This application is based upon and claims the benefit of priority from prior Japanese Patent Application No. 2006-095824, filed Mar. 30, 2006, the entire contents of which are incorporated herein by reference.
1. Field of the Invention
The present invention relates to a method of treating tobacco mainstream smoke and a smoking tool.
2. Description of the Related Art
Conventionally, it has been proposed to add various adsorbents and modifiers to the filter in order to remove hazardous substances in tobacco smoke.
Further, known is a smoking article comprising a rod of a smoking material and a filter section connected to the rod, wherein the filter section includes means for collecting particulate matter in smoke generated from the smoking material rod into a collecting zone, and means for heating the collecting zone such that a nonvolatile material is maintained in the filter and a semi-volatile material is released from the filter (see Jpn. Pat. Appln. KOKAI Pub. No. 4-262773).
However, no effective means for selectively removing carbon monoxide from tobacco mainstream smoke are known so far.
An object of the present invention is to provide a method of treating tobacco mainstream smoke and a smoking tool that is capable of selectively removing carbon monoxide in tobacco mainstream smoke.
A method of treating tobacco mainstream smoke according to an aspect of the present invention comprises: introducing tobacco mainstream smoke into a heated catalyst packed section packed with an oxidation catalyst containing copper oxide, and selectively removing carbon monoxide relative to nicotine among components of the tobacco mainstream smoke.
In the method of the present invention, the catalyst packed section is preferably heated to a temperature in a range of 200 to 350° C.
A smoking tool according to another aspect of the present invention comprises: a catalyst packed section packed with an oxidation catalyst capable of selectively removing carbon monoxide relative to nicotine among components of the tobacco mainstream smoke, into which tobacco mainstream smoke is introduced; and a heating means for heating the catalyst packed section.
In the smoking tool of the present invention, the oxidation catalyst is selected from the group consisting of Hopcalite (registered trademark), CuO/ZnO, CuO/ZnO2 and CuO/CeO2. Further, the heating means is set to heat the catalyst packed section to a temperature preferably in a range of 200 to 350° C., more preferably in a range of 200 to 280° C.
The smoking tool of the present invention may comprise a cooling section which cools the tobacco mainstream smoke and/or a filter material which collects tar at a rear section of the catalyst packed section.
According to the present invention, it makes possible to provide a method of treating tobacco mainstream smoke and a smoking tool capable of selectively removing carbon monoxide in tobacco mainstream smoke.
Examples of the present invention are described below with reference to drawings.
With the above device setup, gas components in tobacco mainstream smoke which has passed through the smoking tool 1 were measured in the following experimental procedures.
(1) Measurement of CO, CO2, and O2
The catalyst packed section 4 is packed with 200 mg of oxidation catalyst and capped with a stainless mesh. The catalyst packed section 4 is heated with the heater 5 to a predetermined experimental temperature and then left for 30 minutes. After it is checked that there is no leakage, an aluminum bag is fitted to the automatic smoking machine 20 so as to introduce dilution air. The reason for introducing dilution air is that a certain amount of gas is necessary for CO measurement. A commercial cigarette single rod 10 is smoked under the condition of 17.5 ml per two seconds. Seven puffs and one clearing puff are performed. The dilution air introduced above and tobacco mainstream smoke generated through automatic smoking are collected in one bag. CO, CO2 and O2 are quantified with a portable gas analyzer (available from Horiba, Ltd.). The above experiment is repeated twice to determine the average value.
(2) Measurement of NO and NOx
The catalyst packed section 4 is packed with 200 mg of oxidation catalyst and capped with a stainless mesh. The catalyst packed section 4 is heated with the heater 5 to a predetermined experimental temperature and then left for 30 minutes. Eight aluminum bags are prepared for one experiment (seven puffs and one clearing puff) to collect smoke for each puff. After it is checked that there is no leakage, another aluminum bag prepared separately containing dilution air is fitted. A commercial cigarette single rod 10 is smoked under the condition of 17.5 ml per two seconds. Seven puffs and one clearing puff are performed, while the bag is changed for each puff. NO and NOx of the collected gas for each bag are quantified with a portable gas analyzer (available from Horiba, Ltd.). The above experiment is repeated twice to determine the average value.
The oxidation catalyst used is Hopcalite (MnO2—CuO), CuO/ZnO, CuO/ZnO2, MnO/Fe2O3, ZrO2, ZrO2/CeO2, CuO/CeO2, or Cu, CuO/CeO2 (each crushed product with a grain size of 0.5 to 2 mm). The experiment was performed with the catalyst packed section 4 heated to 350° C., and the selective filtration coefficients of components of the collected gas were determined.
The selective filtration coefficient is defined as follows. Given that the amount of a component come out from the cigarette single rod (without the smoking tool) is Ain, and the amount of a component come out from the smoking tool when the smoking tool is attached to the cigarette single rod is Aout, the delivery rate (1−E)_A of component A is represented by the following expression: (1−E)_A=Aout/Ain. Here, the selective filtration coefficient S_B/A between component A (for example, CO) and component B (for example, nicotine) is represented by the following expression:
S
—
B/A=(1−E)—B/(1−E)—A
Table 1 and
As shown in Table 1 and
Next, experiments were performed at various temperatures using Hopcalite which exhibited the best selective removal rate for carbon monoxide relative to nicotine, and the delivery rates (1−E) for CO, NO and nicotine in the components of the collected gas were determined. Table 2 and
Table 2 and
Number | Date | Country | Kind |
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2006-095824 | Mar 2006 | JP | national |
Number | Date | Country | |
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Parent | PCT/JP2007/056429 | Mar 2007 | US |
Child | 12240921 | US |