1. Field of the Invention
The present invention relates to a powder containing Fe—Ni nano-particles and its manufacturing method, and particularly to a powder having a film of Fe—Ni nano-particles deposited on the surface. The powder containing Fe—Ni nano-particles has very small volume and very large surface area. The contact chance between Fe/Ni bimetal and chlorinated organic substance is largely increased. It can be used to treat various environmental pollutants or for some catalytic reactions, and particularly to treat the organic pollutants containing chlorine in environment.
2. Description of the Prior Art
The chlorinated organic substance generally has strong toxicity, which are rather dangerous to the human body and the environment of living things. For example, tetrachloroethene (PCE) and carbon tetrachloride (CT) have been proved to be able to cause cancer on human body, and the other various chlorinated organic substance are also possible for human to cause cancer. The chlorinated organic substance such as chloroform (CF), trichloroethene (TCE), dichloromethane (DCM), PCE and CT etc. are widely used in industry. They are chiefly used for degreasing, dyeing, cleaning and printed circuit manufacturing processes. These kinds of compounds are rather stable and not easy to be resolved. Their resolvability in water is low and easy to accumulate in soil and underground water so that they after become the general pollutants in soil and underground water. Therefore, besides to make law to prevent the chlorinated organic substance from entering the environment, the place that has been polluted by the chlorinated organic substance must be treated and remedied as quickly as possible.
The chlorine atom has high electronegativity and can adsorb electrons from neighborhood, so the most carbons in the chlorinated organic substance exist at relatively high oxidation state and the chlorine in the chlorinated organic substance can be resolved and removed by the reduction method. Because the iron metal has rather high reducing power, i.e. able to provide electrons, it can be used to resolve various chlorinated organic substance such as chlorinated methane, chlorinated ethane, trichloroethene, tetrachloroethene, trichloroethane, and trichloromethane etc.
Although the iron metal can effectively resolve the chlorinated organic substance, it would occur that the pH value does increase in the dechlorine process and the surface of the iron particle does form some iron oxide in the environment containing water and is covered up, so the activity of the iron is reduced and the ability for resolving the chlorinated organic substance is lowered.
In order to improve the drawback of the iron metal as stated above, the second kind of metal such as Pd, Ni, Ag, Cu, and Au is added in the iron to form bimetal, keep the dechlorine activity for iron surface and promote the reaction of dechlorine. Among these metals, Ni has catalysis and anti-corrosion in water, so it is relatively often used to form Fe/Ni bimetal for dechlorine.
The ability of bimetal, for removing the chlorinated organic substance, is higher than iron metal. For resolving the chlorinated organic substance, the dechlorine substance needs possess both the reducing power and large surface area. The more the surface area, the higher the dechlorine power. Therefore, it is necessary that the bimetal is made into micro-particles with large surface area. The micro-particle of metal as a dechlorine agent cannot only promote the surface contact and reaction but also increase the penetrative power in the contaminated soil to promote the treatment effect.
The volume of the metal particle must be decreased to increase its surface area. If the volume of the metal particle is too small, it will quickly penetrate through the soil and easily flows away. Therefore, the time of contact and reaction between metal and chlorinated organic substance becomes too short and the effect of removing chlorinated organic substance by metal is lowered. The problem of penetration and loss of the metal particle must also be considered when the volume of the metal particle is reduced to increase the surface area.
In addition, it is rather difficult in technique how to make micro-particles of Fe—Ni bimetal, especially particles with nanometer size. In the prior technique, the nano-particles of iron metal are first made, and subsequently the iron nano-particles are put into the solution containing Ni++ to make the Fe atoms on the surface of the particles be replaced by the Ni atoms. The reducing reaction is shown in the following:
Ni+++Feo→Fe+++Nio
But the Fe—Ni particles made by this way are strictly not the real Fe/Ni bimetal, they are only the iron particles of which surface are covered with a film of Ni. Only the film of Ni can touch the chlorinated organic substance to proceed the reducing and resolving reaction, and the Fe atoms inside have no chance to touch the chlorinated organic substance at all.
In order to get the real Fe—Ni nano-particles, of which Fe and Ni atoms can simultaneously exist on the surface of the particles and have the same chance to touch with chlorinated organic substance and proceed reducing and catalyzing reaction, and to prevent the particles in the contaminated soil from flowing away due to their small volume. Therefore, the present invention provides a powder and its manufacturing method, which can solve the all problems as stated above.
The primary object of the present invention is to provide a powder containing Fe—Ni nano-particles. The powder has a carrier and Fe—Ni nano-particles. The Fe—Ni nano-particles are deposited on the surface of the carrier by an electroless plating technique. The carrier has about μm of size and has very large surface area. The contact area between Fe/Ni bimetal and chlorinated organic substance is largely increased and the effect of processing chlorinated pollutants is consequently promoted.
Another object of the present invention is to provide a method for manufacturing a powder containing Fe—Ni nano-particles. The method chiefly uses the electroless plating technique to connect Fe—Ni nano-particles on the surface of the μm-sized carrier. The atomic ratio of the Fe and Ni atoms in the Fe—Ni nano-particles can be controlled by changing the relative concentration of the Fe++ and Ni++ ions in the plating solution and the plating condition. It suits for various chlorinated pollutant treatments.
Another object of the present invention is to provide a powder containing Fe—Ni nano-particles including the carrier, which is ceramic particle and is μm-sized. It suits for penetrating the soil containing pollutants and does not quickly flow away.
In order to achieve the objects as stated above, the present invention selects some ceramic particles with about micrometer size as the carrier. These ceramic particles have the following characteristics: stable in chemistry, no contamination to environment and cheap. These ceramic particles include Al2O3, SiO2, TiO2, CaO, SiC and WC etc. The carrier first is cleaned in the aqueous solution containing HCl, H2SO4 or HF in order to remove the dirt on the surface of the carrier and activate the surface atoms of the carrier. The carrier then is sensitized and activated in the solution of SnCl2 and the solution of PdCl2 to make the surface of the carrier be plated a film of catalytic substance. Subsequently the surface of the carrier is deposited a film of Fe—Ni nano-particles in the solution containing Fe and Ni ions. At last, the powder containing Fe—Ni nano-particles is dried in the drying furnace with protective atmosphere.
The powder containing Fe—Ni nano-particles obtained by the above-stated steps, comprising the carrier and Fe—Ni nano-particles, wherein the size of the carrier is about micrometer (μm) and Fe and Ni atoms of the Fe—Ni nano-particles are simultaneously deposited on the surface of the carrier. The size of the Fe—Ni nano-particles is from several nanometers (nm) to several hundred of nanometers. The atomic ratio of the Fe and Ni atoms can be controlled by changing the relative concentration of the plating solution and the plating condition, wherein the Fe—Ni nano-particles contain 0(a trace)˜25 wt % Fe and 75˜100 wt % Ni.
In order to let the objects, technique and advantages of the present invention be deeply understood, there are some preferred embodiments with drawings described in detail below.
The method for manufacturing a powder containing Fe—Ni nano-particles according to the present invention first selects a ceramic particle as a carrier. The ceramic particle can be Al2O3, SiO2, TiO2, CaO, SiC, WC or the like. The average size of the carrier is μ-sized. And then proceed the steps as follows.
The powder containing Fe—Ni nano-particles obtained by the above-stated steps, comprising the carrier and Fe—Ni nano-particles, wherein the size of the carrier is about micrometer (μm) and Fe and Ni atoms of the Fe—Ni nano-particles are simultaneously deposited on the surface of the carrier. The size of the Fe—Ni nano-particles is from several nanometers (nm) to several hundred of nanometers. The atomic ratio of the Fe and Ni atoms can be controlled by changing the relative concentration of the plating solution and the plating condition, wherein the Fe—Ni nano-particles contain 0(a trace)˜25 wt % Fe and 75˜100 wt % Ni. Now there are some embodiments described in detail below.
Referring to
In this embodiment the carrier is also the Al2O3 ceramic particles and proceed the steps (1)˜(3) as described in the embodiment (1). And then proceed the electroless plating process of the step (4), wherein the electroless plating bath and operation condition are shown in table (2) below.
Then proceed the step (5) of embodiment (1) to get the Al2O3 particles containing Fe—Ni nano-particles, which is almost the same as the
The embodiment (3) of the present invention selects the SiO2 ceramic particles as the carrier and proceed the steps (1)˜(3) as described in the embodiment (1). And then proceed the electroless plating process of the step (4), wherein the electroless plating bath and operation condition are shown in table (3) below.
Then proceed the step (5) of embodiment (1) to get the powder containing Fe—Ni nano-particles, which is almost the same as the embodiment (1).
The embodiment (4) of the present invention as the embodiment (3) selects the SiO2 ceramic particles as the carrier and proceed the steps (1)˜(3) as described in the embodiment (1). And then proceed the electroless plating process of the step (4), wherein the electroless plating bath and operation condition are shown in table (4) below.
Then proceed the step (5) of embodiment (1) to get the powder containing Fe—Ni nano-particles, which is almost the same as the embodiment (1).
The embodiment (5) of the present invention selects the TiO2 ceramic particles as the carrier and proceed the steps (1)˜(3) as described in the embodiment (1). And then proceed the electroless plating process of the step (4), wherein the electroless plating bath and operation condition are shown in table (5) below.
Then proceed the step (5) of embodiment (1) to get the powder containing Fe—Ni nano-particles, which is almost the same as the embodiment (1).
The above statement is only the preferred embodiments of the present invention, they cannot be used to limit the scope of the present invention. The all apparent modification and application made by the persons who are skilled at this field should be regard as the content of the present invention.
The powder containing Fe—Ni nano-particle and its manufacturing method has the following advantages:
To sum up, the present invention indeed can accomplish its expected object to provide a powder containing Fe—Ni nano-particles and its manufacturing method. The powder can be used to treat the chlorinated pollutants in the environment. It has its industrial practical value.
Number | Name | Date | Kind |
---|---|---|---|
4532190 | Kanbe et al. | Jul 1985 | A |
4624798 | Gindrup et al. | Nov 1986 | A |
4944985 | Alexander et al. | Jul 1990 | A |
5134039 | Alexander et al. | Jul 1992 | A |
5512094 | Linton | Apr 1996 | A |
5616423 | Sanjyou et al. | Apr 1997 | A |
5963771 | Chan et al. | Oct 1999 | A |
6277489 | Abbott et al. | Aug 2001 | B1 |
6746508 | Deevi et al. | Jun 2004 | B1 |
6878445 | Hattori et al. | Apr 2005 | B2 |
20050227074 | Oyamada et al. | Oct 2005 | A1 |