CN103954576B - A kind ofly measure the method for Chemical Components in Cigarette Smoke at the adsorption form on solid adsorption material surface - Google Patents
A kind ofly measure the method for Chemical Components in Cigarette Smoke at the adsorption form on solid adsorption material surface Download PDFInfo
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Abstract
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技术领域technical field
本发明涉及红外光谱化学分析技术领域,具体涉及一种测定卷烟烟气成分在固体吸附材料表面的吸附形式的方法。The invention relates to the technical field of infrared spectrochemical analysis, in particular to a method for measuring the adsorption form of cigarette smoke components on the surface of a solid adsorption material.
背景技术Background technique
随着吸烟与健康问题争议的日益突出,烟草行业面临着巨大挑战,降焦减害已成为当前烟草行业发展的方向和趋势。其中,卷烟滤嘴吸附材料对于有害烟气成分的吸附应用作为降焦减害的重要手段之一,一直备受研究者们的关注。因此,如何判断固体吸附材料的吸附特性,即烟气成分在固体吸附材料表面的吸附形式,对于吸附材料在卷烟滤嘴上的应用具有极其重要的现实意义。With the growing controversy of smoking and health issues, the tobacco industry is facing huge challenges, reducing tar and harm has become the current development direction and trend of the tobacco industry. Among them, the application of cigarette filter adsorption materials to the adsorption of harmful smoke components, as one of the important means of reducing tar and harm, has always attracted the attention of researchers. Therefore, how to judge the adsorption characteristics of solid adsorbent materials, that is, the adsorption form of smoke components on the surface of solid adsorbent materials, has extremely important practical significance for the application of adsorbent materials on cigarette filters.
目前,在烟草行业中测定某种固体吸附材料的吸附特性,一般从烟气出发,利用比较法直接测定卷烟烟气成分中某些挥发性成分的去除率,从而确定吸附材料的吸附性能。而XRD、XPS、TEM、SEM、BET等仪器也只能起到分析测定固体吸附材料的本身性质的辅助作用。对于考察卷烟烟气和固体吸附材料之间的相互作用方式的表征尚未见报道。由此可见,目前仅单方面考虑研究开发固体吸附材料,而不注意烟气和固体吸附材料之间的相互作用关系的情况,存在很大的局限性,亟待解决。At present, in the tobacco industry, to determine the adsorption characteristics of a certain solid adsorption material, generally starting from the smoke, using the comparison method to directly measure the removal rate of some volatile components in the cigarette smoke components, so as to determine the adsorption performance of the adsorption material. Instruments such as XRD, XPS, TEM, SEM, and BET can only play an auxiliary role in analyzing and determining the properties of solid adsorption materials. The characterization of the interaction mode between cigarette smoke and solid adsorbent materials has not been reported. It can be seen that at present, the research and development of solid adsorption materials is only considered unilaterally, and the interaction between flue gas and solid adsorption materials is ignored, which has great limitations and needs to be resolved urgently.
红外光谱法作为一种利用物质对红外光区的电磁辐射的选择性吸收来进行结构分析及对各种吸收红外光的化合物进行定性和定量分析的方法。当成键原子或者化学键和固体吸附材料相互作用而发生吸附反应后,成键原子周围的电子云发生变化,导致成键原子的振动能级跃迁发生位移,采用红外光谱法测定分子中成键原子的振动能级跃迁,可以用来作为判定有机物特殊官能团的特征表征手段。目前,利用红外光谱表征的是一些非可逆吸附物质在固体材料表面的吸附形式,通常采用常规的压片制样后进行红外光谱分析。而卷烟烟气成分中挥发或者半挥发性物质采用压片制样后表征卷烟烟气成分在固体吸附材料表面的吸附形式不可行。Infrared spectroscopy is a method for structural analysis and qualitative and quantitative analysis of various compounds that absorb infrared light by using the selective absorption of electromagnetic radiation in the infrared region. When the bonded atom or chemical bond interacts with the solid adsorption material and the adsorption reaction occurs, the electron cloud around the bonded atom changes, resulting in a shift in the vibration energy level transition of the bonded atom. Infrared spectroscopy is used to measure the bonded atom in the molecule. Vibration level transitions can be used as a characteristic characterization method to determine the special functional groups of organic substances. At present, infrared spectroscopy is used to characterize the adsorption form of some irreversible adsorbed substances on the surface of solid materials, and infrared spectroscopy analysis is usually performed after conventional tablet preparation. However, it is not feasible to characterize the adsorption form of cigarette smoke components on the surface of solid adsorption materials after the volatile or semi-volatile substances in cigarette smoke components are prepared by pressing tablets.
而原位红外光谱作为一种研究气体和固体材料之间相互作用的重要分析工具,已广泛应用在催化反应中表征原位条件下气体分子在固体吸附材料表面的吸附形式,特别是在催化反应中捕捉一些反应中间态的物质,从分子原子角度理解催化反应的机理。但采用原位红外光谱来考察卷烟烟气中挥发或者半挥发性成分在固体吸附材料表面以物理吸附和化学吸附并存时的相互作用方式尚未见报道。In situ infrared spectroscopy, as an important analytical tool for studying the interaction between gas and solid materials, has been widely used in catalytic reactions to characterize the adsorption forms of gas molecules on the surface of solid adsorption materials under in situ conditions, especially in catalytic reactions. Capture some substances in the intermediate state of the reaction, and understand the mechanism of the catalytic reaction from the perspective of molecular atoms. However, the use of in-situ infrared spectroscopy to investigate the interaction mode of volatile or semi-volatile components in cigarette smoke when physical adsorption and chemical adsorption coexist on the surface of solid adsorption materials has not been reported.
因此,如何采用原位红外光谱考察卷烟烟气中挥发或者半挥发性成分在固体吸附材料表面的吸附形式,从而探究固体吸附材料吸附特性,满足卷烟降焦减害技术发展的需求,非常值得本领域从业者研究和探讨。Therefore, how to use in-situ infrared spectroscopy to investigate the adsorption form of volatile or semi-volatile components in cigarette smoke on the surface of solid adsorption materials, so as to explore the adsorption characteristics of solid adsorption materials and meet the needs of the development of cigarette tar and harm reduction technology, is very worthy of this paper. Field practitioner research and discussion.
发明内容Contents of the invention
鉴于以上所述现有技术的缺点,本发明的目的在于提供一种测定卷烟烟气成分在固体吸附材料表面的吸附形式的方法,采用原位红外光谱,用于解决现有技术中只能测定非可逆吸附物种在固体吸附材料表面的吸附形式,克服测定可逆吸附在固体吸附材料表面吸附形式表征技术上存在的不足,进而研究卷烟烟气成分中挥发或者半挥发性成分在固体吸附材料上的吸附形式,同时能定性分析不同吸附活性位的的表面吸附量,为卷烟滤嘴固体吸附材料的改性和开发提出更有价值的信息,满足卷烟减害技术发展的需求的问题。In view of the shortcomings of the prior art described above, the purpose of the present invention is to provide a method for determining the adsorption form of cigarette smoke components on the surface of a solid adsorption material, using in-situ infrared spectroscopy to solve the problem that the prior art can only measure The adsorption form of the irreversible adsorption species on the surface of the solid adsorption material overcomes the deficiency in the characterization technique of the determination of the adsorption form of the reversible adsorption on the surface of the solid adsorption material, and then studies the volatile or semi-volatile components in the cigarette smoke components on the solid adsorption material. At the same time, it can qualitatively analyze the surface adsorption amount of different adsorption active sites, provide more valuable information for the modification and development of cigarette filter solid adsorption materials, and meet the needs of the development of cigarette harm reduction technology.
为实现上述目的,本发明提供一种测定卷烟烟气成分在固体吸附材料表面的吸附形式的方法,包括以下步骤:In order to achieve the above object, the present invention provides a method for determining the adsorption form of cigarette smoke components on the surface of a solid adsorption material, comprising the following steps:
所述原位红外光谱是指在测试过程中,原位不动还原吸附材料在实际吸附环境的情况下,用红外线连续扫描并采集微观的反应变化的红外谱图等数据,并根据采集的数据进行定量定性分析的技术。The in-situ infrared spectrum refers to that during the test process, the in-situ fixed reduction adsorption material is in the actual adsorption environment, and the infrared spectrum is continuously scanned with infrared rays to collect data such as infrared spectra of microscopic reaction changes, and according to the collected data Techniques for quantitative and qualitative analysis.
1)将卷烟烟气成分与载气混合,并将混合后的气体与固体吸附材料进行吸附反应;1) Mixing the cigarette smoke components with the carrier gas, and performing an adsorption reaction between the mixed gas and the solid adsorption material;
较佳的,所述固体吸附材料选自活性炭、分子筛、白炭黑、离子交换树脂等。进一步的,所述分子筛选自分子筛3A、4A、5A、13X、13Z、AA。Preferably, the solid adsorption material is selected from activated carbon, molecular sieve, white carbon black, ion exchange resin and the like. Further, the molecular sieves are selected from molecular sieves 3A, 4A, 5A, 13X, 13Z, and AA.
较佳的,混合后的气体与固体吸附材料进行吸附反应的具体方法为:所述固体吸附材料填充于原位红外反应池中,将混合后的气体通过管路引入原位红外反应池中,与位于原位红外反应池中固体吸附材料进行吸附反应。Preferably, the specific method for carrying out the adsorption reaction between the mixed gas and the solid adsorption material is: the solid adsorption material is filled in the in-situ infrared reaction cell, and the mixed gas is introduced into the in-situ infrared reaction cell through the pipeline, The adsorption reaction is carried out with the solid adsorption material located in the in-situ infrared reaction cell.
进一步的,所述原位红外反应池安装在红外光谱仪中。Further, the in-situ infrared reaction cell is installed in an infrared spectrometer.
进一步的,所述管路通过六通阀来控制进样,并通过质量流量计来控制气体流速。具体的,如图1中所示,气体从钢瓶减压阀出来,通过连接在管路上的质量流量计控制气体流速,并通过六通阀来控制进样,其中,在脉冲进样时,通过第一个六通阀来控制取样和进样的切换;而与原位红外反应池相连的第二个六通阀,则是控制脉冲进样和连续进样的切换。Further, the pipeline controls sample injection through a six-way valve, and controls the gas flow rate through a mass flow meter. Specifically, as shown in Figure 1, the gas comes out of the pressure reducing valve of the steel cylinder, the gas flow rate is controlled by the mass flow meter connected to the pipeline, and the sampling is controlled by the six-way valve. The first six-way valve controls the switching between sampling and injection; while the second six-way valve connected to the in-situ infrared reaction cell controls the switching between pulse injection and continuous injection.
所述原位红外反应池是指:一种放置固体粉末吸附材料,且可以控制红外光路在固体吸附材料表面发生漫反射,同时可以通反应气体以及控制反应温度的装置。The in-situ infrared reaction pool refers to a device that places solid powder adsorption materials, and can control the diffuse reflection of the infrared light path on the surface of the solid adsorption materials, and can simultaneously pass reaction gases and control the reaction temperature.
所述高温原位红外反应池是指:反应温度可以控制在室温及其以上的原位红外反应池。The high-temperature in-situ infrared reaction cell refers to an in-situ infrared reaction cell whose reaction temperature can be controlled at room temperature or above.
所述原位红外反应池安装在红外光谱仪中是指:原位红外反应池安装在红外光谱仪的红外光路中,可以使红外光在固体吸附材料(填充在原位红外反应池内)表面发生漫反射。The installation of the in-situ infrared reaction cell in the infrared spectrometer means that the in-situ infrared reaction cell is installed in the infrared light path of the infrared spectrometer, so that infrared light can be diffusely reflected on the surface of the solid adsorption material (filled in the in-situ infrared reaction cell) .
较佳的,所述卷烟烟气成分选自一氧化碳、巴豆醛、丙烯醛、乙醛。Preferably, the cigarette smoke components are selected from carbon monoxide, crotonaldehyde, acrolein and acetaldehyde.
进一步的,所述混合气体中卷烟烟气成分一氧化碳、巴豆醛、丙烯醛、乙醛的浓度与实际卷烟烟气中的浓度相近。以便考察的固体吸附材料在实践使用时的效果表现。Further, the concentrations of the cigarette smoke components carbon monoxide, crotonaldehyde, acrolein and acetaldehyde in the mixed gas are similar to those in the actual cigarette smoke. In order to investigate the performance of the solid adsorption material in practical use.
较佳的,所述载气选自氦气、氩气、氮气。Preferably, the carrier gas is selected from helium, argon and nitrogen.
所述载气为不会在红外区域有吸收的惰性气体。The carrier gas is an inert gas that does not absorb in the infrared region.
较佳的,所述吸附反应前需要对固体吸附材料表面脱附处理。具体的,所述的脱附处理是在一个比吸附温度高的温度处理一定时间,使得固体吸附材料表面容易分解以及易挥发的成分脱附,避免在吸附实验过程中影响基线稳定性。Preferably, the surface of the solid adsorption material needs to be desorbed before the adsorption reaction. Specifically, the desorption treatment is performed at a temperature higher than the adsorption temperature for a certain period of time, so that the surface of the solid adsorption material is easily decomposed and the volatile components are desorbed, so as to avoid affecting the baseline stability during the adsorption experiment.
进一步的,所述脱附处理条件为:通载气30min,载气流速为20mL/min,将固体吸附材料以10℃/min的速度加热至120℃,并保持30min,使固体吸附材料表面吸附物种脱附,降温至30-90℃,稳定30min。Further, the desorption treatment conditions are: pass the carrier gas for 30 minutes, the carrier gas flow rate is 20mL/min, heat the solid adsorption material to 120°C at a rate of 10°C/min, and keep it for 30min, so that the surface of the solid adsorption material is adsorbed Species desorption, cooling to 30-90 ℃, stable for 30min.
较佳的,所述吸附反应的反应条件为:吸附反应测试温度:10-100℃;混合气体中卷烟烟气成分与载气的体积百分含量之比为0.01~2%:98~99.99%;混合气体的流速为20mL/min;反应时间:30min。优选的,所述吸附反应测试温度:30-90℃。Preferably, the reaction conditions of the adsorption reaction are: adsorption reaction test temperature: 10-100°C; volume percentage ratio of cigarette smoke components to carrier gas in the mixed gas is 0.01-2%: 98-99.99% ; The flow rate of the mixed gas is 20mL/min; Reaction time: 30min. Preferably, the adsorption reaction test temperature: 30-90°C.
所述卷烟烟气成分与固体吸附材料吸附反应的原理为:固体吸附材料吸附主要分为色散吸附和极性吸附。色散吸附为固体吸附材料和被吸附气体相互靠近,其偶极距发生改变,从而发生的吸附行为,多为物理吸附;极性吸附为固体吸附材料和被吸附气体由于极性相互作用,电子云转移而而发生的吸附行为,多为化学吸附。当发生极性吸附是,被吸附气体在固体吸附表面富集,同时官能团的电子对发生了转移,很容易利用红外光谱的方法判定官能团和固体吸附材料之间的相互作用的吸附形式。The principle of the adsorption reaction between the cigarette smoke components and the solid adsorption material is as follows: the adsorption of the solid adsorption material is mainly divided into dispersion adsorption and polar adsorption. Dispersive adsorption is that the solid adsorption material and the adsorbed gas are close to each other, and the dipole moment changes, and the resulting adsorption behavior is mostly physical adsorption; polar adsorption is that the solid adsorption material and the adsorbed gas are due to the polar interaction, and the electron cloud The adsorption behavior that occurs due to the transfer is mostly chemical adsorption. When polar adsorption occurs, the adsorbed gas is enriched on the solid adsorption surface, and the electron pairs of the functional groups are transferred at the same time. It is easy to use infrared spectroscopy to determine the adsorption form of the interaction between the functional group and the solid adsorption material.
2)采用红外光谱仪测定固体吸附材料表面,获得红外谱图;2) Using an infrared spectrometer to measure the surface of the solid adsorption material to obtain an infrared spectrum;
较佳的,所述红外光谱仪为傅里叶红外光谱仪。Preferably, the infrared spectrometer is a Fourier transform infrared spectrometer.
所述红外光谱仪测定固体吸附材料表面,获得红外谱图是指:采用红外光谱仪原位连续测定并采集固体吸附材料表面物种的红外谱图。The said infrared spectrometer measures the surface of the solid adsorption material and obtains the infrared spectrum refers to: adopting the infrared spectrometer to continuously measure and collect the infrared spectrum of the species on the surface of the solid adsorption material in situ.
较佳的,所述混合气体与固体吸附材料进行吸附反应时,同步采用红外光谱仪测定固体吸附材料表面。Preferably, when the mixed gas is undergoing adsorption reaction with the solid adsorption material, an infrared spectrometer is used simultaneously to measure the surface of the solid adsorption material.
进一步的,所述同步采用红外光谱仪测定固体吸附材料表面,当所述混合气体与固体吸附材料进行吸附反应达到饱和吸附后,停止采谱。Further, the infrared spectrometer is used simultaneously to measure the surface of the solid adsorption material, and when the adsorption reaction between the mixed gas and the solid adsorption material reaches saturated adsorption, the spectrum collection is stopped.
具体的,所述饱和吸附是指:在混合气体与固体吸附材料进行吸附反应时,同步采用红外光谱仪测定固体吸附材料表面,连续采谱。当测定获得的红外谱图中峰强度随时间变化不再发生变化时,即气体分子在固体吸附材料表面达到饱和吸附状态。Specifically, the saturated adsorption refers to: when the mixed gas and the solid adsorption material undergo an adsorption reaction, simultaneously use an infrared spectrometer to measure the surface of the solid adsorption material, and continuously collect spectra. When the peak intensity in the infrared spectrum obtained by the measurement does not change with time, that is, the gas molecules have reached a saturated adsorption state on the surface of the solid adsorption material.
较佳的,所述红外光谱仪测定条件为:光谱范围:4000-650cm-1;最高分辨率:0.4cm-1;信噪比:20000:1(P-P);分束器:KBr;检测器:MCT;光源:长寿命冷红外;灵敏度:10ppm;连续采样间隔:6-60s;采谱数量:73;检测时间:30min;扫描速度:24s扫描一个谱图。Preferably, the measurement conditions of the infrared spectrometer are: spectral range: 4000-650cm -1 ; highest resolution: 0.4cm -1 ; signal-to-noise ratio: 20000:1 (PP); beam splitter: KBr; detector: MCT; light source: long-life cold infrared; sensitivity: 10ppm; continuous sampling interval: 6-60s; number of spectra: 73; detection time: 30min;
3)对步骤2)测定获得的红外谱图进行分析,从而测定卷烟烟气成分在固体吸附材料表3) Analyze the infrared spectrogram obtained in step 2) to determine the content of cigarette smoke components on the surface of the solid adsorbent material.
面的吸附形式。surface adsorption.
所述对获得的红外谱图进行分析的原理为:被吸附气体在固体吸附材料表面发生吸附时,其官能团在固体吸附材料表面富集,同时被吸附的官能团电子对发生转移,此时可以根据某些官能团红外吸附波数的变化,判定哪些官能与固体吸附材料产生了相互作用并形成吸附,并且根据红外吸收波数的位移,可以判定官能团与固体吸附材料之间的相互作用的吸附形式。The principle of analyzing the obtained infrared spectrum is: when the adsorbed gas is adsorbed on the surface of the solid adsorbent, its functional groups are enriched on the surface of the solid adsorbent, and at the same time the electron pairs of the adsorbed functional groups are transferred. The change of the infrared adsorption wave number of some functional groups can determine which functions have interacted with the solid adsorption material and form adsorption, and according to the shift of the infrared absorption wave number, the adsorption form of the interaction between the functional group and the solid adsorption material can be determined.
所述卷烟烟气成分在固体吸附材料表面的吸附形式是指:官能团有一定的空间结构,他们和固体吸附材料表面原子发生相互作用后,其吸附结构有很大区别。在同一固体吸附材料表面,被吸附气体分子可以和固体吸附材料表面的一个原子发生作用,同样的也可以和多个原子发生作用。以上不同的吸附形式,其吸附作用力强弱有较大的区别。在不同固体吸附材料表面,被吸附气体分子和单个固体吸附材料表面原子发生相互作用,其电子对的转移形式也有不同。以上发生的吸附行为,利用红外的手段,观测官能团在红外波段处的吸收,可以得到判定被吸附分子在固体吸附材料表面的具体吸附形式。以便于利用一些廉价的吸附材料,对其表面修饰具有特定吸附能力的官能团,达到与价格较昂贵的固体吸附材料具有相同的吸附能力。The adsorption form of cigarette smoke components on the surface of the solid adsorption material means that the functional groups have a certain spatial structure, and after they interact with the surface atoms of the solid adsorption material, the adsorption structure is very different. On the surface of the same solid adsorption material, the adsorbed gas molecules can interact with one atom on the surface of the solid adsorption material, and can also interact with multiple atoms. The above different adsorption forms have great differences in the strength of the adsorption force. On the surface of different solid adsorption materials, the adsorbed gas molecules interact with the surface atoms of a single solid adsorption material, and the transfer forms of electron pairs are also different. For the above adsorption behavior, using infrared means to observe the absorption of functional groups in the infrared band, the specific adsorption form of the adsorbed molecules on the surface of the solid adsorption material can be determined. In order to use some cheap adsorption materials, the surface is modified with functional groups with specific adsorption capacity, so as to achieve the same adsorption capacity as the more expensive solid adsorption materials.
所述烟气成分的红外谱图可以从数据库(常用红外数据库有NISTChemistryWebBook,SDBS的NIMC有机物谱图库和ChemExper化学品目录CDD等)查到,固体吸附材料的不同活性位对于单一官能团的吸附量可以直接从红外吸收峰的强弱来判定。The infrared spectrograms of the flue gas components can be found from databases (commonly used infrared databases include NISTChemistryWebBook, the NIMC organic spectrum library of SDBS and the ChemExper chemical catalog CDD, etc.), and the adsorption capacity of different active sites of solid adsorption materials for a single functional group can be It can be judged directly from the strength of the infrared absorption peak.
如上所述,本发明的一种测定卷烟烟气成分在固体吸附材料表面的吸附形式的方法,利用原位红外光谱的测定方法,通过傅里叶红外光谱直接读取卷烟烟气挥发或者半挥发性成分在固体吸附材料表面吸附后的实时红外谱图,并对红外谱图进行分析解读,考察卷烟烟气中挥发或者半挥发性成分在固体吸附材料表面以物理吸附和化学吸附、可逆吸附和非可逆吸附并存时的相互作用方式,同时能定性分析不同吸附活性位的表面吸附量。与现有技术只能测定非可逆吸附物种在固体吸附材料表面的吸附形式,克服了测定可逆吸附在固体吸附材料表面吸附形式表征技术上存在的不足,可以扩展到研究卷烟烟气成分中挥发或者半挥发性成分在固体吸附材料上的吸附形式,为卷烟滤嘴固体吸附材料的改性和开发提出更有价值的信息,满足卷烟减害技术发展的需求。As mentioned above, a method for determining the adsorption form of cigarette smoke components on the surface of a solid adsorption material according to the present invention uses the measurement method of in-situ infrared spectroscopy to directly read the volatilization or semi-volatility of cigarette smoke through Fourier transform infrared spectroscopy. The real-time infrared spectrum of the volatile components after adsorption on the surface of the solid adsorption material, and the analysis and interpretation of the infrared spectrum, to investigate the physical adsorption, chemical adsorption, reversible adsorption and The interaction mode when irreversible adsorption coexists, and at the same time, it can qualitatively analyze the surface adsorption amount of different adsorption active sites. Compared with the existing technology, which can only measure the adsorption form of irreversible adsorption species on the surface of solid adsorption materials, it overcomes the shortcomings in the characterization technology of the determination of reversible adsorption on the surface of solid adsorption materials, and can be extended to the study of volatilization or The adsorption form of semi-volatile components on solid adsorption materials provides more valuable information for the modification and development of cigarette filter solid adsorption materials, and meets the needs of the development of cigarette harm reduction technology.
附图说明Description of drawings
图1显示为本发明的原位红外光谱的整体装置连接示意图,其中,1:原位红外反应池;2:红外光谱仪;3:六通阀;4:质量流量计Figure 1 shows a schematic diagram of the connection of the overall device for in-situ infrared spectroscopy of the present invention, wherein, 1: in-situ infrared reaction cell; 2: infrared spectrometer; 3: six-way valve; 4: mass flow meter
图2显示为本发明的3A分子筛在30℃、60℃和90℃条件下,CO饱和吸附的红外谱图Figure 2 shows the infrared spectra of CO saturated adsorption of the 3A molecular sieve of the present invention at 30°C, 60°C and 90°C
图3显示为本发明的3A、4A、5A、13X、13Z和AA分子筛在30℃条件下,CO饱和吸附的红外谱图Figure 3 shows the infrared spectra of CO saturation adsorption for 3A, 4A, 5A, 13X, 13Z and AA molecular sieves of the present invention at 30°C
图4显示为本发明的13X分子筛在30℃条件下,巴豆醛,丙烯醛和乙醛饱和吸附的红外谱图Figure 4 shows the infrared spectrum of saturated adsorption of crotonaldehyde, acrolein and acetaldehyde under the condition of 30°C for 13X molecular sieve of the present invention
具体实施方式detailed description
下面结合具体实施例进一步阐述本发明,应理解,这些实施例仅用于说明本发明而不用于限制本发明的保护范围。The present invention will be further described below in conjunction with specific examples. It should be understood that these examples are only used to illustrate the present invention and are not intended to limit the protection scope of the present invention.
本实施例中选用材料包括仪器、样品和试剂如下所示:Materials selected in this embodiment include instruments, samples and reagents as follows:
1材料1 material
1.1仪器1.1 Instrument
DRK-4-NI8高温原位红外反应池(美国HARRICK公司);Nicolet5700傅里叶红外光谱仪(美国THERMOFISHER公司);C100L质量流量计(美国SIERRA公司);PMF-1六通阀(南京科立华仪器仪表有限公司)DRK-4-NI8 high temperature in-situ infrared reaction cell (HARRICK company, USA); Nicolet5700 Fourier transform infrared spectrometer (Thermofisher company, USA); C100L mass flow meter (SIERRA company, USA); PMF-1 six-way valve (Nanjing Kelihua Instrumentation Co., Ltd.)
1.2样品和试剂1.2 Samples and reagents
卷烟烟气成分:一氧化碳、巴豆醛、丙烯醛、乙醛(99.999%,上海基量标准气体有限公司);载气:氦气、氩气、氮气(99.9999%,上海基量标准气体有限公司);固体吸附材料:活性炭(Jacobi碳公司)、白炭黑(赢创工业集团)、离子交换树脂(美国陶氏公司)、分子筛:3A、4A、5A、13X、13Z、AA(上海绿强新材料有限公司)Cigarette smoke components: carbon monoxide, crotonaldehyde, acrolein, acetaldehyde (99.999%, Shanghai Jiliang Standard Gas Co., Ltd.); carrier gas: helium, argon, nitrogen (99.9999%, Shanghai Jiliang Standard Gas Co., Ltd.) ; Solid adsorption material: activated carbon (Jacobi carbon company), white carbon black (Evonik Industrial Group), ion exchange resin (Dow, USA), molecular sieve: 3A, 4A, 5A, 13X, 13Z, AA (Shanghai Lvqiangxin Materials Co., Ltd.)
实施例1Example 1
1.方法1. Method
1.1前处理1.1 Pre-processing
将固体吸附材料3A分子筛填充到原位红外反应池中,并将原位红外反应池安装在红外光谱仪中。通入纯度为99.9999%的氮气气体半小时(流速20mL/min)进行脱附程序,将原位反应池中以10℃/min的速度加热至120℃,并保持半小时,使得分子筛表面吸附物种脱附,分别降温至30、60、90℃,稳定半小时。将卷烟烟气成分CO与载气N2混合,通过管路引入原位红外反应池中,与固体吸附材料进行吸附反应。Fill the solid adsorption material 3A molecular sieve into the in-situ infrared reaction cell, and install the in-situ infrared reaction cell in the infrared spectrometer. Introduce nitrogen gas with a purity of 99.9999% for half an hour (flow rate 20mL/min) to carry out the desorption procedure, heat the in-situ reaction cell to 120°C at a rate of 10°C/min, and keep it for half an hour, so that the species adsorbed on the surface of the molecular sieve After desorption, the temperature was lowered to 30, 60, and 90°C respectively, and it was stable for half an hour. The cigarette smoke component CO is mixed with the carrier gas N 2 , introduced into the in-situ infrared reaction cell through the pipeline, and undergoes adsorption reaction with the solid adsorption material.
1.2测定1.2 Determination
针对引入原位红外反应池中与固体吸附材料进行吸附反应的混合气体,同步采用红外光谱仪测定固体吸附材料表面,连续采谱,在吸附反应达到饱和后停止采谱。For the mixed gas introduced into the in-situ infrared reaction cell for adsorption reaction with the solid adsorption material, the infrared spectrometer is used to measure the surface of the solid adsorption material simultaneously, and the spectrum is continuously collected, and the spectrum collection is stopped after the adsorption reaction reaches saturation.
原位红外反应池的反应条件为:混合气体CO与N2的体积百分含量之比:2%:98%;混合气体流速:20mL/min;吸附反应测试温度:30、60、90℃;反应时间:30min。The reaction conditions of the in-situ infrared reaction cell are: the volume percentage ratio of mixed gas CO to N2: 2 %:98%; mixed gas flow rate: 20mL/min; adsorption reaction test temperature: 30, 60, 90°C; Reaction time: 30min.
红外光谱仪测定条件为:光谱范围:4000-650cm-1;最高分辨率:0.4cm-1;信噪比:20000:1(P-P);分束器:KBr;检测器:MCT;光源:长寿命冷红外;灵敏度:10ppm;连续采样间隔:60s;采谱数量:73;检测时间:30min;扫描速度:24s扫描一个谱图。The measurement conditions of the infrared spectrometer are: spectral range: 4000-650cm -1 ; highest resolution: 0.4cm -1 ; signal-to-noise ratio: 20000:1 (PP); beam splitter: KBr; detector: MCT; light source: long life Cold infrared; sensitivity: 10ppm; continuous sampling interval: 60s; number of spectra: 73; detection time: 30min; scanning speed: 24s to scan a spectrum.
2分析结果与讨论2 Analysis Results and Discussion
将测定获得的红外谱图进行分析,具体谱图见图2。根据图2可知,在30℃和90℃的吸附温度下,3A分子筛对CO有较好的吸附。在30℃和60℃条件下,主要吸收峰在2013cm-1,归属为CO和单个Al原子的相互作用。在90℃条件下,主要吸收峰在1920cm-1和1865cm-1,分别归属为CO和两个Al原子的相互作用,以及CO和三个Al原子的相互作用。这里CO的浓度为2%,所测得的数据具有很高的灵敏度,信噪比S/N为=2500~8100。The infrared spectrum obtained by the determination is analyzed, and the specific spectrum is shown in Figure 2. According to Figure 2, at the adsorption temperatures of 30°C and 90°C, 3A molecular sieves have better adsorption of CO. At 30°C and 60°C, the main absorption peak is at 2013cm -1 , which is attributed to the interaction between CO and a single Al atom. At 90°C, the main absorption peaks are at 1920cm -1 and 1865cm -1 , which are attributed to the interaction between CO and two Al atoms, and the interaction between CO and three Al atoms, respectively. The concentration of CO here is 2%, the measured data has high sensitivity, and the signal-to-noise ratio S/N is =2500-8100.
由此可见,对于卷烟烟气成分CO,在不同温度条件下,吸附材料3A分子筛吸附能力不同,因此,选择接近室温的吸附温度25~30℃或高温90℃,都能有效吸附CO分子,同时在不同温度下,CO的吸附形式也是不同的。目前,常规的吸附材料,吸附性能随着温度的升高而降低,而这里我们发现了在不同温度下都能对卷烟烟气成分CO有较好吸附性能的吸附材料3A分子筛,有利于开发新型的且在不同温度下都有较好吸附性能的吸附材料。It can be seen that for CO, the component of cigarette smoke, under different temperature conditions, the adsorption capacity of the adsorption material 3A molecular sieve is different. Therefore, choosing an adsorption temperature close to room temperature of 25-30°C or a high temperature of 90°C can effectively adsorb CO molecules. At different temperatures, the adsorption forms of CO are also different. At present, the adsorption performance of conventional adsorption materials decreases with the increase of temperature, and here we found that the adsorption material 3A molecular sieve can have better adsorption performance on cigarette smoke component CO at different temperatures, which is conducive to the development of new It is an adsorbent material with good adsorption performance at different temperatures.
实施例2Example 2
1.方法1. Method
1.1前处理1.1 Pre-processing
分别将固体吸附材料4A、5A、13X、13Z、AA分子筛填充到原位红外反应池中,并将原位红外反应池安装在红外光谱仪中。通入纯度为99.9999%的氦气气体半小时(流速20mL/min)进行脱附程序,将原位反应池中以10℃/min的速度加热至120℃,并保持半小时,使得分子筛表面吸附物种脱附,分别降温至30℃,稳定半小时。将卷烟烟气成分CO与载气He混合,通过管路引入原位红外反应池中,与固体吸附材料进行吸附反应。Fill solid adsorption materials 4A, 5A, 13X, 13Z, and AA molecular sieves into the in-situ infrared reaction cell, and install the in-situ infrared reaction cell in the infrared spectrometer. Introduce helium gas with a purity of 99.9999% for half an hour (flow rate 20mL/min) to carry out the desorption procedure, heat the in-situ reaction cell to 120°C at a rate of 10°C/min, and keep it for half an hour to allow the surface of the molecular sieve to adsorb Species were desorbed, and the temperature was lowered to 30°C and stabilized for half an hour. The cigarette smoke component CO is mixed with the carrier gas He, and introduced into the in-situ infrared reaction cell through the pipeline, and undergoes adsorption reaction with the solid adsorption material.
1.2测定1.2 Determination
针对引入原位红外反应池中与固体吸附材料进行吸附反应的混合气体,同步采用红外光谱仪测定固体吸附材料表面,连续采谱,在吸附反应达到饱和后停止采谱。For the mixed gas introduced into the in-situ infrared reaction cell for adsorption reaction with the solid adsorption material, the infrared spectrometer is used to measure the surface of the solid adsorption material simultaneously, and the spectrum is continuously collected, and the spectrum collection is stopped after the adsorption reaction reaches saturation.
原位红外反应池的反应条件为:混合气体CO与He的体积百分含量之比:2%:98%;混合气体流速:20mL/min;吸附反应测试温度:30℃;反应时间:30min。The reaction conditions of the in-situ infrared reaction cell are: the volume percentage ratio of CO and He in the mixed gas: 2%:98%; the flow rate of the mixed gas: 20mL/min; the adsorption reaction test temperature: 30°C; the reaction time: 30min.
红外光谱仪测定条件为:光谱范围:4000-650cm-1;最高分辨率:0.4cm-1;信噪比:20000:1(P-P);分束器:KBr;检测器:MCT;光源:长寿命冷红外;灵敏度:10ppm;连续采样间隔:6s;采谱数量:73;检测时间:30min;扫描速度:24s扫描一个谱图。The measurement conditions of the infrared spectrometer are: spectral range: 4000-650cm -1 ; highest resolution: 0.4cm -1 ; signal-to-noise ratio: 20000:1 (PP); beam splitter: KBr; detector: MCT; light source: long life Cold infrared; sensitivity: 10ppm; continuous sampling interval: 6s; number of spectra: 73; detection time: 30min; scanning speed: 24s to scan a spectrum.
2分析结果与讨论2 Analysis Results and Discussion
将测定获得的红外谱图进行分析,具体谱图见图3。根据图3可知,13X和13Z分子筛的吸附能力比较强。13X和13Z分子筛的孔径为1nm,适合CO分子扩散到孔内,有利于孔内表面与CO分子相互作用,同时,13X和13Z分子筛的硅铝比其他分子筛高,表面的羟基和水较多,这样由于氢键作用吸附的CO分子也更多,综合以上两点13X和13Z分子筛表现了优越的CO吸附能力。图3中,2046cm-1和2021cm-1处的红外吸收峰可以归属为OH基团吸附的CO,2046cm-1和2021cm-1处的红外吸收峰可以归属为OH基团吸附的CO,1994cm-1和1970cm-1处的红外吸收峰可以归属为分子筛中金属离子吸附的CO。这里CO的浓度为2%,所测得的数据具有很高的灵敏度,信噪比S/N=270~45000。The infrared spectrum obtained by the determination was analyzed, and the specific spectrum is shown in Figure 3. According to Figure 3, it can be seen that the adsorption capacity of 13X and 13Z molecular sieves is relatively strong. The pore size of 13X and 13Z molecular sieves is 1nm, which is suitable for the diffusion of CO molecules into the pores, and is conducive to the interaction between the inner surface of the pores and CO molecules. At the same time, the silicon aluminum of 13X and 13Z molecular sieves is higher than other molecular sieves, and there are more hydroxyl groups and water on the surface. In this way, more CO molecules can be adsorbed due to the hydrogen bond. Based on the above two points, 13X and 13Z molecular sieves have shown superior CO adsorption capacity. In Figure 3, the infrared absorption peaks at 2046cm -1 and 2021cm -1 can be attributed to CO adsorbed by OH groups, and the infrared absorption peaks at 2046cm -1 and 2021cm -1 can be attributed to CO adsorbed by OH groups, and 1994cm - 1 The infrared absorption peaks at 1 and 1970 cm -1 can be assigned to the CO adsorbed by metal ions in the molecular sieve. The concentration of CO here is 2%, the measured data has high sensitivity, and the signal-to-noise ratio S/N=270-45000.
由此可见,对于卷烟烟气成分CO,在相同温度30℃条件下,选用不同的吸附材料,从中选择最佳的吸附材料代替现有常规的吸附材料。以此为鉴,在常规吸附材料表面修饰羟基、羰基等极性基团,能更有效地提高其吸附CO的能力,同时提高常规吸附材料的使用价值。It can be seen that for the CO component of cigarette smoke, different adsorbent materials are selected under the same temperature of 30°C, and the best adsorbent material is selected to replace the existing conventional adsorbent material. Taking this as a lesson, modifying polar groups such as hydroxyl groups and carbonyl groups on the surface of conventional adsorption materials can more effectively improve its ability to adsorb CO, and at the same time increase the use value of conventional adsorption materials.
实施例3Example 3
1.方法1. Method
1.1前处理1.1 Pre-processing
将固体吸附材料13X分子筛填充到原位红外反应池中,并将原位红外反应池安装在红外光谱仪中。通入纯度为99.9999%的氩气气体半小时(流速20mL/min)进行脱附程序,将原位反应池中以10℃/min的速度加热至120℃,并保持半小时,使得分子筛表面吸附物种脱附,降温至30℃,稳定半小时。分别将卷烟烟气成分巴豆醛、丙烯醛和乙醛与载气Ar混合,通过管路引入原位红外反应池中,与固体吸附材料进行吸附反应。Fill the solid adsorption material 13X molecular sieve into the in-situ infrared reaction cell, and install the in-situ infrared reaction cell in the infrared spectrometer. Introduce argon gas with a purity of 99.9999% for half an hour (flow rate 20mL/min) to carry out the desorption procedure, heat the in-situ reaction cell to 120°C at a rate of 10°C/min, and keep it for half an hour to allow the surface of the molecular sieve to adsorb Species desorption, cooling to 30 ° C, stable for half an hour. The cigarette smoke components crotonaldehyde, acrolein and acetaldehyde were mixed with the carrier gas Ar, and introduced into the in-situ infrared reaction pool through the pipeline, and carried out adsorption reaction with the solid adsorption material.
1.2测定1.2 Determination
针对与固体吸附材料进行吸附反应的混合气体,同步采用红外光谱仪测定固体吸附材料表面,连续采谱,在吸附反应达到饱和后停止采谱。For the mixed gas that undergoes adsorption reaction with the solid adsorption material, the infrared spectrometer is used simultaneously to measure the surface of the solid adsorption material, and the spectrum is continuously collected, and the spectrum collection is stopped after the adsorption reaction reaches saturation.
原位红外反应池的反应条件为:混合气体巴豆醛与Ar的体积百分含量之比:0.01%:99.99%;混合气体丙烯醛与N2的体积百分含量之比:0.01%:99.99%;混合气体乙醛与N2的体积百分含量之比:0.01%:99.99%;混合气体流速:20mL/min;吸附反应测试温度:30℃;反应时间:30min。The reaction conditions of the in-situ infrared reaction cell are: the volume percentage ratio of the mixed gas crotonaldehyde to Ar: 0.01%: 99.99%; the volume percentage ratio of the mixed gas acrolein to N2 : 0.01%: 99.99% ; Volume percentage ratio of acetaldehyde to N 2 in mixed gas: 0.01%: 99.99%; Flow rate of mixed gas: 20mL/min; Adsorption reaction test temperature: 30°C; Reaction time: 30min.
红外光谱仪测定条件为:光谱范围:4000-650cm-1;最高分辨率:0.4cm-1;信噪比:20000:1(P-P);分束器:KBr;检测器:MCT;光源:长寿命冷红外;灵敏度:10ppm;连续采样间隔:6-60s;采谱数量:73;检测时间:30min;扫描速度:24s扫描一个谱图。The measurement conditions of the infrared spectrometer are: spectral range: 4000-650cm -1 ; highest resolution: 0.4cm -1 ; signal-to-noise ratio: 20000:1 (PP); beam splitter: KBr; detector: MCT; light source: long life Cold infrared; sensitivity: 10ppm; continuous sampling interval: 6-60s; number of spectra: 73; detection time: 30min; scanning speed: 24s to scan a spectrum.
2分析结果与讨论2 Analysis Results and Discussion
将测定获得的红外谱图进行分析,具体谱图见图4。根据图4可知,具体红外吸收峰的位置在图中已标注,丙烯醛在13X分子筛表面的吸附较巴豆醛和乙醛吸附吸附强,同时可以发现当3种烟气成分在13X分子筛表面发生吸附后,1654cm-1处出现了负峰,而此处归属于水和羟基的红外吸收位。所以可以得到的信息是,巴豆醛、丙烯醛和乙醛在13X分子筛表面的吸附形式为,醛基上的氧原子和分子筛表面的水和羟基发生氢键相互作用。所测得的数据具有很高的灵敏度,信噪比S/N=400~1270。The infrared spectrum obtained by the determination is analyzed, and the specific spectrum is shown in Figure 4. According to Figure 4, the position of the specific infrared absorption peak is marked in the figure, and the adsorption of acrolein on the surface of 13X molecular sieve is stronger than that of crotonaldehyde and acetaldehyde. Finally, a negative peak appeared at 1654cm -1 , which was attributed to the infrared absorption of water and hydroxyl. Therefore, the information that can be obtained is that the adsorption form of crotonaldehyde, acrolein and acetaldehyde on the surface of 13X molecular sieve is that the oxygen atoms on the aldehyde group interact with the water and hydroxyl groups on the surface of the molecular sieve. The measured data has high sensitivity, and the signal-to-noise ratio S/N=400-1270.
由此可见,对于卷烟烟气成分中不同气体成分,在相同温度30℃条件下,选用合适的吸附材料,可以代替现有的常规吸附材料。而且在其他较廉价的常规固体吸附材料表面修饰羟基、羰基等极性官能团,可以达到与价格较昂贵的固体吸附材料相同的吸附能力,提高其使用价值。It can be seen that, for different gas components in cigarette smoke, at the same temperature of 30°C, the selection of suitable adsorption materials can replace the existing conventional adsorption materials. Moreover, modifying polar functional groups such as hydroxyl group and carbonyl group on the surface of other relatively cheap conventional solid adsorption materials can achieve the same adsorption capacity as the more expensive solid adsorption materials and improve its use value.
综上所述,本发明的一种测定卷烟烟气成分在固体吸附材料表面的吸附形式的方法,研究卷烟烟气成分中挥发或者半挥发性成分在固体吸附材料上的吸附形式,同时能定性分析不同吸附活性位的的表面吸附量,根据所得到的实验结果,从而判定不同固体吸附材料表面吸附活性位的吸附能力,从而利用一些廉价的吸附材料,对其表面修饰具有特定吸附能力的官能团,达到与价格较昂贵的固体吸附材料具有相同的吸附能力。为卷烟滤嘴固体吸附材料的改性和开发提出更有价值的信息,满足卷烟减害技术发展的需求。所以,本发明有效克服了现有技术中的种种缺点而具高度产业利用价值。In summary, a method for measuring the adsorption form of cigarette smoke components on the surface of solid adsorbent materials according to the present invention is used to study the adsorption forms of volatile or semi-volatile components in cigarette smoke components on solid adsorbent materials, and can also qualitatively Analyze the surface adsorption capacity of different adsorption active sites, and according to the obtained experimental results, determine the adsorption capacity of different solid adsorption materials surface adsorption active sites, so as to use some cheap adsorption materials to modify the surface with functional groups with specific adsorption capacity , to achieve the same adsorption capacity as the more expensive solid adsorption materials. Provide more valuable information for the modification and development of cigarette filter solid adsorption materials, and meet the needs of the development of cigarette harm reduction technology. Therefore, the present invention effectively overcomes various shortcomings in the prior art and has high industrial application value.
上述实施例仅例示性说明本发明的原理及其功效,而非用于限制本发明。任何熟悉此技术的人士皆可在不违背本发明的精神及范畴下,对上述实施例进行修饰或改变。因此,举凡所属技术领域中具有通常知识者在未脱离本发明所揭示的精神与技术思想下所完成的一切等效修饰或改变,仍应由本发明的权利要求所涵盖。The above-mentioned embodiments only illustrate the principles and effects of the present invention, but are not intended to limit the present invention. Anyone skilled in the art can modify or change the above-mentioned embodiments without departing from the spirit and scope of the present invention. Therefore, all equivalent modifications or changes made by those skilled in the art without departing from the spirit and technical ideas disclosed in the present invention should still be covered by the claims of the present invention.
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