was similar to that of nickel particles, i. e. two peaks were observed at 21 nm and
V. Dudoitis et al. / Lithuanian J. Phys. 51, 248–259 (2011)
253
Fig. 4. Dynamics of generated particle number concentration during laser ablation of various metals in ambient
air: (a) nickel by ns-laser at 0.4 W, 20 kHz, 1.59 J/cm2 and (b) by ps-laser at 0.49 W, 100 kHz, 1.56 J/cm2; (c) tungsten by ns-laser at 0.85 W, 22 kHz, 3.07 J/cm2 and (d) by ps-laser at 0.25 W, 100 kHz, 1.80 J/cm2; (e) aluminum by
ns-laser at 0.6 W, 50 kHz, 3.82 J/cm2.
99 nm (Fig. 5(b)). he maximum particle number
concentration reached 1.13·106 cm-3 for the smallest size of 21 nm (Table 1).
he measurement data showed that the maximum number concentration of generated alumi-
num particles by the ps-laser was (1.7–2.5)·105 cm-3
and it was higher than in case of the ns-laser, i. e.
the particle size ranged widely from 50 to 200 nm
with two maximums: at 79 and 170 nm (Fig. 5(e),
Table 1).
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Fig. 5. Particle size dp distribution for the ns-laser ablation of various metals in argon gas: (a) nickel at 2.7 W, 30
kHz, 10 mm/s, 7.16 J/cm2; (b) aluminum at 1.36 W, 20 kHz, 100 mm/s, 5.41 J/cm2; (c) stainless steel at 1.75 W, 5
kHz, 10 mm/s, 27.85 J/cm2 and the ps-laser ablation in argon gas: (d) nickel at 1.5 W, 50 kHz, 100 mm/s, 9.55 J/cm2;
(e) aluminum at 0.6 W, 50 kHz, 100 mm/s, 3.82 J/cm2; (f) tungsten at 1.2 W, 100 kHz, 100 mm/s, 3.82 J/cm2.
Tungsten. Generation of tungsten particles by
laser ablation was investigated using only the pslaser in ambient air and argon gas medium. he size
distribution of generated particles was completely
diferent in both cases and evidently showed that
the particle size distribution strongly depended on
the experimental conditions. he highest number
concentration (3.9·105 cm-3) was found during the
ps-laser ablation in argon gas and the particle size
distribution in this case was observed in a wide
V. Dudoitis et al. / Lithuanian J. Phys. 51, 248–259 (2011)
range from 18 to 200 nm (Table 1). In both media,
particles of a narrow size mode were not formed,
but a wide size spectrum was observed with a shit
to the smaller particle size in ambient air, while
in argon gas it was shited to coarse particle size
(Figs. 3(c) and 5(f)). Measurement in argon gas
showed two number concentration peaks at 36 nm
and 131 nm. CPC data of tungsten particle formation process are shown in Figs. 4(c,d) during the
ns- and the ps-laser ablation. As seen, the dynamics of the generated particle number concentration
shows that during ablation in ambient air and argon gas the production of particles was diferent.
In case of tungsten CPC data showed a slight
growth of the particle number concentration for the
ns- laser ablation when a small declining tendency
in the irst six minutes for the ps-laser ablation and
a further slow growth of the particle number concentration were observed (Fig. 4(d)).
Stainless steel. he experimental data on generation of particles in stainless steel by the nanosecond
laser ablation in argon gas are shown in Fig. 5(c).
It should be noted that the particle number concentration reached 1.86·106 cm-3 (the distinct peak
at 17 nm), but the size spectrum of generated particles was ranging to 200 nm. he second small peak
at 190 nm in the size distribution of generated particles was observed.
5. Discussion
In this research, as in many cases of such type of investigations [3, 5, 10, 11, 18–20], it has been shown
that concentration of generated particles and their
size distribution depend on the experimental medium, target material properties and laser process
parameters. At irst, the formation of nanoparticles
their size were afected by parameters of laser irradiation – the intensity, pulse length and radiation
wavelength. Our experimental data showed that the
smallest (~8 nm) particles of nucleation mode were
formed by the picosecond laser ablation (Figs. 3
and 5). Larger (17–21 nm) particles of nucleation
mode were generated during the nanosecond laser
ablation.
Diferent physical mechanisms of laser beammatter interaction for ns- and ps-lasers have an effect on the diameter of generated particles. he primary thermal nature of nanosecond laser ablation
can lead to formation of a molten layer and ejection
255
of melted particles at evaporation, in addition to
particles formed from condensation [1]. he metal
surface impacted by picosecond laser radiation can
be attributed to electrons and mass emitted from
the target surface, while particle generation ater
several 10 ns pulses proceeds due to emission of
particles and droplets ater a thermal boiling process. Vaporized material, in contact with metal, is
ionized and over the target surface a formation of
plasma cloud from electrons, ions and particles of
metals starts [5, 11, 19, 21]. Our registered smallest nickel particles of nucleation mode (~8 nm) by
the ps-laser ablation can be produced during this
process (Figs. 3 and 5).
Experimental results have shown that the generated particles (nickel, aluminum) during the pslaser ablation are characterized by the maximum in
the particle size range of 160–170 nm, while during the ns-laser ablation particles of size range of
90–110 nm were produced (Table 1).
he efects of various laser process parameters
on the nickel particle size and number concentration during the nanosecond laser ablation in argon gas at four diferent laser intensities were observed, and two almost identical narrow peaks of
size distribution of particles for all energies were
obtained (Fig. 6(a)). Two narrow peaks of nickel particles in the range of 14–18 nm and 100–
150 nm at pulse energies from 90 to 207 µJ were
observed. It should be noted that by changing the
laser beam scanning speed (10 or 100 mm/s) the
diference in the particle concentration and size
distribution was very small.
he same results were observed in experiments
with aluminum (Fig. 6(b)). Two narrow peaks of
particles in the range of 20–24 nm and 80 nm at laser pulse energies from 47 to 89 µJ with stable particle number concentration by changing laser beam
scanning speed (100 mm/s or 1000 mm/s) were
obtained. he production of the maximum number
concentration of metal particles by laser ablation in
argon was reached: for nickel at 93 µJ, stainless steel
at 350 µJ and aluminum at 89 µJ.
As seen in Fig. 6(c), the largest efect on stainless
steel particle generation at various (150–385 µJ) nslaser pulse energies was observed at 350 µJ pulse
energy and the beam scanning speed of 10 mm/s.
he variations of the nickel particle number
concentration only of the smallest size particles
(10–12 nm) during the ps-laser ablation in argon
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Fig. 6. Particle size dp distribution for ns-laser ablation
of metals in argon gas at diferent beam intensities: (a)
nickel at 10–30 kHz, 10–100 mm/s (16.47, 11.70, 7.40
and 7.16 J/cm2 respectively to the laser pulse energy);
(b) aluminum at 10–20 kHz, 100–500 mm/s (7.08,
5.41 and 3.74 J/cm2 respectively to the laser pulse energy) and (c) stainless steel at 1–20 kHz, 10–100 mm/s
(27.85, 30.64, 13.13 and 11.94 J/cm2 respectively to the
laser pulse energy).
gas by changing the laser beam scanning speed (100
or 1000 mm/s) were observed. In case of stainless
steel during the ns-laser ablation by changing the
beam scanning speed from 10 to 100 mm/s, the
particle number concentration varied about two
times in the range of 14–18 nm. he optimal regime for particle generation (nickel and stainless
steel) was observed at following laser parameters:
the pulse frequency 10 kHz and the beam scanning
speed 100 mm/s.
As seen in Figs. 2, 3 and 5, the size distribution
and number concentration of generated metal particles during laser ablation in ambient air difered
from those in argon gas. First of all, we consider
that formation of particle size and their number
concentration was inluenced by the complex of
precursors (oxygen, water vapor, suspended matter <5 nm, etc.) present in ambient air, which was
passing through the ablation chamber. Precursors
themselves are actively forming various chemical
compounds with generated metal particles (NiO,
Al2O3, FeO) during the ablation. Studies of particle formation by Gonzalez et al. [1] show that the
particle size strongly depends on the precursor
concentration (atoms and clusters), which will affect the size of the primary particles. he oxidation
process of nickel particles during laser ablation
in ambient air is shown in works of Liu et al. [5].
For example, in Fig. 2 it can be seen that the nickel
particle size spectrum is wide and the generation
of particles by the ns-laser in narrow ranges was
not observed. he standard deviation of the generated particle number concentration at 61 nm was
σg = 3.21 and only a sharp peak of smallest nickel
particles at 18 nm (σg = 1.15) was observed.
Investigation of nickel particle formation by the
ns- and ps-laser ablation in ambient air showed
that the inluence of precursors on the particle
size and concentration was diferent as well. he
size distribution of the generated nickel particles
showed that during the ps-laser ablation in argon gas the smallest particles in the nucleation
mode (dp = 8 nm) and coarser particles in Aitken
(dp = 46 nm) and accumulation (dp = 166 nm)
modes were produced (Fig. 5(d)). he standard
deviations of particle concentration for these sizes
were σg = 1.35, σg = 1.13 and σg = 1.56, respectively.
In addition to the particle size in the range from 10
to 100 nm for nickel during ps-laser ablation in ambient air the inluence of precursors was observed,
except for particles less than 10 nm with σg = 1.35
(Fig. 3(a)). Comparison of the aluminum particle
size with the size of nickel and tungsten particles
under the same ablation conditions (ambient air,
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ps-laser) showed a wide variety range of all particles
(Fig. 3). Aluminum particles in a wide range with
peaks at 20 nm (the standard deviation σg = 1.31)
and with a negligible peak at 43 nm (σg = 2.32) were
formed (Fig. 3(b)). Based on aluminum properties,
it is possible to explain that the ablated particles can
be originated from Al2O3. A constant ilm of aluminum oxide is formed on the surface of this metal in
contact with air [10].
Besides, the inluence of precursors during the
picosecond laser ablation in ambient air was observed in case of generated tungsten particles. As
seen in Fig. 3(c) Aitken mode particles dominated
(dp = 31 nm, σg = 2.46) in a wide size spectrum. he
accumulation mode was clearly separated in the
particle size distribution (dp = 186 nm, σg = 1.13). In
general, the particle generation of all investigated
metals in ambient air was very small.
Experimental data of particle formation by the
ns- and ps-laser ablation in argon gas have shown
that the particle size distribution and concentration
depended on the processed metal characteristics, on
the laser process parameters as well as on the thermodynamic conditions in the processed zone. For
example, during the ns-laser ablation in argon gas
smaller particles were produced (17–21 nm) than
during the ps-laser ablation, except for nickel particles (dp = 8 nm, σg = 1.35) (Table 1, Fig. 5(a, d).
Furthermore, the dependence of the nanoparticle size distribution on material properties of various metals during the ns- or ps-laser ablation was
observed. he laser pulse energy inluencing the
size distribution of nanoparticles generated during
laser ablation of various materials depends on their
relectivity [10]. he smallest particles are generated at higher pulse energies, but a size shit decreases
for materials with lower relectivity.
Our measurement data showed that during the
ns-laser ablation of stainless steel, nickel and aluminum the shit to a smaller size range was observed
at higher pulse energy of metals with lower relectivity. We observed the smallest generated particles
(dp = 17 nm) of stainless steel (34% relectivity) at
350 μJ pulse energy, whereas aluminum (relectivity – 91%) generated particles were of 21 nm magnitude at 89 µJ pulse energy (Fig. 6, Table 2).
he explanation for separate number concentrations of nanoparticles and their size spectrum
of investigated metals is more complicated due to
the diferent physical properties of each material.
As can be seen in Fig. 5, a major variety of discrepancy of modes of produced particles among metals
is observed during the picosecond laser ablation.
Our results for tungsten are in agreement with [22]
where an increase in the formation of larger particles of elements with a high melting point was determined. As seen in Table 2, the melting point of
tungsten is highest among investigated metals and
a wide size spectrum of produced tungsten particles with a shit to the coarse particle size compared
to other metals was observed (Fig. 5).
According to the investigations by Gonzalez et al.
[1], Brikas [10] and Hola et al. [22], the inluence of
material properties on the size and concentration
of particles generated by the nanosecond laser ablation is important. he higher number concentration
of stainless steel and nickel particles produced by
the ns-laser (Table 1) could be relatted to the lowest thermal conductivity of these metals compared
with other investigated metals (Table 2). Generally,
the generation of stainless steel, nickel and aluminum particles by the ns-laser ablation in argon gas
was the most intensive.
6. Conclusions
he peculiarities of nanoparticle formation during
the ns- and ps-lasers ablation of nickel, aluminum,
stainless steel and tungsten in ambient air and argon gas were investigated experimentally.
Table 2. Physical properties of investigated metals.
Metals
hermal conductivity K,
W / (cm K)
Density
ρ, g/cm3
Melting point
TM, K
Boiling point,
TB, K
Relectivity
coeicient R
Aluminum (Al)
Tungsten (W)
Stainless steel (302)
Nickel (Ni)
2.37
1.74
0.16
0.91
2.7
19.3
7.8–8
8.9
933
3673–3683
1644–1672
1 726
2467
5930
3000
3005
0.91
0.49
0.34
0.70
258
V. Dudoitis et al. / Lithuanian J. Phys. 51, 248–259 (2011)
It was found that the size distribution and
number concentration of generated metal particles
during the laser ablation in ambient air difered
from those in argon gas medium. he number
concentrations of generated nanoparticles during
the laser ablation in argon gas, compared to the
produced nanoparticle concentrations in ambient
air, were up to 100 times higher and characterized
by stable separate size peaks (nucleation, Aitken
and accumulation modes) of nanoparticles, while
a wide size spectrum (from 8 to 200 nm) of generated nanoparticles without clear separation of the
size modes in ambient air was observed. he natural precursors in ambient air can have an efect
on the on size spectrum of particles composed of
various chemical compounds with target material
during ablation process.
Primary particles of 8 nm size during the pslaser ablation and of 17–21 nm in nucleation mode
by the ns-laser ablation were produced. It was evidently caused by diferent physical processes in the
laser beam material interaction zone.
he inluence of laser process parameters on the
number concentration and a shit in dynamics of
size distribution of nanoparticles generated during the ns- and ps-laser ablation in argon gas were
observed. he maximum number concentration of
generated metal particles by laser ablation in argon
was reached:: for nickel at 93 µJ, stainless steel at
350 µJ and aluminum at 89 µJ. Moreover, the dependence of the investigated metal properties (relectivity, melting point and thermal conductivity)
on the size distribution and number concentration
of generated nanoparticles was determined.
he study showed that according to particular
laser process parameters during the nanosecond
and picosecond laser ablation in argon gas the generation of stable separate modes of nickel and aluminum particle size distribution can be controlled.
Further investigations will focus on the development of technology of generation of monodisperse metal nanoparticles (the standard deviation
σg = 1.1) based on primary and secondary particle
formation physical processes.
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METALŲ NANODALELIŲ GENERAVIMAs LAZERINE ABLIACIJA
V. Dudoitis, V. Ulevičius, G. Račiukaitis, N. Špirkauskaitė, K. Plauškaitė
Valstybinis mokslinių tyrimų institutas Fizinių ir technologijos mokslų centras, Vilnius, Lietuva
santrauka
Lazerinė abliacija, kaip efektyvus ir spartus įvairių
medžiagų smulkių struktūrų formavimo būdas, pastaruoju metu vis sėkmingiau įsitvirtina nanodarinių
gamyboje. Metalai yra vieni tinkamiausių medžiagų
mikrosistemoms gaminti. Norint formuoti tikslias mikrosistemas turi būti atliekami generuojamų nanodalelių dydžių spektro bei koncentracijos eksperimentiniai
tyrimai. Darbe nagrinėti nikelio, aliuminio, nerūdijančio plieno ir volframo nanodalelių generavimo procesai, taikant nanosekundinės ir pikosekundinės trukmės
impulsų lazerius. Nustatyta, kad generuojamų visų tirtų
metalų nanodalelių dydžių spektras ir skaitinė koncentracija, vykstant lazerinei abliacijai oro ar argono dujų
aplinkoje, ženkliai skiriasi. Vykstant lazerinei abliacijai
ore generuojamos nanodalelių (1–12).104 cm-3 koncentracijos bei 8–200 nm dydžių platus spektras su nukleacinės ir akumuliacinės modų nedidelėmis smailėmis.
Manome, kad atskirų dydžių generuojamų nanodalelių
spektrui įtakos turėjo oro sudėties komponentės, kurios abliacijos proceso metu dalyvavo susidarant cheminiams junginiams (pvz., FeO, NiO, Al2O3). Lazerinės
abliacijos ore atveju argono dujų aplinkoje generuojamos metalų nanodalelių (0,1–1,9).106 cm-3 koncentracijos su gerai besiformuojančiu nukleacinės, Aitkeno ir
akumuliacinės modų spektru. Stebėta lazerinės abliacijos parametrų ir metalų savybių įtaka generuojamų
nanodalelių skaitinei koncentracijai bei dalelių dydžių
pasiskirstymo spektre poslinkiui. Mažiausios nanodalelės (~8 nm) generuotos abliuojant nikelį pikosekundinės trukmės impulso lazeriu argono dujų aplinkoje.
Manome, kad registruotos pirminės nikelio dalelės
galėjo būti generuojamos susidarius plazmai lazerinės
spinduliuotės ir metalo sąveikos zonoje. Nerūdijančio
plieno, nikelio ir aliuminio nanodalelių (10–200 nm)
generavimo procesas intensyviausiai vyko abliuojant
metalus nanosekundinės trukmės impulso lazeriu argono dujose.