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TW201247115A - Smoking articles - Google Patents

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Publication number
TW201247115A
TW201247115A TW101105014A TW101105014A TW201247115A TW 201247115 A TW201247115 A TW 201247115A TW 101105014 A TW101105014 A TW 101105014A TW 101105014 A TW101105014 A TW 101105014A TW 201247115 A TW201247115 A TW 201247115A
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TW
Taiwan
Prior art keywords
tobacco
smoking
smoking article
carbon
smoke
Prior art date
Application number
TW101105014A
Other languages
Chinese (zh)
Inventor
David John Dittrich
Peter James Branton
Michael Arthur John Bevan
Original Assignee
British American Tobacco Co
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
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Publication date
Priority claimed from GBGB1102785.1A external-priority patent/GB201102785D0/en
Priority claimed from GBGB1113614.0A external-priority patent/GB201113614D0/en
Application filed by British American Tobacco Co filed Critical British American Tobacco Co
Publication of TW201247115A publication Critical patent/TW201247115A/en

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Classifications

    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24BMANUFACTURE OR PREPARATION OF TOBACCO FOR SMOKING OR CHEWING; TOBACCO; SNUFF
    • A24B15/00Chemical features or treatment of tobacco; Tobacco substitutes, e.g. in liquid form
    • A24B15/10Chemical features of tobacco products or tobacco substitutes
    • A24B15/16Chemical features of tobacco products or tobacco substitutes of tobacco substitutes
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24BMANUFACTURE OR PREPARATION OF TOBACCO FOR SMOKING OR CHEWING; TOBACCO; SNUFF
    • A24B15/00Chemical features or treatment of tobacco; Tobacco substitutes, e.g. in liquid form
    • A24B15/18Treatment of tobacco products or tobacco substitutes
    • A24B15/24Treatment of tobacco products or tobacco substitutes by extraction; Tobacco extracts
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24BMANUFACTURE OR PREPARATION OF TOBACCO FOR SMOKING OR CHEWING; TOBACCO; SNUFF
    • A24B15/00Chemical features or treatment of tobacco; Tobacco substitutes, e.g. in liquid form
    • A24B15/18Treatment of tobacco products or tobacco substitutes
    • A24B15/24Treatment of tobacco products or tobacco substitutes by extraction; Tobacco extracts
    • A24B15/241Extraction of specific substances
    • A24B15/245Nitrosamines
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24BMANUFACTURE OR PREPARATION OF TOBACCO FOR SMOKING OR CHEWING; TOBACCO; SNUFF
    • A24B15/00Chemical features or treatment of tobacco; Tobacco substitutes, e.g. in liquid form
    • A24B15/18Treatment of tobacco products or tobacco substitutes
    • A24B15/24Treatment of tobacco products or tobacco substitutes by extraction; Tobacco extracts
    • A24B15/241Extraction of specific substances
    • A24B15/248Heavy metals
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24DCIGARS; CIGARETTES; TOBACCO SMOKE FILTERS; MOUTHPIECES FOR CIGARS OR CIGARETTES; MANUFACTURE OF TOBACCO SMOKE FILTERS OR MOUTHPIECES
    • A24D1/00Cigars; Cigarettes
    • A24D1/18Selection of materials, other than tobacco, suitable for smoking
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24DCIGARS; CIGARETTES; TOBACCO SMOKE FILTERS; MOUTHPIECES FOR CIGARS OR CIGARETTES; MANUFACTURE OF TOBACCO SMOKE FILTERS OR MOUTHPIECES
    • A24D3/00Tobacco smoke filters, e.g. filter-tips, filtering inserts; Filters specially adapted for simulated smoking devices; Mouthpieces for cigars or cigarettes
    • A24D3/06Use of materials for tobacco smoke filters
    • A24D3/08Use of materials for tobacco smoke filters of organic materials as carrier or major constituent
    • A24D3/10Use of materials for tobacco smoke filters of organic materials as carrier or major constituent of cellulose or cellulose derivatives
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24DCIGARS; CIGARETTES; TOBACCO SMOKE FILTERS; MOUTHPIECES FOR CIGARS OR CIGARETTES; MANUFACTURE OF TOBACCO SMOKE FILTERS OR MOUTHPIECES
    • A24D3/00Tobacco smoke filters, e.g. filter-tips, filtering inserts; Filters specially adapted for simulated smoking devices; Mouthpieces for cigars or cigarettes
    • A24D3/06Use of materials for tobacco smoke filters
    • A24D3/12Use of materials for tobacco smoke filters of ion exchange materials
    • AHUMAN NECESSITIES
    • A24TOBACCO; CIGARS; CIGARETTES; SIMULATED SMOKING DEVICES; SMOKERS' REQUISITES
    • A24DCIGARS; CIGARETTES; TOBACCO SMOKE FILTERS; MOUTHPIECES FOR CIGARS OR CIGARETTES; MANUFACTURE OF TOBACCO SMOKE FILTERS OR MOUTHPIECES
    • A24D3/00Tobacco smoke filters, e.g. filter-tips, filtering inserts; Filters specially adapted for simulated smoking devices; Mouthpieces for cigars or cigarettes
    • A24D3/06Use of materials for tobacco smoke filters
    • A24D3/16Use of materials for tobacco smoke filters of inorganic materials
    • A24D3/163Carbon

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Cigarettes, Filters, And Manufacturing Of Filters (AREA)
  • Manufacture Of Tobacco Products (AREA)

Abstract

A smoking article comprising at least two of: (a) a tobacco blend comprising one or more tobaccos or tobacco grades with low TSNA and/or metal content; (b) a tobacco blend that has been treated to remove polyphenols and/or peptides; (c) a tobacco substitute sheet comprising a non-combustible inorganic filler, a binder and an aerosol generating means; (d) a high activity carbon comprising a polymer-derived carbon material; and (e) an amine-functionalised chelating resin.

Description

201247115 六、發明說明: 【發明所屬之技術領域】 本發明係關於吸煙物件,且特別係關於結合二或更多 技術應用以個別降低主流煙中特定成分或成分群的機器測 量出量的吸煙物件。 【先前技術】 終草煙係由超過5000種已確認之成分組成的複雜動態 混合物,其中約150種已證實為不良成分。這些成分存在 於吸煙者吸入的主流煙(MS),且在吞雲吐霧間釋出成側流 煙(SS)的成分。 西元2001年醫學研究機構(I0M)報導指出,由於吸煙 相關疾病與劑量有關,又因流行病學研究顯示戒煙後可降 .低得到吸煙相關疾病的風險’故開發潛在減少接觸產品 (PREP),可降低吸煙相關風險。其定義為:⑴可實質減少 接觸一或更多菸草毒物的產品;和(2)若宣稱風險降低,則 可合理預期降低得到一或更多特殊疾病或受到其他有害健 康影響的風險的產品(Stratton等人,2〇〇1)。迄今仍無符合 I0M總體要求的可燃捲菸產品問世。 σ Ι0Μ和其他團體(生命科學研究室(LSR〇)2〇〇7 ;世界衛 生組織〇νΗΟ)2007)描述可燃菸草產品被認定為pREp可能 需要的-些作業階段’然科學界對提供相關資料所需的詳二 方式和階段莫衷-是。例如,-些圑紅就敎煙成分提出 MS出量極限,其他團體則建議評估時應採行生物心則。 4 2〇1247ll5 近年來許多研究熱中於減少特定MS成分。種種方、 針對吸煙物件的不同部分,並致力於減少含量去已 移除特定化合物,例如利用基因工程或摻合特料 處理乃試圖在併入吸煙物件前,減少或去除菸草材料的 物二許多方式嘗試利用各類稀釋劑或填料來,,稀釋,,吸煙物: 的菸草棒中的菸草。其他方式涉及使吸煙物件通風,以將周 圍空氣抽入吸煙物件而稀釋MS。過濾顯然是另一領域]^ 中有很多研究加強去除通過吸煙物件濾嘴段的成分。、: 些個別措施都有益處,但其一般只解決全貌的一小部分。= 另一待解決的課題為生產消費者可接受產品的重要 性。習用吸煙物件的感官衝擊大多基於MS成分。去除某此 成分很可能提供吸煙者不甚滿足的吸煙體驗。 、— 故提供大幅減少所有不良MS成分排放的吸煙物件為 一大挑戰。然減少特定成分的個別措施常常導致其他成分不 會減少,在一些情況下,甚至會增加其他成分的含量。 利用濾嘴通風孔或高滲透性捲菸紙來稀釋煙,可減少整 體吸煙機測量毒物出量,且對特殊煙相相關的毒物而言,可 藉由提兩遽嘴的過遽效率達成。多年來,政府和世界各地的 公共衛生機構視較少iso焦油產出捲菸為降低未戒煙者吸 煙的健康風險的方式。然此產品改質方式近來飽受批評。世 界衛生組織的菸草產品管制研究小組(TobReg)近來提出限 制選定特殊煙成分群出量的管制方式。此小組還建議應依據 以強烈吸煙機定制測量的出量來限制成分出量,及測定每毫 克的尼古丁。 5 201247115 八相對機器測量焦油和尼古丁出i,選擇性減少特定煙 外方式與烟成分的理化本質息息相關。習知捲終設 用f在相對減少煙成分方面的能力有限。例如,提高習 隹乙酸纖維素(CA)濾嘴的過濾效率時,特殊相成分將伴隨 =油與尼古丁減少,選擇性減少的情況很少或根本沒發 &担2於乙酸纖維素濾嘴對揮發性成分毫無或影響極微, θ濾效率可提高其相對焦油與尼古丁的出量比率。 提同濾嘴通風對煙成分有各種影響。所有煙成分的絕 量減乂、’但特殊相成分相對焦油或尼古丁的出量大多 不4或甚至可能增加。一些揮發性成分(如氨和一氧化碳) 相對焦油與尼古丁的出量減少,-些半揮發性成分(如紛) 的相對出量則增加。 遽嘴中使用諸如活性炭或某些樹脂等吸附材料,可選 擇性減少s午多揮發性氣相組分,例如揮發性醛類和氰化 氫。然永久氣體(如一氧化碳和一氧化氮)在室溫下無法吸 附’且其緊緊結合氣溶膠微粒,是以過濾無法選擇性減少 特殊相中的毒物。 自1950年起已試圖選擇性從捲菸煙移除或減少成分。 利用多孔吸附劑吸附可去除煙的一些揮發性成分。活性碳 (AC)係非選擇性吸附劑,其泛用於捲菸濾嘴,並透過物理 吸附而大幅減少各種揮發性煙成分。然不應低估此挑戰的 難度。使用捲菸煙吸附劑時,需在高流率條件下操作(典型 機器吸煙條件為約1升每分鐘),故煙成分與過濾吸附劑的 接觸時間非常短(數秒)。吸附劑亦需於氣固界面(即不在溶 ⑤ 6 201247115 液内)作用、,’且氣相與微粒相中存在數千種其他化學品。吸 附劑表面尚易因煙氣溶膠微粒凝結而阻塞。對永久氣體和 在周溫下具高蒸汽壓的煙成分(如甲醛、乙醛或HCN)而 言,物理吸附不太有效,故需要替代途徑。 捲菸煙含有一些揮發性醛類,包括飽和化合物(如曱 醛、乙醛、内醛和丁醛)與不飽和化合物(如丙烯醛和巴豆 酿)。捲於煙中的駐要由—祕草成分(主要為碳水化合物) 燃燒產生特別地,糖被認為是捲終煙中甲搭的主要來源。 纖維素為主流煙中乙醛的主要前驅物。—些資料指出,甘 油(有時加入菸草做為保濕劑的材料)係丙烯醛的附加前驅 物。雖,然曱駿的;弗·點係負溫,但離開過丨慮捲於的主流煙有 30%的曱〃_留於特殊相而無法在室溫下選擇性過滤。因存 有水蒸汽,特殊煙相中的曱醛以水合形式”CH2(〇H)2”存 在。乙路(捲於煙的最高出量成分之一)在周溫下以其彿點或 左右存在,故有很高的蒸汽壓。這兩種因素結合導致以濾 嘴添加劑實質移除煙流中的乙醛變成一大挑戰。 實質具體減少習知捲於構造的特殊成分的一可行方式 為改質菸草。將不同菸草種類替換成摻合物將影響數種煙 成分出量。例如,白肋種菸草的含氮煙成分出量比火烤或 東方種多,火烤種菸草的曱醛和兒茶酚出量較多。然減少 某一或某組成分往往要增加其他成分來彌補。為避免如 此,能鑑定及從菸葉移除煙成分的前驅物是有益的。 除金屬成分(鉻、鎳、砷、硒、録、采和錯)與一些菸草 特有亞硝胺(TSNA ’例如n AT和NAB,其直接從菸葉轉移) 201247115 ΐ并熱合成所形成。故揮發性幾、 人 氧化衩、本和曱苯的前驅物大多 巧=糖。含氮煙成分由:葉= 认士 战,大置證據顯不,蛋白質和脫1 二拿大衛生部名單上數麵煙成分。ΐΓΐί助 胺1自㈣㈣歧變雜環 (火烤為祕煙化合物的主要前驅物。綠原酸 主要前驅物,5的多⑽係笨酚、兒茶紛和取代兒茶盼的 咖啡酸亦因妖=—_報為綠原酸熱解產物。芸香苦和 草中的兒茶驗和取代兒茶紛,但由於其在柊 的兒茶紛且熱解產率較低’故其對火烤種於草煙中 要熱解產物小於綠原酸。間苯二㈣知為芸香苷的主 【發明内容】 組合:發訂製菸草摻合物與訂製 吸附過遽添加劑的 口更具體造ΐ吸煙物件的不良主流煙成分大幅減少。 (a)菸而S,本發明提供吸煙物件,包含下列至少二者: 审^ ^ δ物包含具低TSNA及/或金屬含量的一或 更多_柃草或菸草等級; 其已經處理移除㈣及/或胜肽(可溶與 ⑤ 8 201247115 (c) 於草代替片,包含不燃無機填料、黏結劑與氣溶膠 產生用具; / (d) 高活性碳,包含聚合物衍生碳材料;以及 (e) 胺官能化螯合樹脂。 在一較佳具體實例中,根據本發明的吸煙物件為使在 此定義的關鍵主流煙成分減少至少75%,較佳為至少 90%,更佳為全部。 在本發明中,所謂MS的”關鍵成分”係指文獻鑑定為不 t 的後氣令(如參 t’The Scientific Basis of Tobacco Product201247115 VI. OBJECTS OF THE INVENTION: TECHNICAL FIELD OF THE INVENTION The present invention relates to smoking articles, and in particular to machine-measured smoking articles that combine two or more technical applications to individually reduce specific components or groups of components in mainstream smoke. . [Prior Art] Endemic tobacco is a complex dynamic mixture of more than 5,000 identified ingredients, of which about 150 have been shown to be undesirable. These ingredients are present in mainstream smoke (MS) inhaled by smokers and are released as components of sidestream smoke (SS) during swallowing. In 2001, the Institute of Medical Research (I0M) reported that because of the dose-related diseases associated with smoking, and because epidemiological studies have shown that smoking cessation can be reduced and the risk of smoking-related diseases is low, the development of potential reduced contact products (PREP), Can reduce the risk associated with smoking. It is defined as: (1) a product that substantially reduces exposure to one or more tobacco poisons; and (2) a product that is reasonably expected to reduce the risk of acquiring one or more specific diseases or other adverse health effects if the risk is reduced ( Stratton et al., 2〇〇1). To date, there are still no combustible cigarette products that meet the overall requirements of I0M. σ Ι0Μ and other groups (Life Science Research Laboratory (LSR〇) 2〇〇7; World Health Organization 〇νΗΟ) 2007) describe the flammable tobacco products identified as pREp may be required - some of the operational phases 'the scientific community to provide relevant information The detailed two methods and stages required are not - yes. For example, some blushers impose MS limits on smog components, while others recommend biospheres for evaluation. 4 2〇1247ll5 In recent years, many studies have focused on reducing specific MS components. Variety, targeting different parts of smoking articles, and working to reduce the amount of specific compounds that have been removed, such as using genetic engineering or blending special treatments, trying to reduce or remove tobacco material before incorporating smoking articles. Ways to try to use a variety of thinners or fillers to, dilute,, smoking: tobacco in tobacco rods. Other methods involve venting the smoking article to draw ambient air into the smoking article to dilute the MS. Filtration is clearly another area where there are many studies that enhance the removal of components through the filter segment of smoking objects. , : Some individual measures are beneficial, but they generally only solve a small part of the whole picture. = Another issue to be addressed is the importance of producing acceptable products for consumers. The sensory impact of conventional smoking objects is mostly based on the MS component. Removal of one of these ingredients is likely to provide a smoking experience that is not well met by smokers. — Therefore, providing smoking items that significantly reduce emissions of all undesirable MS components is a major challenge. However, individual measures to reduce specific ingredients often result in no reduction in other ingredients and, in some cases, even increase in other ingredients. The use of filter vents or high-permeability cigarette papers to dilute the smoke reduces the amount of toxic emissions measured by the entire smoking machine, and can be achieved by raising the efficiency of the two cigarettes for the specific smoke-related toxicants. Over the years, governments and public health agencies around the world have seen less iso tar-derived cigarettes as a way to reduce the health risks of smokers who do not quit smoking. However, this product modification method has recently been criticized. The World Health Organization's Tobacco Control Research Group (TobReg) has recently proposed a regulatory approach that limits the selection of specific smoke constituents. The team also recommended limiting the amount of ingredient to be measured based on a custom measurement of a strong smoking machine and measuring nicotine per milligram. 5 201247115 Eight relative machines measure tar and nicotine, and the selective reduction of specific smoke patterns is closely related to the physical and chemical nature of smoke constituents. Conventional volumes have a limited ability to reduce the composition of smoke. For example, when increasing the filtration efficiency of a cellulose acetate (CA) filter, the specific phase components will be accompanied by a decrease in oil and nicotine, and the selectivity will be reduced with little or no hair & With little or no effect on volatile components, θ filtration efficiency increases the ratio of relative tar to nicotine. Filing with the filter has various effects on the composition of the smoke. The absolute reduction of all smoke components, but the specific phase composition relative to tar or nicotine output is mostly not 4 or even likely to increase. Some volatile components (such as ammonia and carbon monoxide) have a reduced relative tar and nicotine output, and the relative yield of some semi-volatile components (such as sputum) increases. Adsorption materials such as activated carbon or certain resins are used in the mouth to selectively reduce the volatile components of the gas phase, such as volatile aldehydes and hydrogen cyanide. However, permanent gases (such as carbon monoxide and nitrogen monoxide) are not able to adsorb at room temperature and are tightly bound to aerosol particles, which are filters that do not selectively reduce poisons in the particular phase. Since 1950, attempts have been made to selectively remove or reduce ingredients from cigarette smoke. Adsorption with a porous adsorbent removes some of the volatile constituents of the smoke. Activated carbon (AC) is a non-selective adsorbent that is widely used in cigarette filters and greatly reduces various volatile smoke components through physical adsorption. However, the difficulty of this challenge should not be underestimated. When using a cigarette smoke adsorbent, it is required to operate under high flow rate conditions (typical machine smoking conditions are about 1 liter per minute), so the contact time of the smoke component with the filtered adsorbent is very short (several seconds). The adsorbent also needs to act at the gas-solid interface (ie, not in solution), and there are thousands of other chemicals in the gas phase and particulate phase. The surface of the adsorbent is also likely to clog due to condensation of the aerosol particles. For permanent gases and smoke constituents with high vapor pressure at ambient temperature (such as formaldehyde, acetaldehyde or HCN), physical adsorption is less effective and an alternative route is required. Cigarette smoke contains some volatile aldehydes, including saturated compounds (such as furfural, acetaldehyde, internal aldehydes and butyraldehyde) and unsaturated compounds (such as acrolein and croton). The presence in the smoke is caused by the burning of the secret ingredients (mainly carbohydrates). In particular, sugar is considered to be the main source of the net in the final smoke. Cellulose is the main precursor of acetaldehyde in mainstream smoke. — Some sources indicate that glycerol (sometimes added to tobacco as a humectant) is an additional precursor to acrolein. Although, it is Jun Jun's; Fu · point is negative temperature, but the mainstream smoke that has left the care is 30% of the 曱〃 _ left in the special phase and can not be selectively filtered at room temperature. The furfural in the special flue phase exists in the hydrated form "CH2(〇H)2" due to the presence of water vapor. B Road (one of the highest output components of the cigarette) is present at its peripheral temperature at its point of view or around, so it has a high vapor pressure. The combination of these two factors has led to a substantial challenge in the substantial removal of acetaldehyde from the plume with the filter additive. A practical way to specifically reduce the specific components of a conventional structure is to upgrade tobacco. Replacing different tobacco species into blends will affect several smoke constituents. For example, the amount of nitrogen-containing smoke constituents of burley tobacco is higher than that of fire-roasted or oriental species, and the amount of furfural and catechol produced by fire-cured tobacco is more. However, reducing one or a certain component often requires adding other components to make up for it. To avoid this, it is beneficial to be able to identify and remove precursors of the smoke constituents from the tobacco leaves. In addition to metal components (chromium, nickel, arsenic, selenium, germanium, and mis-), some tobacco-specific nitrosamines (TSNA ', such as n AT and NAB, which are directly transferred from tobacco leaves) 201247115 are formed by hydrazine thermal synthesis. Therefore, the precursors of volatility, human cerium oxide, and benzene are mostly sugars. The composition of nitrogen-containing smoke consists of: leaf = knives, warfare, and evidence of protein, and the number of cigarettes on the list of the Ministry of Health. ΐΓΐ 助 助 助 助 助 助 ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( The demon =-_ is reported as the pyrolysis product of chlorogenic acid. The catechu tea in the scent of scent and the grass replaces the catechu tea, but because of its low catechin and low pyrolysis yield, it is roasted on fire. The pyrolysis product is less than chlorogenic acid in the grass tobacco. The main content of the meta-benzene di(4) is known as rutin. The combination: the combination of the custom-made tobacco blend and the custom-adsorbed antimony additive is more specific. The undesirable mainstream smoke constituents of smoking articles are substantially reduced. (a) Smoke and S, the present invention provides smoking articles comprising at least two of the following: The test ^ ^ δ contains one or more of the low TSNA and / or metal content _ 柃Grass or tobacco grade; it has been treated to remove (iv) and/or peptides (soluble and 5 8 201247115 (c) in grass substitute tablets, containing non-combustible inorganic fillers, binders and aerosol generating appliances; / (d) high activity Carbon, comprising a polymer-derived carbon material; and (e) an amine functionalized chelating resin. In an embodiment, the smoking article according to the present invention is such that at least 75%, preferably at least 90%, and more preferably all of the key mainstream smoke constituents defined herein are reduced. In the present invention, the term "key component" of MS means The literature is identified as a post-gas order that does not t (eg, t'The Scientific Basis of Tobacco Product

Regulation: Report of a WHO Study Group (2007) WHO 以心r/aPC’’,日内瓦)及/或在此提供資料已 分析出量者(如參見表6、7和8)。 減少情形較佳係利用表3所列吸煙機條件測定。較佳 地,在Health Canada Intense吸煙機條件下測量減少出量。 關鍵成分出量較佳減少至少5%或至少1〇%或以上。 較佳地’當本發明吸煙物件包括包含具低TSNA及/或 金屬含量的一或更多於草或於草等級的菸草摻合物時,其 更包含如(b)至(e)所列的二或更多其他技術。 【實施方式】 把以菸草代替片(TSS)或菸草摻合物處理(BT)為特徵 的二低毒性菸草摻合物結合含胺官能化樹脂(CR20L)及/或 201247115 高活性碳吸附劑(HAC)的濾嘴,以產生三種實驗捲菸(EC) D 在四種不同吸煙機條件下測定煙成分的主流煙(Mg)出量。 Health Canada Intense (HCI)機器吸煙條件提供無尼古丁乾 顆粒物質和多數待測煙成分的最高MS出量。比較ec的成 分出莖與兩種市售比較(CC)捲終、三種科學對照(sc)捲於 和120個市售捲於的公開資料。茲發現ec產生一些捲於的 最低機器成分出量,其可利用HCI煙化學。故比較結果證 實EC產生的MS機器成分出量比市售捲菸少。 設計捲菸基PREP的第一階段涉及開發減少煙成分出 量的技術。利用這些技術組裝實驗捲菸(EC),接著以吸煙 機評估其成分出量;比較相關對照與參考產品,表示捲菸 設計在產生減少成分出量方面的效用。與參考產品相比, 可減少煙成分的吸煙機測量出量的EC稱為,,減少機器出量 原型(RMYP)”。 本發明描述減少捲菸煙的成分的不同個別技術方式, 其一涉及選擇菸草摻合物組分而提供具少量已知不良煙成 分的前驅物的摻合物,其中兩個為改質於草,又其中兩個 為改質捲菸濾嘴。菸草摻合物(TB)、菸草代替片材料(TSS) 和菸草摻合物處理(B T)減少在燃燒捲菸内的根源產生成 分。二過濾技術(胺官能化樹脂材料(CR2〇L)和高活性聚合 物衍生碳吸附劑(HAC))於形成後從煙流移除揮發性物種。 這些技術將詳述於後(第2.1節)。 菸草摻合物 此涉及選擇菸草摻合物組分,其呈少量不良煙成分的 前驅物,例如TSNA和金屬。例如,使用特定(如較淡)菸草 201247115 摻合物及選擇含少量硝酸鹽(TSNA的前驅物)的部分菸草 作物,可減少TSNA含量。熟諳此技術者當知曉改變摻合 方法以提供預定性質之終草摻合物的方式。 菸草摻合物亦可包含膨脹菸草,其為經膨脹而減少捲 菸中菸草燃燒量的菸絲。膨脹方法類似製造爆米花零嘴的 方法。其一方法稱為乾冰膨脹菸草(DIET),且涉及在加熱 前,以液態二氧化碳浸透菸葉結構,產生的二氧化碳氣體 迫使菸草膨脹。一些標榜具低IS〇焦油出量的市售菸草品 牌在整體摻合物中使用某一比例的膨脹於草。 菸草摻合物處理 質和多酚的方法處理而對煙毒物出量有所助益。、 °菸草處王审Regulation: Report of a WHO Study Group (2007) WHO by heart r/aPC’', Geneva) and/or data provided here have been analyzed (see, for example, Tables 6, 7 and 8). The reduction is preferably determined using the smoking machine conditions listed in Table 3. Preferably, the reduced yield is measured under Health Canada Intense smoking machine conditions. The yield of key ingredients is preferably reduced by at least 5% or at least 1% or more. Preferably, when the smoking article of the present invention comprises a tobacco blend comprising one or more grass or grass grades having a low TSNA and/or metal content, it further comprises as listed in (b) to (e) Two or more other technologies. [Embodiment] A two-low toxicity tobacco blend characterized by tobacco substitute tablet (TSS) or tobacco blend treatment (BT) is combined with an amine-containing functional resin (CR20L) and/or 201247115 high activity carbon adsorbent ( HAC) filter to produce three experimental cigarettes (EC) D The mainstream smoke (Mg) output of the smoke constituents was determined under four different smoking machine conditions. Health Canada Intense (HCI) machine smoking conditions provide the highest MS yield of no nicotine-free particulate matter and most smoke components to be tested. Compare the ec component stems with two commercially available (CC) volumes, three scientific controls (sc), and 120 publicly available volumes. It has been found that ec produces some of the lowest machine component yields that can be utilized for HCI smoke chemistry. Therefore, the comparison results show that the EC produces less MS machine components than commercial cigarettes. The first phase of designing a cigarette-based PREP involves developing techniques to reduce the amount of smoke constituents. These techniques were used to assemble experimental cigarettes (EC), which were then evaluated by a smoking machine; the relevant controls and reference products were compared to indicate the utility of the cigarette design in producing reduced component yields. Compared with the reference product, the EC that can reduce the smoked component of the smoke component is referred to as, reduce the machine output prototype (RMYP). The present invention describes different individual technical means for reducing the composition of the cigarette smoke, one of which involves selection The tobacco blend component provides a blend of precursors with a small amount of known undesirable smoke constituents, two of which are modified to grass, and two of which are modified cigarette filters. Tobacco Blend (TB) , Tobacco Substitute Sheet (TSS) and Tobacco Blend Treatment (BT) reduce the root-derived components in burning cigarettes. Two filtration techniques (amine functionalized resin material (CR2〇L) and high activity polymer derived carbon adsorbent (HAC)) Removal of volatile species from the plume after formation. These techniques will be detailed later (Section 2.1). Tobacco Blends This involves the selection of a tobacco blend component which is in the form of a small amount of undesirable smoke constituents. Precursors, such as TSNA and metals. For example, using a specific (eg, lighter) tobacco 201247115 blend and selecting a portion of the tobacco crop containing a small amount of nitrate (TSNA precursor) can reduce TSNA content. Change blending The tobacco blend may also comprise expanded tobacco, which is expanded tobacco which is expanded to reduce the amount of tobacco burned in the cigarette. The expansion method is similar to the method of manufacturing a popcorn nozzle. Known as dry ice expanded tobacco (DIET), and involves soaking the tobacco structure with liquid carbon dioxide before heating, the carbon dioxide gas generated forces the tobacco to expand. Some of the commercial tobacco brands advertised with low IS tar yield are in the overall blend. Use a certain proportion of expansion in the grass. Tobacco blend treatment and polyphenols are treated to help the yield of tobacco poisons.

,而不需重建成片材。 所,此描述已處理於草摻合物,其經可去除終草中蛋白 係施行於火烤Γ ^ 酶水溶液處理 物重新用於已j 利用習用捲菸1.…〜用取从條聆, 菸草代替片Without rebuilding into sheets. The description has been applied to the grass blend, which can be used to remove the protein from the final herb and to be used in the roasting of the enzyme. The aqueous solution of the enzyme has been reused for the use of conventional cigarettes. Replacement piece

泛輝發性物種, 评理,並提出 片。此實驗捲 ,大部分的測 減少煙毒物出量的另一 捲知包括至多達60%的含甘 於的主流煙分析顯示,除了 〜. 量成分出量將減少。 胺官能化樹脂材料A genus of genus, a review, and a film. In this experimental volume, most of the other measurements that reduce the amount of smoke poisoning include up to 60% of the analysis of the mainstream smoke that is shown to contain less than ~. Amine functionalized resin material

茲發現化學吸附能從主 。鑑定與二乙歸笨交聯 201247115 聚苯乙烯樹脂及評估其做為捲菸濾嘴添加劑的效果。三菱 化學公司製造的材料通常係以備於水環境的珠粒形式供 應,並依商品名稱Diaion®CR20(以下簡稱CR20)販售。此 材料提供從主流煙親核捕捉醛類的可能性,且因具弱鹼本 質’故其亦可用來去除MS中的HCN。 胺官能化螯合樹脂材料可併入吸煙物件的濾嘴孔穴或 分散(斑點型)遍及整個或一段濾嘴的濾嘴材料(如乙酸纖維 素)。 高活性碳 包含聚合物衍生碳球微粒的高活性材料可以適當方法 (Von Blucher 與 De Ruiter ’ 2004 ; Von Bliicher 等人,2006 ;I have found that the chemical adsorption energy is from the main. Identification and cross-linking of the second and second batches of 201247115 polystyrene resin and evaluation of its effect as a cigarette filter additive. Materials manufactured by Mitsubishi Chemical Corporation are usually supplied in the form of beads prepared for use in water, and are sold under the trade name Diaion® CR20 (hereinafter referred to as CR20). This material provides the possibility of nucleophilic capture of aldehydes from mainstream smoke and can also be used to remove HCN from MS due to its weak base nature. The amine functionalized chelating resin material can be incorporated into the filter pores of the smoking article or the filter material (e.g., cellulose acetate) that spreads (spotted) throughout the entire filter or section of the filter. Highly active carbon Highly active materials comprising polymer-derived carbon spheres can be suitably used (Von Blucher and De Ruiter' 2004; Von Bliicher et al., 2006;

Behringer 與 Fichtner,2〇〇8)製備’且可取自 BmcherBehringer and Fichtner, 2〇〇8) Preparation' and may be taken from Bmcher

GmbH(德國卜聚合物衍生材料錄揮發性捲於煙毒物的效 力通常約為當前碳據捲於產品常用椰殼财碳的兩倍。在 1=0與HCI吸煙定制下,利用規律和較小_捲於的聚合 物竹生碳表現良好。亦觀測到較高流率吸煙條件下的乙搭 去除極眼。 炭可併入吸煙物件的渡嘴孔穴或分散(斑點型) 遍及整個或-段渡嘴的濾嘴材料(如乙酸纖維素)。 EC的合及所述軸技術製作的EC。這些 二 出量的原型,並可減少人吸煙時吸煙者 二及:祕的煙成分 J出Ϊ比羊表不,並與相關市售比較 (g 12 201247115 捲終和文獻報導的各種產品相比。此作業結果證實發展可 燃RMYP係可行的。 2.材料與方法 2.1實驗、對照及比較捲菸設計 , 結合開發以減少菸草中特定煙毒物化學種類或其前驅 物(表1)的摻合及過濾技術來建構EC。就各EC選擇具低 TSNA與金屬含量的個別菸草等級,及摻合而提供實驗捲菸 設計低毒性起點。 表1用於建構實驗捲菸(EC)的技術 技術應用 捲菸組分 說明 潛在減少情形 菸草掺合物 (TB) 摻合物 選擇呈少量不良煙成 分的前驅物的菸草摻 合物組分 一些TSNA和金屬 菸草代替片 (TSS) 摻合物 菸草代替片減少菸草 可燃物及產生甘油攜 式煙 整團煙 菸草掺合物處 理(BT) 摻合物 蛋白酶處理的終草, 減少掺合物的蛋白氮 和多酚 氮系成分:芳香 胺、NAB、NAT、 NNK、NNN ;苯酚 胺官能化樹脂 珠粒(CR20L) 遽嘴 包括在濾嘴段内的胺 基官能化樹脂 HCN、HCHO、乙 醛和其他羰 而活性碳 (HAC) 濾嘴 包括在濾嘴段内的聚 合物衍生球形碳珠粒 氣相成分 13 201247115 於草摻合物處理 通過L言之^草摻合物施以水性萃取步驟,萃取物隨後 =個過滤階段而去除多紛和可溶胜肽。殘二草固 理,以移除不溶蛋白質。洗務及酶去活化後, 重新、,,。合菸竽固體和過濾的水性 、 酚醛、芳香胺、HCN和-減他〜° &理過程將導致 讓和異戍二稀的出量一也會他増:氣煙成分的煙出量減少’ 待萃取的菸草材料可為菸條、 在一較佳具體實例中,於草係切碎;^、切碎或磨碎於草。 也可萃取其絲草_。 4°_用所述方法 菸草材料可與萃取用溶劑混合而 终草材料的比按重量計可為10 : !至5〇成 至40 : 1,更佳為25 . 1 5 m · 1 λ. 較佳為20 . 1 ,.、、.1至30 .。在一特定較佳且妒眚相丨 中,,加入菸草材料的比按重量計為27 :广具體貫例 >谷劑可為有機溶液’但較佳為水溶 — 始’溶劑通常為水’但其亦可含有醇,例如=取二開 或者其可含有界面活性劑。可視欲自 甲醇’ 分,使用其他溶劑。 、旱卒取的特定成 可在15°C至85〇C下進行萃取,較佳传 :。萃取時,最好持續_料,伴上二。C下進 ,進行15分鐘至2小時。在—較佳具體實萃取 約20分鐘。 員列中,卒取進行 、、萃取期間,可溶於草組分從終草材 液。其包括尼古丁、糖、一些蛋白質示及進入溶 妝基酸、果膠、多 ⑤ 14 201247115 酚和香料。至多達約55%的初始菸草重量可能變成可溶 性。重要的是,菸草纖維中的果膠在整個萃取及處理過程 保持交聯,以維持菸草的纖維結構。因此,可將鈣加入用 於萃取菸草的溶劑和處理程序下游所用的任何溶液。 萃取後,流出漿料,以收集液態濾液(“母濾液”)。同時, 於其輸送時逆流洗滌而進一步萃取不溶菸草殘留物,以從 菸草移除盡可能多的可溶成分。 將新溶劑加到菸草及收集濾液(洗滌遽液)。將洗滌濾液 引到在上游處傳送帶上行進的傳入於草殘留物,以回收洗 滌濾液。可反覆收集洗滌濾液及上游再用於傳入菸草殘留 物數次,較佳為三次、四次或甚至五次。是以於傳送帶前 端收集的最終洗滌濾液將濃縮在可溶菸草成分,當其行經 濾嘴長度時,已從菸草殘留物移除。將最終洗滌濾液加到 新菸草而形成菸草漿料,以進一步回收供萃取之用。例如, 最終洗滌濾液可加入菸草混合槽,在此於萃取前形成菸草 漿料。故萃取方法可為連續方法,其利用回收洗滌濾液萃 取新菸草。只有在萃取開始係以新溶劑萃取菸草。一旦開 始萃取,即無新溶劑用於萃取,溶劑僅由回收洗滌濾液組 成。 繼續萃取時,可溶菸草成分中的萃取物變得更濃。這 些成分包括主要萃取期間萃取槽内進入溶液者(形成母濾 液)和次要萃取期間水平帶濾機上進入溶液者(形成洗滌濾 液)。 故最終濾、液包含母滤液和洗務濾、液。如此,過慮後產 生的菸草殘留物將無這些可溶於萃取用溶劑的成分。可於 15 4 4201247115 f 過濾終了壓榨已萃取菸草,以 «機析出的已萃祕草通液體。從水平 隨後加工最終攄液(以下稱為 ^ 於草產品的不良成分。不良成分^卒取物\去除最終 « A ^ *ν X 成刀包括蛋白質、多胜肽、胺 基酸、㈣、姐H亞俩和_化合物。然視為 需要的成分含1(如糖和尼古丁)仍不受影響,故已萃取終草 的風味和吸煙性質可媲美原材料。 在-較佳具體實例中,處理終草萃取物,以去除蛋白 質、多胜肽及/或胺基酸。利用不溶吸附劑,例如羥基磷灰 石或漂白土礦(如膨土或皂土)’可去除原菸草材料中至多達 60%的蛋白質。菸草萃取物較佳經皂土處理,以去除其中的 多胜肽。加到萃取物的皂土量可為最初待萃取菸草重量的 2%-4%。或者,菸草萃取物可送入含有水中皂土漿料的槽 内。適合漿料含有約7公斤(kg)的皂土備於約64kg的水中 (每小時量),例如7.13kg的皂土備於約64.18kg的水中(每 小時量)。在任何情況下,皂土濃度應夠高,以實質減少於 草萃取物的蛋白質含量,但也不宜太高,以免額外D及附尼 古丁。皂土處理亦可有效去除菸草萃取物所含的顏料化人 物,若其未去除,則萃取物濃縮後易變黑。使用足約的息 土處理萃取物,可減少顏料化合物量,使產品外觀不至過 暗。 皂土處逵後,利用離心及/或過濾’淨化出自漿料的菸 草萃取物。或可或亦可處理菸草萃取物,以去除其中的多 盼0 ⑤ 16 201247115 聚乙烯聚吡咯啶酮(PVPP)係針對多酚的不溶吸附劑, 其傳統上用於釀造業來去除啤酒中的多酚。加到萃取二的 PVPP量可為最初待萃取於草重量的5%-10°/。。此pypp量 能去除溶液中50°/〇-90〇/〇的多酚。咸信PVPP從菸草萃取二 移除多酚的最佳pH為約3。故添加適當酸(如氣氣酸)來降 低萃取物的,可提高PVPP吸附效率。 以PVPP吸附多酚的替代方式為將一或更多酶加入菸 草萃取物,使内含多酚降解。一適合酶為漆酵素(漆酚氧化 酶)。然本發明不限於只從菸草移除蛋白質及/或多h酚的方 法。替代或附加酶、劑或吸附劑可用於去除菸草萃取物中 的,他不良菸草成分。可從萃取物移除的其他不良菸 分實例包括硝酸鹽、胺和亞硝胺。 ; 一匕若欲去除菸草萃取物中的複數個成分,則可串聯嗖置 ::槽;”目應待去除不良成分的不同酶、劑:吸 單—牛1者’早—槽可含有複數個酶、劑或吸附劑,而以 含-除不良成分。例如,皂土或pvpp盛裝槽可包 蛋白哲if附加酶、劑或吸附劑,如此不僅去除菸草中的 J或苯盼,還移除一或更多其他不良成分。 經濃萃取物以移除選定不良成分後,萃取物較佳 到至多遠ln 50重量%的固體濃度。利用逆滲透能有效達 縮成約的固體濃度。湘降賴發11,可進一步濃 方法。隨接固體。可採用熟請此技術者已知力其他濃縮 然在邀重新結合已濃縮菸草萃取物和已萃取菸草。 取已於上已'農縮菸草萃取物重新結合前,最好進一步萃 '反/谷液中萃取的柊草,以移除一或更多不良成 17 201247115 分。可使用特別挑選來去除選定成分的酶,進一步萃取恭 草。在一較佳具體實例中,酶係蛋白分解酶,用以去除菸 草中的蛋白質。酶較佳為細菌或真菌酶,更佳為市面上食 品與洗滌劑產業用酶。酶可選自由SaVinase™、Neutl>aseTN/、 Enzobake™和AlcalaseTM所組成的群組,其皆可取自 Novozymes A/S。加到於草的蛋白分解酶量較佳為菸草材料 重量的0.1。/。至5%。例如,加到菸草的SavinaseTM量可為 約1重量%。可在選定酶溶液中重新攪拌菸草。漿料中水與 於草比按重量計可為10 : 1至50 :卜較佳為20 : i至4〇 : 1,更佳為25 · 1至30 . 1。在一特定較佳具體實例中水 與菸草比按重量計為27 : 1。 於草/酶混合物的pH應能促進最佳酶活性。故將終草 脫水氈送入如藉由添加鹼(如氫氧化鈉)來調整pH的槽内係 便利的。接著將pH調整菸草送入供酶槽而與選定酶^合^ 隨後將於草/酶混合物送入塞流反應器,在此進行酶萃取。 酶萃取應在能促進最佳酶活性的溫度下進行。最好採用窄 溫度範圍(如30。(:-40。〇,以免酶變性。選用SavinaseTM時, ^佳作業條件為57〇c,pH為9_u。酶萃取應進行至少'乜 分鐘;咸信任何更短時間將不足以讓蛋白分解酶降解菸草 蛋白質。 若欲去除終草中的多個成分,當可進行多種酶萃取。 、可串聯進行’或可在單-處理步驟中將多種酶加到於草。 亦可在處理過程的最早萃取步驟、而 離萃取步驟引人酶。 卩縣成後續分 201247115 殘留:=ί洗=容:(較佳為氯化納溶液)洗務不溶於草 1 。可以連續逆流方式進行鹽沖洗。 f與水沖洗可能不足以移除料中的所有酶。亦 的草’使任何經鹽與水沖洗後殘留在菸草中 :ΓΓ匕。此達成方式為利用蒸汽充分處理於草而去活 實例中在:會C太下過 加為10分鐘左右::分鐘,但滞留時間依需求增 微波加執砂烤可熱4_ “去活化酶,例如 烤於ρ在另__具體實例巾 變性 ㈣去活化’然此需採取步驟從於草移除化學0。 處理合已加工終草和已濃縮终草:物。將已 ==:==。藉由把於草萃取 合的;達成重新、〜δ。與已加草重新結 =原卒取物1料於處理萃取物以去除敎成分時損失 的I,且各種菸草不盡相同。 =在與已處理料萃取物重新結合之前、期間或之 灸’利用標準乾燥方法,乾燥已處理終草。已處理於草的 ,始水氣含量通常為約爆·。。在—較佳且體實例中, 用 氣含量為約14%。加熱乾燥機(如簾式乾燥機) Λ 起始水氣含量減為約30%。第二加熱乾燥機 (〇工乳乾煉機)接著用於將水氣含量進-步減為約14%。 2〇l247ii5 隨後將最終乾燥產品加工成成品形式,例如片,其經 而形成整個或部分捲菸濾嘴。然因萃取及處理時移除 =中高達30%的原成分’故成品中料每單位重量剩 時,、,分濃度將比原材料高。這些成分包括纖維素,燃燒 醛和/、會和糖與澱粉產生有害揮發性材料,例如煙中的乙 甲 。 &草代替片 草Θ把於草代替片(TSS)併入菸草摻合物可減少捲菸的菸 甘:進而降低捲菸產生毒物的整體可能性。TSS亦含有 總-,加熱時’TSS的甘油釋出到煙流中而貢獻顆粒狀煙 油,7,此測作無尼古丁乾顆粒物質(NFDPM,亦稱為,,焦 甘由於多數捲菸設計成符合特定NFDPM出量值,故將 的 < =入煙流可有效降低柊草燃燒產物對整體NFDPM值 煙^八此方法稱為”稀釋”。將TSS併入捲菸可減少各種 活料1,包括顆粒和氣相毒物。體外毒物試驗顯示煙顆粒 旦 低程度與其甘油含量呈比例關係。人體接觸尼古丁 里依濾嘴試驗測定減少平均18%,依24小時尿生物標記分 析減少I4%。煙顆粒接觸量依遽嘴試驗減少平均29%,按 尿4-(甲基亞硝胺基)-1 -(3-比啶基)_丨·丁醇濃度計減少近似 量。這些結果顯示,使用於草代替片可減少接觸一些煙毒 物。 根據本發明,吸煙物件製備成包括菸草代替片材料, 其包含不燃無機填料、藻酸鹽黏結劑和氣溶膠產生用具。 有利地,菸草代替片材料包含不燃無機填料、黏結劑 和氣溶膠產生用具做為其主成分,這三種組分較佳共包含 20 ⑤ 201247115 替片材料重量的至少85%’更佳大於90%,又更佳 佔代替片材料重量的約94%或以上。三種組分甚ΐ可 ^草代替片材料的刚%。其餘組分較佳例如為—或更^ 術者所如杨)或香料。其他主要組分㈣為熟諳此技 ^ ° σ。故菸草代替片材料就其成分而論係十分簡單 叩月材。 在此,菸草代替片材料”一詞係指可‘用於吸煙物件的 料。此未必意味著材料本身一定禁得起燃燒。菸草 片材料通常製作成片,然後再㈣。接著摻合料代替片 材料與其他材料,以製造可吸煙填料。 本發明更提供包含可吸煙填料纏繞棒的吸煙物件,可 吸煙填料由摻合物組成,播合物併人包含不燃無機填料、 ,結劑和氣溶膠產生用具的菸草代替片材料,吸煙物件的 氣溶膠傳遞效率比大於4.0。在此,氣溶膠傳遞效率係依照 煙中氣溶膠百分比除以可吸煙填料中氣溶膠百分比測量。 氣溶膠傳遞效率較佳大於5,更佳大於6。 用於本發明吸煙物件的可吸煙填料可包含摻合物,摻 合物由不超過菸草代替片材料重量的75%組成。 無機填料較佳佔60%-90°/〇,更佳多於最終片材的 70%。有利地,無機填料佔最終片材重量的約74%,但含 量也可更高,例如佔最終片材重量的80%、85%或90%。 有利地,不燃填料包含一定比例的材料,其平均粒徑 為500微米(μηι)至75μπι。無機填料的平均粒徑較佳為 400μιη至ΙΟΟμπι,並大於125μπι,較佳大於Ι50μπι。有利 21 201247115 地,平均粒徑為或約17〇μιη,且為17〇μηι至2〇〇μηι。此粒 徑與替代菸草產品習用的食品級無機填料(即粒徑約 2μηι-3μιη)差別很大。各無機填料的粒徑範圍分別為 毫米(1_μηι)。無機填料可經磨碎、财或沈職預定粒 徑。 有利地’無機填料係-或更多珍珠岩、氧化紹、石夕蕩 土、碳酸飼(生石灰)、蛭石、氧化鎮、硫酸鎮、氧化辞、硫 酸辦(石膏)、氧化鐵_、浮石、二氧化鈦、銘_或且他 不溶紹酸鹽、或其他無機填料。材料的密 ” 至5.:克:立方公分(〆)。有利地,無機填料的密度為二 广’較佳小於2.5g/em3,更佳小於2喻^, 。期使用密度小於lg/em3的無機 二 無機填料可降低產品密度,進而改善灰分特性。低讀 徑,㈣宜具小粒 在可吸煙填料中適當播合料祕草代替片預材 =均粒徑。 成品吸煙物件所需的靜態燃燒率。 〆可達到 較佳地’無機針林為結塊 ,,無機填料幾乎不需預=二::了 填料重量的約5%-13%,更佳少於1Q%佳佔最終 有利地,黏結劑佔最終片材重量的約75%或:料。 右黏結劑係g酸鹽與非騎鹽黏結劑的混1物目f利地’ 較佳包含至少50%的藻酸鹽,更佳為至^6(^貝 =結劑 又更佳為至少70%的藻酸鹽。當使用非藻酸鹽黏 22 201247115 可適當減少結合黏結劑量。有利地,黏結劑組合物的藻酸 鹽量隨結合黏結劑量減少而增加。適合的藻酸鹽黏結劑包 括可溶藻酸鹽,例如藻酸銨、藻酸納、藻酸鈉妈、藻酸約 銨、藻酸鉀、藻酸鎂、藻酸三乙醇胺和藻酸丙二酯。諸如 纖維素黏結劑、黏膠或凝膠等其他有機黏結劑也可結合藻 酸鹽黏結劑使用。適合的纖維素黏結劑包括纖維素與纖維 素衍生物,例如羧曱基纖維素鈉、曱基纖維素、羥丙基纖 維素、羥乙基纖維素或纖維素醚。適合的黏膠包括阿拉伯 膠、印度膠、黃蓍膠、刺梧桐膠、刺槐豆膠、亞拉伯膠、 瓜爾膠、榲棹籽膠或三仙膠。適合的凝膠包括洋菜膠、瓊 脂糖、鹿角菜膠、褐藻糖膠、叉紅藻膠。澱粉亦可用作有 機黏結劑。可參考手冊(如’’ /«t/w对Gwms,五.对/er Mcfli/ew/c 挑選其他適合黏膠。黏結劑最好以藻酸 鹽黏結劑為主要部分。本發明基於燃燒後的中和風味而以 藻酸鹽為首選。 氣溶膠產生用具較佳佔5%-20%,更佳少於15%,又更 佳多於7%,再更佳多於10%。氣溶膠產生用具較佳少於 13%。氣溶膠產生用具更佳佔最終片材重量的11%-13%, 有利地為約11.25%或12.5%。適當選擇氣溶膠產生用具 量,以與摻合物中的於草材料量結合,換合物包含吸煙物 件的可吸煙填料。例如,在包含高比例片材與低比例菸草 材料的換合物中,片材内需裝填較少量的氣溶膠產生用 具。或者,在包含低比例片材與高比例菸草材料的摻合物 中,片材内需裝填較大量的氣溶膠產生用具。 23 201247115 夕一,合的氣溶膠產生用具包括氣溶膠形成用具, 甘油:丙,與三乙二醇)、醋(如捧樣酸三乙_ ,二乙s欠甘油酯)、高彿點羥 -曰 或乳酸)。可使用氣溶膠形成用具組合;;(如乙士山梨醇 塑化=:生塑化片材。適合的附加 多孔結構的片材。充氣於片材。鎮模㈣從而形成具 =地,可封裳該或部分氣溶膠 膠囊化或以其他方式穩 衩佳為微 量可能比給定範圍多“下,氣溶膠產生用具 殊香料吸=含讓材料變深的色素及/或賦予特 如包括可可甘Ϊ 當地法規管制,且例 狀、粒狀或均質於草、、巧克力4太妃糖。也可使用粉 El5〇a(焦糖)、Em里^亦核准使用食用色素,例如 色HT)。適入的^'、、色BN)、E153(植物碳)或E155(褐 亦適用。如包括薄荷和香草。其他缚模材料 材料有較深心子,石或其他無機填料可讓終草代替片 0-10。/。,且P °色素較佳伯最終於草代替片材料重量的 替片材料的^ /%·7%°有利地’色素少於最終終草代 好少於4, 少於6%,更佳少於5 %。色素用量最 村料會二於3 %及少於2%。可可錢最終•草代替片 r ΐ的〇-5%,甘草佔〇-4°/°。色素如為可可或甘草時, 二;,定'色的最低可可量為最終終萆代替片特料重量的 u 甘草則為約2%。同樣地,焦糖宜姑最終終草代替 才料重量的〇_5%,較佳少於約2%,更佳為約i 5〇/<^其 ⑤ 24 201247115 他適合色素包括糖蜜、麥芽萃 脂、角豆樹、梅物、咖啡萃取物、茶似樹 合物。于梅子卒取物或於草萃取物。也可使用色素^ #當地法規允許,亦可加入香 料:風味和香味特性。有利地 食用片材 草代替_重量的0.4:用下:用4素可 片後’將色素灑入片材。 Μ 了於製 可加入纖維,例如纖維素纖維 或勤皮纖維’喊供片材 麻) 較高填充值。若加人输紿夕車乂间強度、較低密度或 。一較佳;::二: 中無纖維素或其他纖維材料存在。'、°有利地’片材 合物=替片材料係非菸草含有片。應理解摻 燃燒性不二例如可75%)時’摻合物的 ^ λ , 糟由將)1、至多達5〇/〇-10%的碳粒 料,即片材料而克服。碳較佳不為結塊的含碳材 枓,^不與其他材料混合成團塊來預處理。 殖粗終片。料較佳祕草材料摻合,以提供可吸煙 利i二二的於草材料組分較佳為高品質薄片等級。有 _ ' 料大多為终絲。菸草材料可包含20%-100%經 =階膨脹過程的膨祕草,例如DmT。此材料的填充力通 吊為64立方公分/克(如參見GB 1484536或us 4,34〇,〇73)。 除薄片外,摻合物較佳包含<30%的其他摻合物組分, 其他摻合物組分為切絲梗片(CRS)、水處理梗片(WTS)或蒸 4理梗>1 (STS)或重組於草。其他組分較佳佔最終於草材 25 201247115 料重里的20%以下’更佳少於1〇%,又更佳少於5〇/〇。 a,據本發明的吸煙物件宜包含以氣溶膠產生用具處理 的於草材料。終草材料可用氣溶膠產生用具處理,但並非 所有終草材料與片材摻合物都需如此。 加到於草的氣溶膠產生用具量為菸草重量的2%-6%。 有利地’加工後’菸草材料與片材摻合物中的氣溶膠產生 用具總量為可吸煙材料重量的4^42%,較佳少於1〇%,更 佳多於5%。 高活性碳 用於兩段和三段濾嘴的聚合物衍生高活性碳粒的孔隙 結構不同於市售捲菸常用的碳(其通常衍生自椰殼)。因此, 其對一系列揮發性煙毒物有優越的吸附特性。 如第14圖所示,以適當方法(v〇n Biticher與DeGmbH (German-based polymer-derived materials record the effectiveness of volatiles in smoke poisons, which are usually about twice the current carbon footprint of the commonly used coconut shells. Under 1 = 0 and HCI smoking custom, the use of regular and smaller The polymer bamboos that have been rolled up have performed well. It has also been observed that the high-flow rate smoking conditions remove the polar eye. The charcoal can be incorporated into the nozzle hole or dispersed (spot type) of the smoking article throughout the entire or The filter material of the mouth (such as cellulose acetate). The combination of EC and the EC made by the shaft technology. These two prototypes can reduce the smoker's smoke when smoking. The sheep is not, and compared with the relevant market (g 12 201247115 end and various products reported in the literature. The results of this operation confirmed that the development of flammable RMYP is feasible. 2. Materials and methods 2.1 experimental, contrast and comparison cigarette design, The EC was developed in conjunction with the development of a blending and filtration technique to reduce the specific chemical species of tobacco poisons or their precursors (Table 1). Individual EC grades with low TSNA and metal content were selected for each EC, and experiments were provided for blending. Cigarette design is low toxic Table 1. Technical Techniques for Constructing Experimental Cigarettes (EC) Application Cigarette Components Description Potential Reductions Tobacco Blend (TB) Blends Tobacco Blend Components Selected as Precursors with Small Amounts of Bad Tobacco Components TSNA and Metal Tobacco Substitute Tablet (TSS) Blend Tobacco Replacement Tablets Reduce Tobacco Combustibles and Produce Glycerol-Containing Tobacco Tobacco Tobacco Blends Blends (BT) Blends Protease-treated Ends, Reduce Blends Protein nitrogen and polyphenol nitrogen components: aromatic amine, NAB, NAT, NNK, NNN; phenolamine functionalized resin beads (CR20L) The mouth contains amine functionalized resins HCN, HCHO, acetaldehyde in the filter section And other carbonyl and activated carbon (HAC) filters are included in the filter segment of the polymer-derived spherical carbon beads gas phase component 13 201247115 in the grass blend treatment by the L-grass blend to apply an aqueous extraction step The extract is then followed by a filtration stage to remove excess and soluble peptides. The residue is solidified to remove insoluble proteins. After washing and enzyme deactivation, re-, ,, and soot solids and filtered Aqueous, phenol Aldehydes, aromatic amines, HCN and - subtractive ~ ° & the process will lead to the yield of the same and the same dilute dilute will also be his: the smoke output of the smoke component is reduced 'tobacco material to be extracted can be smoke The strip, in a preferred embodiment, is chopped in the grass; ^, chopped or ground in the grass. It can also be extracted from the grass. 4°_The tobacco material can be mixed with the solvent for extraction by the method described. The ratio of the final grass material may be from 10:! to 5 to 40: 1, more preferably 25.1 m · 1 λ. Preferably, 20. 1 , ., , .1 to 30 . In a particular preferred embodiment, the ratio of the added tobacco material is 27: a wide specific example > the granule can be an organic solution 'but preferably a water soluble - the initial solvent is usually water' However, it may also contain an alcohol, for example = two or it may contain a surfactant. Other solvents may be used depending on the methanol. The specific composition of the drought can be extracted at 15 ° C to 85 ° C, preferably: When extracting, it is best to continue the material, accompanied by two. C goes down for 15 minutes to 2 hours. In the preferred embodiment, the extraction is about 20 minutes. In the column, during the stroke, during the extraction, the grass component is soluble in the final grass material. It includes nicotine, sugar, some proteins and enters the makeup acid, pectin, and more phenols and fragrances. Up to about 55% of the initial tobacco weight may become soluble. Importantly, the pectin in the tobacco fibers remains crosslinked throughout the extraction and treatment process to maintain the fibrous structure of the tobacco. Therefore, calcium can be added to the solvent used to extract the tobacco and any solution used downstream of the treatment procedure. After extraction, the slurry was discharged to collect a liquid filtrate ("mother filtrate"). At the same time, the insoluble tobacco residue is further extracted by countercurrent washing while it is being transported to remove as much soluble component as possible from the tobacco. A new solvent is added to the tobacco and the filtrate is collected (washing mash). The wash filtrate is directed to the incoming grass residue traveling on the conveyor belt upstream to recover the wash filtrate. The wash filtrate can be collected and reused several times for incoming tobacco residues, preferably three, four or even five times. The final wash filtrate collected at the front end of the conveyor belt will be concentrated in the soluble tobacco component which has been removed from the tobacco residue as it passes through the length of the filter. The final wash filtrate is added to the new tobacco to form a tobacco slurry for further recovery for extraction. For example, the final wash filtrate can be added to a tobacco mixing tank where a tobacco slurry is formed prior to extraction. Therefore, the extraction method can be a continuous process which utilizes the recovered washing filtrate to extract new tobacco. The tobacco is extracted with a new solvent only at the beginning of the extraction. Once the extraction is started, there is no new solvent for extraction and the solvent consists only of the recovered wash filtrate. When the extraction is continued, the extract in the soluble tobacco component becomes more concentrated. These ingredients include those who enter the solution in the extraction tank during the main extraction (forming the parent filtrate) and those who enter the solution on the horizontal belt filter during the secondary extraction (formation of the wash filtrate). Therefore, the final filtration and liquid contain the mother filtrate and the washing filter and liquid. Thus, the tobacco residue produced after the care will be free of these components soluble in the solvent for extraction. At 15 4 4201247115 f, the filter has been extracted and the extracted tobacco has been extracted to remove the liquid from the machine. The final sputum is processed from the level (hereinafter referred to as the undesirable component of the grass product. The bad component ^ strokes \ remove the final « A ^ * ν X into a knife including protein, multi-peptide, amino acid, (four), sister H ya and _ compounds. However, the ingredients required to contain 1 (such as sugar and nicotine) are still unaffected, so the flavor and smoking properties of the extracted grass are comparable to the raw materials. In the preferred embodiment, the end of the treatment Grass extract to remove protein, polypeptides and/or amino acids. Use of insoluble adsorbents such as hydroxyapatite or bleaching earth ore (eg bentonite or bentonite) to remove up to 60% of the original tobacco material % protein. Tobacco extract is preferably treated with bentonite to remove the multi-peptide from the extract. The amount of bentonite added to the extract may be from 2% to 4% of the weight of the tobacco to be extracted. Alternatively, the tobacco extract may be It is sent to the tank containing the bentonite slurry in water. Suitable for the slurry containing about 7 kg (kg) of bentonite in about 64 kg of water (in an hourly amount), for example, 7.13 kg of bentonite is prepared in about 64.18 kg of water. (hourly amount). In any case, the bentonite concentration should be high enough to The quality is reduced to the protein content of the grass extract, but it should not be too high to avoid extra D and nicotine. The bentonite treatment can also effectively remove the pigmented characters contained in the tobacco extract. If it is not removed, the extract is concentrated. It is easy to turn black. The use of sufficient soil to treat the extract can reduce the amount of pigment compounds and make the appearance of the product not too dark. After the bentonite is smashed, the tobacco extract from the slurry is purified by centrifugation and/or filtration. The tobacco extract may or may be treated to remove the desired one. 0 5 16 201247115 Polyvinylpolypyrrolidone (PVPP) is an insoluble adsorbent for polyphenols, which is traditionally used in the brewing industry to remove more beer. Phenol. The amount of PVPP added to the extract 2 can be 5% - 10 ° / / of the weight of the grass to be extracted initially. The amount of pypp can remove 50 ° / 〇 - 90 〇 / 〇 polyphenol in the solution. The optimum pH for removal of polyphenols by Tobacco Extraction II is about 3. Therefore, adding an appropriate acid (such as gas-gas acid) to reduce the extract can improve the PVPP adsorption efficiency. The alternative method of PVPP adsorption of polyphenols is one or more. Multi-enzyme added to tobacco extract to reduce polyphenols A suitable enzyme is laccase (lacquer oxidase). However, the invention is not limited to the method of removing only protein and/or polyh phenol from tobacco. Alternative or additional enzymes, agents or adsorbents can be used to remove tobacco extracts. Among them, his bad tobacco constituents. Other examples of bad tobacco that can be removed from the extract include nitrates, amines and nitrosamines. If you want to remove multiple components from the tobacco extract, you can connect them in series. :: trough; "different enzymes and agents that should be removed from the bad ingredients: sucking single - cattle 1 'early-tank may contain a plurality of enzymes, agents or adsorbents, and containing - in addition to bad components. For example, bentonite Or the pvpp container can be coated with a protein, an enzyme, or an adsorbent, so that not only J or benzene in the tobacco is removed, but also one or more other undesirable components are removed. After the concentrated extract is removed to remove the selected undesirable components, the extract is preferably at a solid concentration of up to 50% by weight. The use of reverse osmosis can effectively reduce the concentration of solids. Xiangshui Laifa 11, can be further concentrated. Follow the solid. Other concentrated concentrations known to those skilled in the art may be used to reintegrate the concentrated tobacco extract and the extracted tobacco. It is best to extract the valerian extracted from the anti-gluten solution to remove one or more of the stalks before it is recombined. Special selection can be used to remove the selected components of the enzyme for further extraction. In a preferred embodiment, the enzyme is a proteolytic enzyme for removing proteins from tobacco. The enzyme is preferably a bacterial or fungal enzyme, more preferably an enzyme for the food and detergent industry on the market. The enzyme can be selected from the group consisting of SaVinaseTM, Neutl>aseTN/, EnzobakeTM and AlcalaseTM, all available from Novozymes A/S. The amount of proteolytic enzyme added to the grass is preferably 0.1 of the weight of the tobacco material. /. To 5%. For example, the amount of SavinaseTM added to the tobacco can be about 1% by weight. The tobacco can be re-stirred in the selected enzyme solution. The ratio of water to grass in the slurry may be from 10:1 to 50 by weight: preferably from 20: i to 4: 1, more preferably from 25 to 1 to 30. In a particular preferred embodiment, the water to tobacco ratio is 27:1 by weight. The pH of the grass/enzyme mixture should promote optimal enzyme activity. Therefore, it is convenient to feed the final dehydrated felt into a tank which is adjusted in pH by adding a base such as sodium hydroxide. The pH-adjusted tobacco is then fed to the enzyme tank for reaction with the selected enzyme. The grass/enzyme mixture is then passed to a plug flow reactor where enzymatic extraction is carried out. Enzymatic extraction should be carried out at a temperature that promotes optimal enzyme activity. It is best to use a narrow temperature range (such as 30. (: -40. 〇, to avoid enzyme denaturation. When SavinaseTM is selected, the best working condition is 57〇c, pH is 9_u. Enzyme extraction should be carried out for at least '乜 minutes; Shorter time will not be enough for proteolytic enzymes to degrade tobacco protein. If multiple components in the final grass are to be removed, multiple enzyme extractions can be performed. They can be carried out in series' or multiple enzymes can be added in a single-treatment step. In the grass. It can also be introduced into the earliest extraction step of the treatment process, and the enzyme is introduced from the extraction step. The follow-up points of the county are 201247115 Residual: = ί wash = volume: (preferably sodium chloride solution) washing is not soluble in grass 1 Salt flushing can be carried out in a continuous countercurrent manner. f. Flushing with water may not be sufficient to remove all enzymes from the material. Grass also 'remains in tobacco after any salt and water rinse: ΓΓ匕. This is achieved by using steam Fully deal with the grass and deactivate the example in: C will be too much for about 10 minutes:: minutes, but the retention time according to the demand increase microwave plus sand roasting can be hot 4_ "deactivate the enzyme, for example, roast in ρ in another __Specific example towel denaturation (four) deactivation This requires steps to remove the chemical 0 from the grass. The treated processed grass and the concentrated grass: will have ==:==. By extracting from the grass; achieving re-, ~δ. Added grass re-catch = original stroke 1 I lost in the treatment of extracts to remove the bismuth component, and the various tobaccos are not the same. = before, during or after re-combination with the treated extract The standard drying method is to dry the treated grass. The water content of the treated grass is usually about blast. In the preferred embodiment, the gas content is about 14%. The heating dryer (such as curtain) Dryer) 起始 The initial moisture content is reduced to approximately 30%. The second heating dryer (completed dry dryer) is then used to reduce the moisture content to approximately 14%. 2〇l247ii5 The final dried product is processed into a finished product form, such as a sheet, which forms a whole or a part of the cigarette filter. However, since the extraction and treatment removes up to 30% of the original component, the finished product is left per unit weight, , the concentration will be higher than the raw materials. These ingredients include cellulose, burning aldehydes and /, and sugar and The powder produces harmful volatile materials, such as acetaminophen in tobacco. & Grass instead of stalks. The incorporation of grass substitute tablets (TSS) into tobacco blends reduces the smoke of cigarettes: thereby reducing the overall likelihood of cigarette poisoning. Sex. TSS also contains total -, when heated, 'TSS glycerol is released into the plume and contributes to granular smoky oil, 7. This is measured as no nicotine dry particulate matter (NFDPM, also known as, Jiao Gan due to most cigarettes) Designed to meet specific NFDPM output values, so the <=inflow can effectively reduce the sorghum combustion products to the overall NFDPM value. This method is called “dilution.” Incorporating TSS into cigarettes can reduce various materials. 1, including particles and gas phase poisons. The in vitro toxicity test showed that the low degree of smoke particles was proportional to its glycerol content. The human exposure to nicotine lining filter assay reduced the average by 18% and decreased by 14% based on 24-hour urine biomarker analysis. The amount of smoke particles contacted was reduced by an average of 29% according to the mouth test, and the approximate amount was reduced by the concentration of 4-(methylnitrosamino)-1 -(3-pyridyl)-indolyl butanol. These results show that the use of grass instead of tablets can reduce exposure to some tobacco poisons. According to the present invention, a smoking article is prepared to include a tobacco substitute sheet material comprising a non-combustible inorganic filler, an alginate binder, and an aerosol generating implement. Advantageously, the tobacco substitute sheet material comprises a non-combustible inorganic filler, a binder and an aerosol generating device as its main component, and the three components preferably comprise a total of 20 5 201247115 at least 85% by weight of the sheet material, more preferably greater than 90%. More preferably, it is about 94% or more by weight of the substitute sheet material. The three components can be used to replace the % of the sheet material. The remaining components are preferably, for example, - or the like, or the like. The other major component (four) is familiar with this technique ^ ° σ. Therefore, tobacco substitute sheet material is very simple in terms of its composition. Here, the term "tobacco instead of sheet material" refers to a material that can be used for smoking articles. This does not necessarily mean that the material itself must be prohibited from burning. The tobacco sheet material is usually made into a sheet and then (4). Then the admixture is substituted for the sheet material. And other materials to make a smokable filler. The present invention further provides a smoking article comprising a smokable filler wrap, the smokable filler is composed of a blend, the smelt comprises a non-combustible inorganic filler, a binder and an aerosol generating device The tobacco replaces the sheet material, and the aerosol transfer efficiency ratio of the smoking article is greater than 4.0. Here, the aerosol transfer efficiency is measured by dividing the aerosol percentage in the smoke by the percentage of aerosol in the smokeable filler. The aerosol transfer efficiency is preferably greater than 5 More preferably greater than 6. The smoking filler for use in the smoking article of the present invention may comprise a blend comprising no more than 75% by weight of the tobacco substitute sheet material. The inorganic filler preferably comprises from 60% to 90°/〇. More preferably more than 70% of the final sheet. Advantageously, the inorganic filler comprises about 74% by weight of the final sheet, but may also be higher in content, for example, the weight of the final sheet. 80%, 85% or 90%. Advantageously, the non-combustible filler comprises a proportion of material having an average particle size of from 500 micrometers (μηι) to 75 μπι. The average particle size of the inorganic filler is preferably from 400 μm to ΙΟΟμπι and greater than 125 μm. Preferably, it is greater than Ι50μπι. Advantageously 21 201247115, the average particle size is or about 17〇μηη, and is 17〇μηι to 2〇〇μηι. This particle size is equivalent to the food grade inorganic filler used in the alternative tobacco product (ie, the particle size is about 2μηι-3μιη) varies greatly. The particle size range of each inorganic filler is mm (1_μηι). The inorganic filler can be ground, grained or settled to a predetermined particle size. Advantageously 'inorganic filler system - or more perlite, Oxidation Shao, Shixi Dangtu, carbonated feed (lime), vermiculite, oxidation town, sulfuric acid town, oxidation, sulfuric acid (gypsum), iron oxide _, pumice, titanium dioxide, Ming _ or he does not dissolve the acid salt, Or other inorganic fillers. The density of the material is up to 5.: gram: cubic centimeter (〆). Advantageously, the inorganic filler has a density of two', preferably less than 2.5 g/cm3, more preferably less than two. Inorganic two inorganic fillers with a density of less than lg/em3 can reduce the product density and improve the ash characteristics. Low reading diameter, (4) Suitable for small particles In the smoking filler, the appropriate sowing material is used instead of the sheet material = average particle size. The static burning rate required for finished smoking articles. 〆 can achieve better 'inorganic needle forest for agglomeration, inorganic filler almost no need to pre-= two:: about 5%-13% of the weight of the filler, better than less than 1Q% of the final advantage, the binder About 75% of the weight of the final sheet or material. The right binder is a mixture of a g-acid salt and a non-ride salt binder. Preferably, it comprises at least 50% of an alginate, more preferably a ^6 (^bey = a better and at least a binder) 70% alginate. When using non-alginate adhesive 22 201247115, the combined bonding dose can be appropriately reduced. Advantageously, the amount of alginate in the binder composition increases with the reduction of the bonding amount. Suitable alginate binder Including soluble alginate, such as ammonium alginate, sodium alginate, sodium alginate, ammonium perlamate, potassium alginate, magnesium alginate, triethanolamine alginate and propylene glycol alginate. Such as cellulose binder Other organic binders such as viscose or gel can also be used in combination with alginate binders. Suitable cellulose binders include cellulose and cellulose derivatives such as sodium carboxymethyl cellulose, sulfhydryl cellulose, and hydroxy Propyl cellulose, hydroxyethyl cellulose or cellulose ether. Suitable adhesives include gum arabic, gum, gum tragacanth, karaya gum, locust bean gum, arabe gum, guar gum, coriander seeds Gum or Sanxian gum. Suitable gels include acacia, agarose, carrageenan, fucose Fork red algae. Starch can also be used as an organic binder. Refer to the manual (eg '' / «t / w for Gwms, five. / / er Mcfli / ew / c choose other suitable adhesive. Best bonding agent The alginate binder is mainly used. The present invention is based on the neutralized flavor after combustion, and the alginate is preferred. The aerosol generating device preferably accounts for 5%-20%, more preferably less than 15%, and more preferably. More than 7%, more preferably more than 10%. The aerosol generating device is preferably less than 13%. The aerosol generating device preferably accounts for 11%-13% by weight of the final sheet, advantageously about 11.25% or 12.5. %. The amount of aerosol generating utensil is appropriately selected to combine with the amount of grass material in the blend, and the blend contains a smoking filler of the smoking article. For example, in the case of including a high proportion of sheet material and a low proportion of tobacco material. In the case, a smaller amount of aerosol generating means is required to be filled in the sheet. Alternatively, in a blend comprising a low proportion of sheet material and a high proportion of tobacco material, a larger amount of aerosol generating means is required in the sheet. 23 201247115 A combined aerosol generating device comprising an aerosol forming device, glycerin: C, and three Glycol), vinegar (e.g., acid holding comp _ triacetate, glyceryl diacetate s less), the high point of Buddha hydroxyalkyl - or said lactic acid). An aerosol-forming tool combination can be used; (eg, sorbitol plasticization =: plasticized sheet. A suitable sheet of additional porous structure. Inflated in sheet. Town mold (4) to form a ground, can be sealed Capsules or partial aerosols may be encapsulated or otherwise stabilized as a trace amount may be more than a given range "under, aerosol-generating utensils, flavors, pigments, and/or imparting pigments such as cocoa Ϊ Local regulations, and examples, granular or homogeneous in grass, chocolate 4 toffee. You can also use the powder El5〇a (caramel), Em Li also approved the use of food coloring, such as color HT). Into the ^', color BN), E153 (plant carbon) or E155 (brown is also applicable. For example, including mint and vanilla. Other bonding materials have deep core, stone or other inorganic fillers can make the grass replace the tablet 0 -10. /., and the P ° pigment is preferably at the end of the grass instead of the weight of the sheet material of ^ /% · 7% ° advantageously 'pigment less than the final end of the grass is better than 4, less than 6 %, preferably less than 5%. The amount of pigment used in the village will be 2% and less than 2%. Cocoa money • Grass instead of tablets r ΐ 5% -5%, licorice 〇 -4 ° / °. When the pigment is cocoa or licorice, the second; the minimum cocoa amount of the final color is the final 萆 萆 萆 片 萆 萆 萆 u u u u 2%. Similarly, caramel is the final grass to replace the weight of 才 5%, preferably less than about 2%, more preferably about 5 〇 / lt; ^ its 5 24 201247115 Molasses, malt extract, carob, plum, coffee extract, tea-like sap. In the plum or the grass extract. You can also use the pigment ^ #Local regulations allow, you can also add spices: Flavor and aroma characteristics. It is advantageous to eat the grass instead of 0.4 weight: use: use 4 tablets to pour the pigment into the sheet. Μ can be added to the fiber, such as cellulose fiber or fiber 'Call for sheet hemp.' Higher filling value. If you add people to the strength of the car, the lower density or lower density. One is better;:: Two: no cellulose or other fiber materials exist. ', ° favorable The 'sheet compound=the sheet material is a non-tobacco-containing sheet. It should be understood that the blending flammability is not as good as, for example, 75%), the blend of the compound λ, the bad will be 1 Up to 5〇/〇-10% of carbon pellets, that is, the sheet material is overcome. The carbon is preferably not agglomerated carbonaceous material, and is not mixed with other materials to form agglomerates for pretreatment. Preferably, the material of the grass material is blended to provide a high quality sheet grade of the grass material component which can be smoked. The material is mostly the final yarn. The tobacco material may comprise 20%-100. The swelling grass of the % expansion process, such as DmT. The filling force of this material is 64 cubic centimeters per gram (see GB 1484536 or us 4, 34 〇, 〇 73). Preferably, <30% of other blend components are included, the other blend components are cut stem pieces (CRS), water treated stem pieces (WTS) or steamed stems > 1 (STS) or reconstituted In the grass. The other components preferably account for less than 20% of the final weight of the grass 25 201247115, preferably less than 1%, and more preferably less than 5〇/〇. a. The smoking article according to the present invention preferably comprises a grass material treated with an aerosol generating device. The final grass material can be treated with an aerosol generating device, but not all of the final grass material and sheet blends. The amount of aerosol-generating equipment added to the grass is from 2% to 6% by weight of the tobacco. Advantageously, the total amount of aerosol generating material in the 'processed' tobacco material and sheet blend is 4^42%, preferably less than 1%, more preferably more than 5% by weight of the smokable material. Highly activated carbon The pore structure of the polymer-derived high activity carbon particles used in the two- and three-stage filters differs from the carbon commonly used in commercial cigarettes (which are usually derived from coconut shells). Therefore, it has superior adsorption characteristics for a range of volatile smoke poisons. As shown in Figure 14, in an appropriate way (v〇n Biticher and De

Ruiter ’ 2004,Von Bliicher 等人,2006 ; Behringer 與Ruiter' 2004, Von Bliicher et al., 2006; Behringer and

Fichtner,2008)製備球粒狀聚合物衍生碳。利用批次方法與 間接加熱旋轉爐’在減壓、惰性大氣中,製造聚合物衍生 活性碳。製備球形聚合物原料後,利用過量發煙硫酸,熱 穩定材料。隨後,緩慢加熱材料達500°C,以釋出主要的二 氧化硫(S02)和水(H2〇)及碳化聚合物。所得碳的初始孔隙系 統無法供典型吸附。為製造能供吸附的多孔系統,進一步 加熱材料達900°C至1000°C,以利用氧化劑(蒸汽)活化。 此將建立主要由孔徑0.7至3奈米(nm)的微孔組成的孔隙系 統。隨後以二氧化碳(C〇2)活化而形成主要為3至80nm的 較大中孔。結合蒸汽和C〇2活化步驟為製造預定孔隙特性 提供了靈活策略。 ⑧ 26 201247115 鈐廓Γ 為口成材料,且具有更緊密分明的球形 均勻的粒徑。聚合物衍生材料有較低密度和較少 ;二含量’此反映聚合物原料相較於天然椰殼做為碳化過 私的起始材料的合成本質。 絲發現在·定制下,聚合物衍生碳比活化椰殼更能 有^^數煙成分,其辦除甲盤、乙酸、氰化氫(HCN) Γ本(減少5G%·)外的煙成分減少_福。在Ηα 二件下,具習用椰碳的捲終對除甲㈣购外的多數煙成分 口 乂 25%-45%。包括聚合物衍生碳的捲菸對除乙醛和 HCN(15%_3〇%)外的多數煙成分出量減少6〇% 9〇%。 胺官能化樹脂珠粒 mAI0_ CR20係市售胺官能化樹月旨雜,其可用於 本發明(由三菱化學公司製造)。其具❹胺基做為螯合配位 體以接合至㊉度交聯的多孔聚苯乙烯基質上。CR2G顯示對 過渡金屬離子有強親和力。無法精確控制官能化而得的確 切胺基類型,樹脂上可能存在數種不同類型。 茲發現商業級CR20(以下稱為CR2〇c)併入捲菸時,其 特徵氣味與習用消費者可接受捲菸煙特性不相容。然三菱 修改合成條件後可大幅降低此氣味強度而獲得,,低味,,等級 CR20(以下稱為CR20L)。在此作業下,除非另外註明,否 則所有產物稱為CR20L。此材料的粒徑為600毫米(mm), 密度為0.64g/cm3 ’水含量為15重量%,總體交換能力為 0-92meq/cm3。 27 201247115 其他各種類型的CR20係由三菱化學公司製造,包括 CR20D和CR20HD。在此以’’CR20”一詞涵蓋所有不同類型 或等級的離子交換樹脂。 將一些CR20珠粒備於水中,使之適合捲菸濾嘴應用, 其可能需移除至少一些水。在一具體實例中,移除水及乾 燥材料,使其具約15%或以下的水氣。在替代具體實例中, 吸煙物件的濾嘴可接受較高水氣含量。 CR20(包括特定CR20L)可併入捲於濾嘴。相較於含習 用碳的遽嘴’ CR20L能有效減少HCN、曱搭和乙酿。然在 去除煙流的其他揮發性成分方面,碳比CR20L有效。 實驗捲菸 以1至6毫克(mg)的ISO NFDPM(焦油)出量為目標, 利用這些技術建構捲菸。 亦製造三種科學對照捲菸,以評估過濾技術對減少EC 的煙成分的貢獻。尚使用兩種市售比較捲菸(Img ISO設計 和6mg ISO設計)進行試驗。比較市售品牌係因實際對照捲 菸需評估不同煙成分減少技術共同造就一致的消費者可接 受捲菸設計。又,使用市售捲菸能檢驗現實捲菸、而非科 學對照捲菸的成分實際減少程度。最後,使用市售參考產 品可就現實使用時的感官可接受度和人體接觸量做出相關 比較。 在lmg與6mg(IS0)方面,市售比較產品有類似來自德 國於2007-8的市場領導品牌的機器吸煙成分出量。為取得 品牌和捲於設計的完整資訊及允許遮蔽產品來進行人體感 ⑤ 28 201247115 f和接觸量評估,乃選用英美菸草(BAT)類比較捲菸、而非 貫際市場領導品牌。故特別針對這些試驗製造二市售捲菸 樣品,且不標示品牌或其他標諸,以辅助人吸煙試驗。 2.2實驗、比較和對照捲菸的規格 EC設計採用共同特徵:全部建構成捲菸長度 84mm(57mm的菸草棒加上27mm的濾嘴)、圓周24.6mm的 相同基本尺寸,且濾嘴皆以經檸檬酸三乙酯塑化的乙酸纖 維素(CA)纖維為基料。鑑定具低TSNA與金屬含量的菸草 等級及結合做為菸草摻合物原型。製備三種不同實驗捲 私,並於表2(第1圖)總結三種EC的設計特徵及比較對照 捲柊和市售比較捲於如下。 實驗捲菸BT1結合含有BT處理菸草(75.4%的已處理維 吉尼亞種菸草、4.3%的東方種菸草和20.3%的未處理維吉尼 亞種菸草)的維吉尼亞型菸草摻合物與含有CR2〇段(以減少 曱醛、乙醛和HCN出量)與含聚合物衍生高活性碳濾嘴段(以 減少異戊二烯和其他揮發性毒物的濾嘴。此捲於在IS〇機器 吸煙條件下的目標NFDPM出量為lmg。實驗捲於TSS1亦 設計成在ISO機器吸煙條件下的NFDpm出量為lmg,且以 含有TSS(維吉尼亞種、白肋種與東方種菸草摻合物)的us 型摻合物為基料,其包括約20%的TSS和與實驗捲菸BT1 一樣的濾嘴。實驗捲菸TSS6亦使用20%、不同US型摻合 物的TSS,且設計成在ISO機器吸煙條件下的NFDPM出量 為6mg。不同濾嘴構造搭配此捲菸使用:兩段濾嘴在菸草棒 旁有80mg的高活性碳散佈於ca纖維且口端具CA段。 29 201247115 市售比較捲菸CC1含有us型摻合菸草,包括一些馬 里蘭種於草。市售比較捲終CC6亦為典型的US型摻合捲 於,但摻合物不同於CC1。表2(第1圖)總結三種EC的設 計特徵及比較對照捲菸和市售比較捲菸。兩種市售比較捲 菸使用單段乙酸纖維素濾嘴。三種”科學對照,,(SC)捲菸構造 和相關實驗捲菸BT1、TSS1與TSS6 —樣,除了各對照捲 柊所用濾嘴係單段27mm的CA濾嘴且無附加過濾吸附介 質。 表2顯示BT1和CC1的捲菸構造十分相似,且具相當 匹配的濾嘴通風性和紙滲透性。菸草密度和濾嘴壓降(抽取 抗力或流過濾嘴的阻力)略微不同,就兩種參數而言,Βτι 高於ccn。tssi和cci的捲菸構造也很類似。tssi的遽 嘴壓降高於市售對照組,但菸草密度和濾嘴壓降均大於 CC1。TSS6和CC6使用比img(iS0)產品還少的濾嘴通風 孔。比較兩種6mg(ISO)產品發現,TSS6的菸草密度、壓降 值略大,而遽嘴通風性略低。 2.3煙化學分析 進行煙化學分析前,根據IS0 34〇2(1999)規範,調理捲 菸。根據ISO 4387(2000)規定的吸煙條件(即每60秒取得持 續2秒的35毫升煙團,縮寫成35/2/60)和IS〇 33〇8(2〇〇〇)(為 NFDPM與尼古丁分析制定),進行例行性化學分析。 約150種煙成分被視為毒物,一些權責機關已要求其 中一個子集(約40種)的出量資料《茲提出一些毒物的出量 限制(Burns 等人(2008)發表的文獻”Mandated i〇wering 〇f 201247115 toxicants in cigarette smoke: a description of the World Health Organization TobReg proposal; Tob. Control 17, 132-141”)和其生物監測方式(Hecht,S.S.等人(2010)發表的 文獻’’Applying tobacco carcinogen and toxicant biomarkers in product regulation and cancer prevention; Chem. Res. Toxicol. 23, 1001-1008”)。基於這些原因及為更精確描繪EC 特徵,將測量更多種煙成分(47個分析物)的MS出量。此 作業未檢驗的其他約100種毒物因缺乏驗證分析方法而不 測量。透過直接測量及做為多環芳香烴(PAH)系列的一部 分,可取得苯并芘出量值兩次。 測量其他分析物需稍微修改ISO吸煙參數,現行方法 可取自 英美於草公司 (British AmericanFichtner, 2008) Preparation of spherulitic polymer-derived carbon. Polymer-derived activated carbon is produced by a batch process and an indirect heating rotary furnace in a reduced pressure, inert atmosphere. After preparing the spherical polymer raw material, the material is thermally stabilized by using excess fuming sulfuric acid. Subsequently, the material was slowly heated to 500 ° C to release the main sulfur dioxide (S02) and water (H2 〇) and the carbonized polymer. The initial pore system of the resulting carbon is not available for typical adsorption. To produce a porous system capable of being adsorbed, the material is further heated to a temperature of from 900 ° C to 1000 ° C to be activated by an oxidizing agent (steam). This will establish a pore system consisting mainly of micropores with a pore size of 0.7 to 3 nanometers (nm). This is followed by activation with carbon dioxide (C〇2) to form a larger mesopores of predominantly 3 to 80 nm. The combined steam and C〇2 activation steps provide a flexible strategy for manufacturing predetermined pore characteristics. 8 26 201247115 钤 Γ is a material of the mouth and has a more distinct spherical uniform particle size. Polymer-derived materials have lower density and less; two levels' reflect the synthetic nature of the polymer starting material as a starting material for carbonization over natural coconut shells. It has been found that, under custom design, polymer-derived carbon has more smoke components than activated coconut shells, and it can remove smoke components other than A-plate, acetic acid, and hydrogen cyanide (HCN) sputum (reduced by 5G%). Reduce _ blessing. Under the two pieces of Ηα, the volume of the coconut fiber used in the end is 25%-45% for most cigarettes except for the purchase of A (4). Cigarettes including polymer-derived carbon reduced the yield of most smoke components except acetaldehyde and HCN (15% _3〇%) by 6〇% and 9〇%. Amine-functionalized resin beads mAI0_CR20 is a commercially available amine functionalized tree, which can be used in the present invention (manufactured by Mitsubishi Chemical Corporation). It has a guanamine group as a chelating ligand for bonding to a ten degree crosslinked porous polystyrene substrate. CR2G shows a strong affinity for transition metal ions. There is no precise control over the type of amino acid that can be functionalized. There may be several different types of resins. It has been found that when commercial grade CR20 (hereinafter referred to as CR2〇c) is incorporated into a cigarette, its characteristic odor is incompatible with the consumer acceptable cigarette characteristics. However, Mitsubishi can greatly reduce the odor intensity after modifying the synthesis conditions, and the low taste, grade CR20 (hereinafter referred to as CR20L). Under this work, all products are referred to as CR20L unless otherwise noted. This material has a particle diameter of 600 mm (mm), a density of 0.64 g/cm3' water content of 15% by weight, and an overall exchange capacity of 0-92 meq/cm3. 27 201247115 Other various types of CR20 are manufactured by Mitsubishi Chemical Corporation, including CR20D and CR20HD. The term ''CR20' is used here to cover all different types or grades of ion exchange resins. Some CR20 beads are prepared in water to make them suitable for cigarette filter applications, which may require removal of at least some water. The water and the dried material are removed to have a moisture content of about 15% or less. In an alternative embodiment, the filter of the smoking article can accept a higher moisture content. CR20 (including a specific CR20L) can be incorporated into the volume. In the filter, the CR20L can effectively reduce HCN, 曱 和 and 乙 。 compared with the carbon containing the conventional carbon. However, in the removal of other volatile components of the smoke, the carbon is more effective than CR20L. The experimental cigarette is 1 to 6 mg. (mg) ISO NFDPM (tar) output is the target, using these techniques to construct cigarettes. Three scientific control cigarettes were also made to evaluate the contribution of filtration technology to reducing EC smoke constituents. Two commercially available comparative cigarettes (Img) are still used. ISO design and 6mg ISO design) were tested. Comparing commercially available brands is based on the actual comparison of cigarettes to evaluate different smoke composition reduction technologies to create a consistent consumer acceptable cigarette design. Also, use commercially available cigarettes. To test the actual reduction of the composition of actual cigarettes, not scientifically controlled cigarettes. Finally, a commercially available reference product can be used to make a comparison between sensory acceptability and human exposure in actual use. In terms of lmg and 6mg (IS0), Commercially available comparison products have similar machine smoking constituents from the market leading brands of Germany in 2007-8. In order to obtain complete information on the brand and the design of the roll and allow the masking of the product to carry out the human sense 5 28 201247115 f and exposure assessment, British American Tobacco (BAT) is used to compare cigarettes rather than the leading brands in the market. Therefore, two commercially available cigarette samples are specially made for these tests, and no brand or other labels are listed to assist people in smoking tests. 2.2 Experiments, comparisons The EC design of the specifications of the control cigarettes adopts the common features: all of them are constructed with a cigarette length of 84 mm (57 mm tobacco rod plus 27 mm filter), the same basic size of 24.6 mm circumference, and the filters are all molded with triethyl citrate. The cellulose acetate (CA) fiber is used as a base material. The tobacco grade with low TSNA and metal content is identified and combined as a tobacco blend prototype. Three different experimental volumes were prepared, and the design characteristics of the three ECs were compared in Table 2 (Fig. 1). The comparison control volume and the commercially available comparison volume are as follows. Experimental cigarette BT1 combined with BT treated tobacco (75.4% processed dimension) Virginia-type tobacco blend with Gentian tobacco, 4.3% oriental tobacco and 20.3% untreated Virginia tobacco) and containing CR2 mash (to reduce furfural, acetaldehyde and HCN) Output) and filter containing polymer-derived high-activity carbon filter segments (to reduce isoprene and other volatile poisons. This volume is 1 mg of target NFDPM under IS〇 machine smoking conditions. The TSS1 is also designed to produce 1 mg of NFDpm under ISO machine smoking conditions and is based on a us-type blend containing TSS (Virginia, burley and oriental tobacco blend). It includes about 20% TSS and the same filter as the experimental cigarette BT1. The experimental cigarette TSS6 also used TSS of 20% different US type blends and was designed to produce 6 mg of NFDPM under ISO machine smoking conditions. Different filter configurations are used with this cigarette: the two-stage filter has 80 mg of high-activity carbon next to the tobacco rod spread over the ca fiber and has a CA segment at the mouth. 29 201247115 Commercially available comparative cigarette CC1 contains us-type blended tobacco, including some Malayan species in grass. Commercially available comparative final CC6 is also a typical US type blended roll, but the blend is different from CC1. Table 2 (Figure 1) summarizes the design characteristics of the three ECs and compares the control cigarettes with the commercially available comparative cigarettes. Two commercially available comparative cigarettes use a single-stage cellulose acetate filter. Three "scientific controls," (SC) cigarette construction and related experimental cigarettes BT1, TSS1 and TSS6, except that the filter used in each control coil was a single 27 mm CA filter with no additional filter adsorption media. Table 2 shows BT1 It is very similar to the cigarette structure of CC1 and has a fairly matched filter venting and paper permeability. The tobacco density and filter pressure drop (extraction resistance or resistance of the flow filter) are slightly different. For both parameters, Βτι is higher than The cigarette structure of ccn.tssi and cci is also very similar. The pressure drop of tssi is higher than that of the commercially available control group, but the tobacco density and filter pressure drop are both greater than CC1. TSS6 and CC6 use less than img(iS0) products. Filter vents. Comparing the two 6mg (ISO) products, TSS6 has a slightly higher tobacco density and pressure drop, while the mouthpiece has a slightly lower ventilation. 2.3 Tobacco chemical analysis Before the chemical analysis of smoke, according to IS0 34〇2 ( 1999) Specification, conditioning of cigarettes. Smoking conditions according to ISO 4387 (2000) (ie 35 ml of cigarettes lasting 2 seconds per 60 seconds, abbreviated to 35/2/60) and IS〇33〇8 (2〇〇 〇) (developed for NFDPM and nicotine analysis) for routine chemistry Analysis: About 150 kinds of smoke components are regarded as poisons, and some authorities have requested the output of one of the subsets (about 40 species). "There are some restrictions on the yield of poisons (published by Burns et al. (2008). "Mandated i〇wering 〇f 201247115 toxicants in cigarette smoke: a description of the World Health Organization TobReg proposal; Tob. Control 17, 132-141") and its biological monitoring methods (Hecht, SS et al. (2010) published literature ''Applying tobacco carcinogen and toxicant biomarkers in product regulation and cancer prevention; Chem. Res. Toxicol. 23, 1001-1008"). For these reasons and to more accurately depict EC features, the MS yield of more species of smoke (47 analytes) will be measured. The other 100 toxicants not tested in this assignment were not measured due to lack of validated analytical methods. By direct measurement and as part of the Polycyclic Aromatic Hydrocarbons (PAH) series, benzopyrene yields can be obtained twice. Measurement of other analytes requires minor modifications to ISO smoking parameters. Current methods are available from British American (British American)

Tobacco)(www.batscience.com/groupms/sites/BAT_7AWFH3 .nsf/vwPagesWebLive/D07AXLPY?opendocument&SKN=l) 。測量出自吸煙機的煙成分出量無法模擬人吸煙出量,故 擬在各種不同吸煙機設定下測試所有RTP,以在各種可能 吸煙條件下評估機器產率性能。這些已修改吸煙條件列於 表3。 表3吸煙機參數 吸煙說明 縮寫 煙團容積 煙團持續 煙團間隔 濾嘴通風孔 (毫升) 時間(秒) 時間(秒) 阻塞(%) ISO ISO 35 2 60 0 3308/4387 31 201247115Tobacco) (www.batscience.com/groupms/sites/BAT_7AWFH3 .nsf/vwPagesWebLive/D07AXLPY?opendocument&SKN=l) . Measuring the amount of smoke from a smoking machine does not mimic the amount of smoking, so it is intended to test all RTPs at various smoking machine settings to assess machine yield performance under a variety of possible smoking conditions. These modified smoking conditions are listed in Table 3. Table 3 Smoking machine parameters Smoking instructions Abbreviation Tobacco volume Tobacco continuous Tobacco interval Filter vents (ml) Time (seconds) Time (seconds) Blockage (%) ISO ISO 35 2 60 0 3308/4387 31 201247115

Health Canada Intense HCI 55 2 30 100 Health Canada Intense-渡嘴 通風孔打開 HCI- VO 55 2 30 0 ISO WG 9 Intense 選項 B WG9B 60 2 30 50 亦依加拿大衛生部(1"9)所述測量側流煙(SS)出量,但 其只在ISO煙產生參數下斜對各種煙成分。%試驗由 Labstat International ULC 進行。 2.4統計分析 利用黯abvl6執行的雙尾不 計比較不同捲菸類型的煙出量。* 和、很疋、,死 . y ^ ^其顯示顯著水準ρ<0·01和 Ρ<〇.=,任何Ρ值〉0.05表々顯著(NS)。Health Canada Intense HCI 55 2 30 100 Health Canada Intense-Wheel Vents Open HCI- VO 55 2 30 0 ISO WG 9 Intense Option B WG9B 60 2 30 50 Sidestreams are also measured as described by Health Canada (1"9) Smoke (SS) yield, but it is skewed against various smoke components only under ISO smoke generation parameters. The % test was performed by Labstat International ULC. 2.4 Statistical analysis The two-tailed execution using 黯abvl6 does not count the amount of smoke from different cigarette types. * and , very awkward, dead. y ^ ^ which shows significant levels ρ <0·01 and Ρ<〇.=, any 〉 value >0.05 is significant (NS).

DarHng統計法,就常態分布2\= ’ And_ 部,厕,.c。她等人,公開資料集(加拿大衛生 估4丨丨田μ· · u κ〜a ’澳洲衛生部’ 2002)的平均 值。利用Minitab ν16内建的缝 資料的百分位分布。 ,累積分布分析,計算毒物 3.結果與討論 在一些機器吸煙條件下,鼓DarHng statistical method, the normal distribution 2\= ‘And_ department, toilet, .c. She and others, the average of the public data set (Canadian Health Assessment 4 丨丨田μ·· u κ~a ‘Australian Health Ministry' 2002). Use the percentile distribution of the seam data built into Minitab ν16. , cumulative distribution analysis, calculation of poisons 3. Results and discussion Under some machine smoking conditions, drums

物出量來進行EC試驗,以從^4定量⑽成分和特定毒 的實際性能。 $ &物和煙化學觀點檢視EC 32 201247115 亦利用ISO吸煙數據圖表,測量EC的SS排放。在兩 個市售捲菸與三個科學對照捲菸的比較基礎下進行試驗。 最後,比較幾個國家先前公開的捲菸MS出量資料和特定 毒物出量與尼古丁出量的比率,評估EC的整體性能。 3.1主流煙成分出量 表4(第2圖)列出主要煙成*(NFdpm、尼古丁與C0) 和甘油在四種吸煙機條件下的出量。此表包括甘油測量係 因用於EC TSS1和TSS6的菸草代替片已併入甘油來稀釋 煙特殊相中的其他煙成分。 表4顯示BT1和CC1在四種吸煙定制下的MS NFDPM 與尼古丁出量十分相配,但BT1的CO出量比CC1少。TSS1 和CC1在四種吸煙定制下的NFDPM與尼古丁出量十分相 配,但TSS1的CO出量比CC1少。TSS1有較高甘油出量, 此與TSS的甘油含量帶來的預期稀釋作用一致。TSS6和 CC6在四種吸煙定制下的MS NFDPM與尼古丁出量十分相 配,除了 CC6有較高CO出量,TSS6預計有較高甘油出量。 依吸煙機條件:ISO<HCI-VO<WG9B<HCI,按相同排 序測量這些主要煙分析物的出量。1 mg產品在不同定制的 出量差異實質大於6mg產品’對lmg產品而言,由於通風 程度較咼’故WG9B與HCI定制的通風孔阻塞影響更深 遠。對6mg產品而言,一些定制的主要煙測量(Nfdpm、 尼古丁與CO)差異很小(5%·10%)。 亦在表3列出的所有吸煙機條件下,測量此作業定量 的47種毒物,除了不收集EC TSS1與ΒΪ1在ISO機器吸 33 201247115 煙條件下的資料,此係因為初步運作顯示許多成分的出量 低於方法的定量極限(LOQ)。這些毒物的機器吸煙出量通常 按表4列示的NFDPM、尼古丁與c〇排序,故本文其餘部 分僅描述在HCI條件下得到的出量。觀察除一般出量趨勢 外的某些一致性例外。在所有產品中,揮發性苯酚、喹啉 和芴不隨吸煙定制強度與主要煙測量出量提高而有系統地 增加;砷、菲和PAH系列的苯并芘測量亦顯示大多數產品 具此行為。特別地,儘管HCI定制產生較多總煙量,然這 些物種在WG9B定制下的出量大於HCI定制。已知使用乙 酸纖維素濾嘴可選擇性去除煙中的揮發性苯紛;在此觀察 到的一致性行為可表示這些物種在WG9B與HCI定制下的 一些過濾效率變化。或者,其可代表測量方法在高強度吸 煙定制下的一些分析弱點。觀察一些更特殊分析物的類似 變化(如從各種吸煙定制下的其他五個產品趨勢發現CC1 的1,3·丁二烯出量少於預期);此對6mg產品尤其如是。當 在不同吸煙定制下產生類似的NFDPM量時,這些觀察結 果可能係分析誤差或反映分析技術的識別能力極限。 此作業採用HCI吸煙定制代表將對EC和市售比 較捲终進行最嚴格的試驗。雖然這些吸煙條件會鈍化EC和 市售捲菸的設計特徵結構(濾嘴通風孔),但仍為評斷由通風 捲於取得的機器出量值。 3.1.1金屬與tSNA出量 管制名單包括金屬和菸草特有亞硝胺(TSNA)兩組毒 物°這兩組毒物主要受捲菸製造用菸草摻合物影響,故仔 ⑤ 34 2〇1247115 .細遂擇摻合物可有效減少煙量。表5(第3圖)列出摻合金屬 與丁SNA的化學分析,表6(第4圖)列出其在HCI吸煙機條 件f的MS出量。各個EC的出量將於以下第3.1.2.1節至 第3.1.2.3節討論。 3·1·2其他毒物出量 表7(第5圖)列出在HCI吸煙機條件下,EC與市售對 照組的煙成分出量比較。各個EC的出量將於以下第3.1.2.1 節炱第3.1.2.3節討論。 3.1.2.1 ΒΤ1 摻合物化學測量(表5)顯示ΒΤ1的摻合砷和鉻含量統計 上明顯高於市售捲於CC1 ’ ΒΤ1的摻合錯和鎳含量則較低。 除了砷和汞出量較多’ ΒΤ1的金屬的MS出量相當於或少 於CC1的出量。較多砷出量可能係因砷金屬摻合含量較 高,但BT1的汞摻合含量相當於或少於CC1且低於此金屬 的LOQ(表5),故汞出量無法以摻合含量解釋且可能為加工 品0 如同先前維吉尼亞與US摻合型捲菸的比較,BT1的摻 合亞硝胺含量比US摻合型市售比較組CC1低。基於兩個 理由,BT1的含氮成分的MS出量預計比CC1少:第一, 菸草處理會減少含氮煙化合物的前驅物;第二,維吉尼亞 型菸草產生的含氮煙成分出量通常比US摻合型捲菸少。含 氮化合物的出量測量顯示預期差異:BT1的TSNA出量 (83°/〇-96%)統計上明顯比CC1少(表6) ; BT1的芳香胺出量 較CC1少26%-57%(表7) ; BT1的其他含氮化合物出量亦 35 201247115 實。質較CC1的各種出量少(HCN少82%、NO少79%、氨少 75% °比°定少97%、喹琳少67%、丙稀腈少69%)。這些資 料也實選擇換合物、採用Βτ方法(及就hcn出量將如〇 併入^嘴)可使Ec產出預計較少的毒物出量。 屮吾τ方去還可減少摻合多酚量,故也有望減少Ms苯酚 夕3然維吉尼亞型產品的酴搭出量通常比US摻合型產品 夕’疋以不同於草種類將減弱BT方法的減少效果。比較 CC1與BT1的祕化合物出量呈現混合情況:苯紛、對甲 齡和間苯二盼出量少於BT1,而間曱盼、鄰苯二齡和對笨 二酚出量高於BT1(表7)。 _ BT方法;I;影響料$出量和pAH分析,目前研究顯 不BT1的芴、菲、芘和笨并祐出量與cci相當。除阳 有較多甲酸出量(41%)外,捲於BT1的幾出量較少(少26% ^ 74%)。相較於CC1的各種成分出量,ΒΉ的揮發性烴出 量較少,其中異戊二稀、苯、甲苯和蔡為21%至78%;缺 BT1的1>3_ 丁二稀出量比CC1多35〇/〇。在Ηα定制下,^ 的1,3-丁二烯出量少於預期,故此觀測結果並不可靠。揮 發性成分出量的觀測差異大多與ΒΤ1據嘴使用的有效氣相 吸附劑一致。曱醛出量部分取決於糖量,維吉尼亞型換合 物的糖量通常比US型摻合物高。甲醛出量亦因摻合物處理 方法而增加。故根據對捲菸產生曱醛的了解,當可理解βτι 有較多曱醛出量。cci的出量測量誤差可心BT1有明顯 較多的1,3-丁二婦出量,此係因為無顯而易見的機械因素 支持此差異(統計上,料處理方料會提供明軸】Μ ⑤ 36 201247115 二烯出量變化’ BT1濾嘴使用氣相吸附劑應使BT1產生較 少的1,3-丁二烯出量)。第3.2節將強調BT1的摻合物和選 擇性濾嘴對整體煙毒物減少的貢獻,此結果與摻合物化學 因素引起的較高曱醛出量值(表7)—致。 3.1.2.2 TSS1 就一些金屬(砷、鉻和鎳)而言,TSS1的整體摻合金屬 含量比CC1高’但鎘含量較低’其他金屬則無差異(表5)。 TSS含有高比例的生石灰’其將貢獻一部分的摻合金屬。 TSS分析顯示其含鉻量比TSS1高,其他測量金屬量則差不 多或較低。故TSS1有較CC1高的鉻含量極可能係因摻合 物包括TSS材料,較南钟和鎳量極可能係因摻合物使用不 同菸草類型。應注意由於生石灰和菸草中的微量金屬化學 形式(和揮發性)不同,TSS轉移金屬的效率不需和於草一The amount of material was subjected to an EC test to quantify the actual properties of the (10) component and the specific toxicity from ^4. $ & chemistry and smoke chemistry review EC 32 201247115 Also use the ISO smoking data chart to measure EC SS emissions. Experiments were conducted on the basis of a comparison between two commercially available cigarettes and three scientific control cigarettes. Finally, the overall performance of the EC was evaluated by comparing the previously published cigarette MS output data and the ratio of specific toxic yield to nicotine yield in several countries. 3.1 Mainstream smoke constituents Table 4 (Figure 2) lists the major tobacco yields* (NFdpm, nicotine and C0) and glycerol yield under four smoking machine conditions. This table includes glycerol measurements because tobacco substitute tablets for EC TSS1 and TSS6 have been incorporated into glycerin to dilute other smoke components in the smoke specific phase. Table 4 shows that the MS NFDPM of BT1 and CC1 under four smoking customizations is very compatible with the nicotine yield, but the CO yield of BT1 is less than that of CC1. TFS1 and CC1 have a good match between NFDPM and nicotine yield under the four smoking rules, but TSS1 has less CO yield than CC1. TSS1 has a higher glycerol yield, which is consistent with the expected dilution effect of the glycerol content of TSS. The MS NFDPM of TSS6 and CC6 under four smoking customizations is very compatible with the nicotine yield. Except for CC6, the TSS6 is expected to have higher glycerol yield. Depending on the smoking machine conditions: ISO < HCI-VO < WG9B < HCI, the output of these major smoke analytes was measured in the same order. The difference in the output of 1 mg products in different custom is substantially greater than 6 mg. 'For lmg products, WG9B and HCI custom vent obstruction have far-reaching effects due to the higher degree of ventilation. For the 6 mg product, some custom major smoke measurements (Nfdpm, nicotine and CO) differed very little (5%·10%). The 47 toxicants quantified in this operation were also measured under all smoking machine conditions listed in Table 3, except that EC TSS1 and ΒΪ1 were not collected under ISO machine suction 33 201247115. This is because the initial operation shows many components. The yield is below the quantitative limit (LOQ) of the method. The machine smoking output of these poisons is usually sorted according to the NFDPM, nicotine and c〇 listed in Table 4, so the rest of the paper only describes the yield obtained under HCI conditions. Observe some consistency exceptions in addition to the general output trend. Among all products, volatile phenol, quinoline and hydrazine did not increase systematically with the increase in the custom strength of smoking and the measurement of major smoke; the measurement of benzopyrene in the arsenic, phenanthrene and PAH series also showed that most products have this behavior. . In particular, although HCI customization produces more total smoke, these species are more custom-made under WG9B customization than HCI customization. It is known to use a cellulose acetate filter to selectively remove volatile benzene from the smoke; the observed consistent behavior herein can indicate some of the filtration efficiency changes of these species under WG9B and HCI customization. Alternatively, it can represent some of the analytical weaknesses of the measurement method under high-intensity smoking customization. Observing similar changes in some of the more specific analytes (eg, from the other five product trends under various smoking customizations, it was found that CC1's 1,3·butadiene yield was less than expected); this is especially true for 6 mg products. When similar amounts of NFDPM are produced under different smoking customizations, these observations may be analytical errors or reflect the analytical ability limits of the analytical technique. This assignment uses the HCI Smoking Customized Representative to conduct the most rigorous testing of EC and commercial comparisons. Although these smoking conditions passivate the design features of the EC and commercially available cigarettes (filter vents), it is still a measure of the machine output obtained from the ventilation. 3.1.1 Metal and tSNA production control list includes two groups of toxic substances of metal and tobacco-specific nitrosamines (TSNA). These two groups of poisons are mainly affected by tobacco blends for cigarette manufacturing, so it is 5 34 2〇1247115. The blend is effective in reducing the amount of smoke. Table 5 (Fig. 3) lists the chemical analysis of the blended metal with butyl SNA, and Table 6 (Fig. 4) lists the MS yield of the HCI smoking machine condition f. The output of each EC will be discussed in sections 3.1.2.1 through 3.1.2.3 below. 3·1·2 Other Toxic Emissions Table 7 (Figure 5) shows the comparison of the smoke constituents of EC and commercially available control groups under HCI smoking machine conditions. The output of each EC will be discussed in Section 3.1.2.1, Section 3.1.2.3 below. 3.1.2.1 化学1 The chemical measurement of the blend (Table 5) shows that the arsenic and chromium content of ΒΤ1 is statistically significantly higher than the blending error and nickel content of the commercially available coil CC1 ΒΤ1. Except for arsenic and mercury, the amount of MS in the metal of ΒΤ1 is equivalent to or less than the amount of CC1. More arsenic output may be due to the higher content of arsenic metal blending, but the mercury blending content of BT1 is equivalent to or less than CC1 and lower than the LOQ of this metal (Table 5), so the mercury output cannot be blended. Interpretation and possibly processing 0 As compared to previous Virginia-US blended cigarettes, BT1 has a lower blended nitrosamine content than the US blended commercial comparative group CC1. For two reasons, the MS yield of the nitrogenous component of BT1 is expected to be less than that of CC1: first, tobacco treatment will reduce the precursor of nitrogen-containing compounds; second, the nitrogen-containing smoke produced by Virginia-type tobacco will be The amount is usually less than that of US blended cigarettes. The yield measurement of nitrogen-containing compounds showed the expected difference: the TSNA yield of BT1 (83°/〇-96%) was statistically significantly less than CC1 (Table 6); the aromatic amine yield of BT1 was 26%-57% less than CC1. (Table 7); The yield of other nitrogenous compounds of BT1 is also 35 201247115. The quality of CC1 is less than that of CC1 (HCN is 82% less, NO is 79% less, ammonia is 75% lower, 97% less than °, 67% less quinoline, and 69% less acrylonitrile). These materials are also selected for the compound, using the Βτ method (and incorporating hcn yields such as 〇 into the mouth) to allow Ec to produce less expected toxic emissions. The 屮吾τ方 can also reduce the amount of polyphenols blended, so it is also expected to reduce the amount of bismuth in the Ms phenols. The virgins of the virgin products are usually more than the US blended products. Reduce the reduction effect of the BT method. Comparing the amount of secret compounds of CC1 and BT1 in a mixed situation: the amount of benzene, the age of the pair and the amount of meta-phenylene are less than BT1, while the yield of phthalate, phthalate and bisphenol is higher than BT1 ( Table 7). _ BT method; I; impact material $ output and pAH analysis, the current study shows that BT1 芴, Philippine, 芘 and 笨 佑 and the amount of cci is comparable. In addition to the amount of formic acid (41%), the amount of BT1 was less (26% ^ 74% less). Compared with the output of various components of CC1, the volatile hydrocarbons produced by hydrazine are less, among which isoprene, benzene, toluene and Cai are 21% to 78%; and BT1 is less than 1> CC1 is 35 〇/〇. Under the Ηα customization, the 1,3-butadiene output of ^ is less than expected, so the observation is not reliable. The observed differences in the amount of volatile components are mostly consistent with the effective gas phase adsorbents used in the mouth. The amount of furfural output depends in part on the amount of sugar, and the amount of sugar in the Virginia-type blend is generally higher than in the US blend. The amount of formaldehyde produced is also increased by the blend processing method. Therefore, according to the knowledge of the production of furfural in cigarettes, it can be understood that βτι has more furfural output. The measurement error of cci can be significantly higher than that of BT1. This is because there is no obvious mechanical factor to support this difference (statistically, the material processing will provide the axis) Μ 5 36 201247115 Change in diene output 'The use of a gas phase adsorbent in BT1 filters should result in less 1,3-butadiene output from BT1). Section 3.2 will emphasize the contribution of BT1 blends and selective filters to overall smoke toxic reduction, which is consistent with the higher furfural yields due to the chemical factors of the blend (Table 7). 3.1.2.2 TSS1 For some metals (arsenic, chromium and nickel), the overall blended metal content of TSS1 is higher than CC1 but the cadmium content is lower. Other metals have no difference (Table 5). TSS contains a high proportion of quicklime 'which will contribute a portion of the blended metal. TSS analysis showed that the chromium content was higher than TSS1, and the other measured metal amounts were not much or low. Therefore, TSS1 has a higher chromium content than CC1. It is most likely due to the inclusion of TSS material. The amount of Nanzhong and nickel is probably due to the different types of tobacco used in the blend. It should be noted that due to the different chemical forms (and volatility) of trace metals in quicklime and tobacco, the efficiency of TSS transfer metals does not need to be the same as that of grass.

樣。故比較TSS1和CC1發現’在HCI吸煙機條件下MS 中的金屬出量較少或無統計顯著差異(表6),TSS1的摻合 亞硝胺含量比CC1少(23%-72%)(表5),TSS1的TSNA在 HCI吸煙機條件下的MS出量相應較CC1少(17%至69%)(表 6)。 統 s十上 ’ TSS1 的齡搭(29%-57%)、幾(44%-86%)、 PAH(8%至71 %)和混雜揮發性成分(27%至94%)出量明顯比 CC1少,然在鄰苯二酚、對苯二酚和苯并芘方面的差異則 未達統计顯著性(表7卜這些資料顯示TSS1在各類檢驗分 析物方面有較少毒物出量’故可佐證TSS和三段渡嘴能減 少EC的整體Ms毒物出量。 201247115 3·1·2.3 TSS6 、TSS6和CC6的摻合金屬含量類似,但統計上,TSS6 的鉻和鎘摻合量明顯較高◊如上所述,較高鉻量極可能係 的高無機含量,較高鎘量極可能係因二摻合物使用 不同菸草種類。TSS6的鎘和鉻在HCI吸煙機條件下測定的 S出量不比CC6多(表6),此再次證實EC與市售比較組 中的金屬化學形式不同且不太可能轉移到MS。 TSS6的摻合亞硝胺含量(39%至54%)比CC6摻合物低 (表5)。再者,此較低摻合亞硝胺含量轉換成TSNA在HCI 吸煙機條件下的較低MS出量(37%至50%)(表6)。 統計上,除1_與2_胺萘和間與對甲酚的數值無顯著差 異且較多氨出量(13%)與CC6無顯著差異(表7)外,TSS0在 所有其他測量化學種類# MS iU量(芳香胺(13%-20%)、酚 酸(8/ό 32/ί>)、&(35%_85%)、PAH(18%-81%)和混雜揮發性 毒物(41 /。_96°/。))明顯比CC6的出量少。這些資料再次證實 所有測量毒物種類減少,故TSS顯然可如預期用於Ec而 減少整體MS毒物出量。 3.2據嘴比較 從表7所列MS出量資料可知,除了 BT1的曱醛和U· 丁一烯出直,所有£C提供比各市售比較捲终少的羰和氣相 成刀出里。為更清楚了解的掺合物和選擇性滤嘴對整體 煙成分減少的貢獻,乃直接比較EC與對照捲菸(SC_BT1、 SC-TSS1和SC-TSS6),其除使用無吸附劑的單段CA濾嘴 外,在所有方面都和適當EC —樣。表8和表9(分別為第6 201247115 及7圖)列出EC與對照捲終的幾和其他氣相成分出量比較。 從這些資料清楚可知,羰和其他氣相成分出量皆因存 有含CR20L與EC BT1和TSS1所用高活性碳的三段滤嘴 而減少(表8)。在BT1的所有測量揮發性成分中,Ms出量 的平均變化較對照捲菸SC_BT1減少50%,其中乙酿減少 23%’巴豆醛減少79%。TSS1亦有非常相似的減少效果, 其平均減少50%,其中相較於SC-TSS1,甲醛出量減少 10%,巴豆醛出量減少79%。 從表9可知’含附加聚合物衍生碳、但無CR20L樹脂 (如用於TSS6)的兩段濾、嘴亦使氣相煙成分出量平均減少 48%’其中乙醛出量減少11%,巴豆醛出量減少79〇/〇。這 些資料一同證實用於E C的選擇性濾嘴移除捲終M 8中的大 量揮發性煙成分及確定先前過濾吸附劑試驗。對所有EC而 吕’甲酸與1,3-丁二烯的MS出量比科學對照捲终測量值 少。相較於TSS1/SC-TSS1組對減少1.9微克/捲於 (Kg/cig)(10%) ’ BT1/SC-BT1組對從較高起始值減少更多甲 醛出量(53pg/cig或53%)表示CR20L樹脂去除MS中的甲 醛的性能較高活性碳佳。比較BT1與市售捲終CC1(表7) 後發現曱Sk·出1較多顯然係因捲於的播合物不同。類似比 較亦證實BT1的1,3-丁二烯出量比CC1多極可能係因CC1 的1,3-丁二烯測量分析誤差所致。 3.3比較EC毒物出量與公開捲菸品牌資料 本文著重於比較EC毒物出量與兩種市售比較捲終的 出量。然為徹底確認EC是否提供比習用市售捲於少的機器 39 201247115 出量,需比較其出量與各種捲菸。比較所述EC的絕對出量 值與在HCI吸煙條件下取得的其他公開資料(即:(1)加拿大 衛生部(2004)發表的文獻”Constituents and emissions reported for cigarettes sold in Canada” , http://www.hc-sc.gc.ca/hc-ps/alt_formats/hecs-sesc/pdf/tobac tabac/legislation/reg/indust/constitu-eng.pdf(西元 2010 年 11 月存取);資料取自 TRR_RRRT@hc-sc.gc.ca ; (2)Counts,Μ· Ε.等人(2005)發表的文獻’’Smoke composition and predicting relationships for international commercial cigarettes smoked with three machine-smoking conditions; Regul. Toxicol. Pharmacol. 41, 185-227” ;和(3)澳洲衛生和老齡部: http://www.health.gov.au/internet/main/publishing.nsf/Conte nt/tobacco-emis(西元2010年11月存取))。然應注意由於難 以以各實驗室分析除NFDPM、尼古丁與CO外的煙成分的 限定標準化為基礎,故需小心處理比較結果。 以上三個資料來源彙編成資料集,以提供全球捲菸出 量資料參考集,其可與本文所述EC的毒物出量相比。完整 資料集截斷如下:第一,刪除資料集的石申、曱基乙基酮、 鎳和硒出量,因為三個來源皆未提供出量;第二,刪除資 料集的一些品牌,因有不完整、重複或錯誤資料(HC資料 集的兩種品牌似乎有錯誤(對調)的曱苯和苯乙烯出量; GitanesKS的HC資料集未提供焦油、尼古丁和CO出量, 且HC資料集中有多筆相同出量資料)。最後,刪除資料集 的參考產品’以確保只有市售品牌包括在内。如此獲得的 201247115 資料集將涵蓋16個國家或地區的120種捲菸品牌。雖然廣 泛,但無論是在設計特徵方面或做為全球品牌的代表性樣 品,此資料集不太可能完全代表全球販售的捲菸產品。儘 管在這些方面有所限制,然其的確針對這些EC的毒物出量 建立了有效比較集。 檢驗資料,確認其是否為常態分布。雖然資料集中的 一些毒物為常態分布,但大多數(尤其係含氮毒物,例如 TSNA和芳香胺)則不然。因此,參考集需經經驗累積分布 分析處理,以產生毒物出量的百分位分布。接著比較EC的 出量與經驗累積分布,確定這些出量相較於市售品牌的位 置(第8及9圖)。比較發現,所述EC的出量落在眾多毒物 範圍的下端,且通常提供比市售品牌資料集中的任何產品 低的特定毒物值。但BT1的兒茶酚出量和TSS1與TSS6的 NO與TSNA出量為例外,其出量約等於市售產品資料集的 中位值。反之,市售比較捲於CC1和CC6的出量通常分布 在市售資料集的出量範圍。 進一步比較檢驗EC和資料集中各市售產品的毒物總 量,其方式有三。第一種方法為加總各捲菸的39種毒物出 量,以提供各品牌的總體毒物出量(TTY)。此法效用有限, 因為各品牌的TTY值主要取決於焦油、CO和尼古丁,許 多其他毒物對總值無顯著貢獻。第二種方式為加總各捲菸 的所有毒物出量(但排除焦油、尼古丁和CO出量),以提供 總體毒物子集出量(TSY)。第三種正規化法為更深入了解所 有毒物貢獻,其計算市售資料集中各毒物的中位值。將各 201247115 =物的中位值正規化成100,並對應100,比例調整毒物出 里。,计所有毒物的比例值而獲得各品牌的總體正規化毒 物出量(NTT)。比較EC的TTY、TSY和NTT值與第10至 =圖市售資料集中所有品牌的數值及排名。比較結果顯 不,利用各種方式,EC係排在排名下端。利用各種方式, ImgEC有最少總體毒物出量,6mgE(:的TSY* NTT也比 任何市售品牌低。在ττγ分析中,12〇種市售產品中有兩 個的ΤΤΥ值比TSS6低’此係因為其具較低焦油和尼古丁 值。相較於市售品牌資料集’市售比較捲菸CC1和CC6亦 有相當低的總體毒物值,其約落在數值的較小四分位數。 這些分析一同顯示,EC提供可取得公開HCI吸煙化學 的捲菸的某些最少機器毒物出量。故這些比較結果證實£〇 可產生比已知市售捲菸少的機器毒物出量。 3.4比較以尼古丁出量比率表示的ec出量 上述分析限於評估毒物的機器出量。然據悉菸草的煙 毒物與MS尼古丁出量比率較單單MS出量值適合預測吸煙 者接觸毒物量。故計算本文測量的MS成分出量與MS尼古 丁出量比率(皆在HCI吸煙機條件下測量)及列成附表(表 10 ’第8A及8B圖)。在HCI機器吸煙條件下,BT1、TSS1 和CC1的NFDPM出量相當,但BT1的尼古丁出量略多, TSS1的尼古丁出量略少於CC1(表4和表7)。以尼古丁出 量比率計算EC的出量值並與CC1和CC6相比後發現,其 依循和每捲於出量比較結果一樣的趨勢,但BT1的數值明 顯比CC1小,TSS1的數值則沒比cci小那麼多。 ⑤ 42 201247115 3.5側流煙出量 為完成化學分析EC排放煙,乃測量擴大列出的煙成分 在ISO吸煙參數下的SS出量。選擇ISO吸煙參數係因其產 生比任何其他吸煙定制多的SS出量。通常,在任何吸煙定 制下,侧流煙量預計與靜態燃燒或吸煙悶燒時的菸草消耗 量有關。SS出量結果列於表10,用以比較EC BT1和TSS1 與市售捲菸CC1。 統計上,BT1的側流NFDPM出量(21%)和諸如苯并芘 (28%)、酚醛(28%-77%)、羰(22%-63%)和揮發性烴(20%-24〇/〇) 成分等數種成分出量明顯比CC1多。反之,BT1的含氮SS 煙成分出量比CC1少,例如TSNA(31 %-82%)、HCN(47%)、 芳香胺(21%-40%)、氮氧化物、吡啶和喹啉(19%-35°/〇)。先 前多已描述這些變化(Liu等人,2010),然BT1有較多SS 酴酸出量和比預期少的TSNA出量意味著維吉尼亞種與US 摻合型菸草的化學差異亦會影響個別成分的SS出量。最 後’ BT1的菸草重量比CC1重13%亦將全面促成觀察量增 加。 EC捲菸TSS1的許多SS煙成分出量比CC1少。最大 的SS出量差值為TSNA,其中TSS1比cci少28%至52%。 這些觀測結果與觀察這些物種的MS出量趨勢一致。廣泛 減少極可能反映因併入TSS以致捲菸的菸草質量減少,從 而降低產生的總體煙量。統計上,TSS1明顯較CC1多的側 流成分出量為曱醛(多19%)。較多SS曱醛出量亦偕同觀測 到摻合物包括較高TSS量(McAdam等人,2010),此意味 著曱醛可能係用於TSS製造的有機材料的燃燒副產物。 43 201247115 4.結論 參赵合技射式製作三種Ec且在四種不同機器吸煙 +歎^行化學試驗可證實Ec & MS無出量將整體減 甲蚁於習用捲於的公開Ms毒物出量值,儘管BT1的 似…量較多,然即便按尼古丁出量排名,這些EC的性能 、.交佳。本文資料支持將這些Ec做為減少機器出量原 广TSS方式製作的EC的先前資料顯示,當吸煙者使 24二^ΜΥΡ時,有較少生物標記接觸MS毒物。 儘管目^RMYp可得到低整體毒物機器出量,然其相 曰市售比較組和其他公開毒物出量資料的性能仍需取得大 量=學資料’包括接觸生物標記和生物作用生物標記,以 決定此產品是否與較低健康風險有關,因此無法確定這些 RMYP符合pREp的I〇M定義。 但咸信本研究結果足以鼓舞進一步作業,包括這些 RMYP的人體生物標記研究與進一步應用及提升其製造技 術。 5.原型吸煙物件 根據本發明製造三種原型RTP吸煙物件。捲菸具特大 尺寸,其濾嘴長度為27mm,菸草棒為56mm。原型的菸草 棒包含薄片、膨脹菸草和非菸草片或改質菸草的混合物。 習用捲於紙用於形成菸草棒及確保達到燃燒率和後續煙團 數量。 兩種原型的濾嘴係由CA 口端段(長7mm)、含CR20HD 離子交換樹脂(長10mm)的CA中間段與含具加工微結構之 201247115 炭珠粒的斑點型終草端段(長1Gmm)組成的三段滤嘴。第三 ,原型的濾、嘴為由CA 口端段(長15mm)與含高活性聚合物 何生碳珠粒的斑點型菸草端段(長12mm)組成的兩段濾嘴。 原型捲菸製造成提供lmg(T562m3H671)和6mg(F752) 的ISONFDPM出量。表n至表13詳列原型捲終規格。 .. ^ 草摻合物規格 原型 _ TS62(lmg) H671(lmg) F752(6mg) 薄片(%wwb) ___40 12.5 55.0 膨脹终草a(%wwb) 40 ---— 12.5 膨脹於草b(%wwb) 25.0 改質柊草c (%wwb) _ 75 非菸草片d(%wwb) 20 20 增添頂級香料 0.8 0.8 0.8 (AWOLS A)(%wwb) a a 為八八八羞..^ . —kind. Therefore, comparing TSS1 and CC1 found that there was little or no statistically significant difference in metal yield in MS under HCI smoking machine conditions (Table 6), and the content of nitrosamine in TSS1 was less than that of CC1 (23%-72%). Table 5), the TSNA of TSS1 was correspondingly less than CC1 (17% to 69%) under HCI smoking machine conditions (Table 6). The total number of TSS1 (29%-57%), several (44%-86%), PAH (8% to 71%) and mixed volatile components (27% to 94%) is significantly higher than that of TSS1. CC1 was less, but the difference in catechol, hydroquinone and benzopyrene was not statistically significant (Table 7 shows that TSS1 has less toxic yields in various test analytes' Therefore, it can be proved that TSS and three-stage ferry can reduce the total Ms poison yield of EC. 201247115 3·1·2.3 TSS6, TSS6 and CC6 have similar blending metal content, but statistically, TSS6 has obvious chromium and cadmium blending amount. Higher ◊ As mentioned above, the higher chrome content is most likely to be high in inorganic content, and the higher cadmium is most likely due to the use of different tobacco species for the two blends. The cadmium and chromium of TSS6 are determined under HCI smoking machine conditions. The yield was not more than that of CC6 (Table 6), which again confirmed that the chemical form of the metal in the EC and the commercially available comparative group was different and was unlikely to be transferred to MS. The blended nitrosamine content of TSS6 (39% to 54%) was higher than that of CC6. The blend was low (Table 5). Furthermore, this lower blended nitrosamine content was converted to a lower MS yield (37% to 50%) of TSNA under HCI smoking machine conditions (Table 6). ,except There was no significant difference between the values of 1_ and 2_amine naphthalene and p-cresol and the amount of ammonia (13%) was not significantly different from that of CC6 (Table 7). TSS0 was in all other measured chemical species # MS iU (Aromatic amines (13%-20%), phenolic acids (8/ό 32/ί>), & (35%_85%), PAH (18%-81%) and mixed volatile poisons (41 /._96 ° /.)) significantly less than the amount of CC6. These data again confirmed the reduction of all types of measured poisons, so TSS can obviously reduce the overall MS toxic emissions as expected for Ec. 3.2 According to the mouth comparison from the MS listed in Table 7 According to the output data, except for the furfural and U·butene of BT1, all of the £C provides less carbonyl and gas phase than the commercial ones. For a clearer understanding of the blend and selectivity. The contribution of the filter to the overall smoke composition reduction is directly compared to EC and control cigarettes (SC_BT1, SC-TSS1 and SC-TSS6), which are in all respects and appropriate EC except for the use of a single-stage CA filter without adsorbent. Similarly, Tables 8 and 9 (Fig. 6 201247115 and Figure 7 respectively) show the comparison of the EC and the control volume and other gas phase components. It is clear from these data that carbonyl and other gases The phase component yield was reduced by the presence of a three-stage filter containing CR20L and EC BT1 and TSS1 high-activity carbon (Table 8). Among all the measured volatile components of BT1, the average change in Ms yield was lower than that of the control cigarette. SC_BT1 is reduced by 50%, of which B is reduced by 23%, and crotonaldehyde is reduced by 79%. TSS1 also has a very similar reduction effect, which is reduced by an average of 50%, which is 10% less than SC-TSS1, and crotonaldehyde is reduced. The output was reduced by 79%. It can be seen from Table 9 that the two-stage filtration and the mouth containing the additional polymer-derived carbon but no CR20L resin (such as for TSS6) also reduce the gas phase smoke component output by an average of 48%, wherein the acetaldehyde output is reduced by 11%. The yield of crotonaldehyde was reduced by 79〇/〇. Together, these data demonstrate the use of a selective filter for E C to remove large amounts of volatile smoke components from the final M 8 and to determine previous filtered adsorbent tests. The MS yield of all EC and 1,3-carboxylic acid and 1,3-butadiene was less than the final measurement of the scientific control. Compared with the TSS1/SC-TSS1 group, the reduction of 1.9 μg/volume in (Kg/cig) (10%) ' BT1/SC-BT1 group reduces the amount of formaldehyde emission from the higher starting value (53pg/cig or 53%) indicates that the performance of the CR20L resin for removing formaldehyde in the MS is higher than that of the activated carbon. Comparing BT1 with the commercially available final CC1 (Table 7), it was found that 曱Sk·1 was more likely to be different due to the mixed composition. Similar comparisons have also confirmed that the 1,3-butadiene output of BT1 is more likely to be due to the CC1 1,3-butadiene measurement analysis error. 3.3 Comparison of EC toxicant output and public cigarette brand data This article focuses on comparing EC toxicant yields with the output of two commercial comparison volumes. However, in order to thoroughly confirm whether the EC provides a machine that is less than the market volume that is used in the market, it is necessary to compare the output with various cigarettes. Compare the absolute output of the EC with other published information obtained under HCI smoking conditions (ie: (1) Canadian Health (2004) published literature" Constituents and emissions reported for cigarettes sold in Canada", http:/ /www.hc-sc.gc.ca/hc-ps/alt_formats/hecs-sesc/pdf/tobac tabac/legislation/reg/indust/constitu-eng.pdf (accessed November 2010); data taken from TRR_RRRT@hc-sc.gc.ca; (2) The literature published by Counts, Μ·Ε. et al. (2005) 'Smoke composition and predicting relationships for international commercial cigarettes smoked with three machine-smoking conditions; Regul. Toxicol. Pharmacol. 41, 185-227”; and (3) Australian Department of Health and Ageing: http://www.health.gov.au/internet/main/publishing.nsf/Conte nt/tobacco-emis (England 2010 11 Monthly access)). However, it should be noted that because it is difficult to analyze the definition of smoke components other than NFDPM, nicotine and CO in various laboratories, the comparison results should be handled carefully. The above three sources are compiled into data sets to Provide global cigarette output data The collection can be compared with the toxic yield of the EC described in this article. The complete data set is truncated as follows: First, delete the data set of Shishen, mercapto ethyl ketone, nickel and selenium, because all three sources are No supply was provided; second, some brands of the data set were deleted due to incomplete, duplicate or erroneous data (the two brands of the HC data set seem to have errors (opposed) of benzene and styrene output; GitanesKS HC The dataset does not provide tar, nicotine, and CO yields, and there are multiple copies of the same data in the HC data set. Finally, delete the reference product of the dataset to ensure that only commercially available brands are included. The 201247115 dataset so obtained It will cover 120 cigarette brands in 16 countries. Although extensive, whether in design features or as a representative sample of global brands, this data set is unlikely to fully represent the globally sold cigarette products. There are limits to these aspects, but it does establish an effective comparison set for the toxic emissions of these ECs. Check the data to see if it is normal. Although some of the toxicants in the dataset are normally distributed, most (especially nitrogen-containing toxicants such as TSNA and aromatic amines) do not. Therefore, the reference set needs to be processed by empirical cumulative distribution analysis to produce a percentile distribution of toxic emissions. The EC's output and empirical cumulative distribution are then compared to determine the location of these outputs compared to commercially available brands (Figures 8 and 9). It has been found that the EC yield falls below the broad range of toxicants and typically provides a lower specific toxic value than any product in the marketed brand data set. However, the catechol yield of BT1 and the NO and TSNA yields of TSS1 and TSS6 are exceptional, and the yield is approximately equal to the median value of the commercially available product data set. Conversely, the volume of commercially available comparative volumes in CC1 and CC6 is usually distributed in the range of the market data set. Further comparisons were conducted to examine the total amount of poisons in each of the commercially available products in the EC and datasets in three ways. The first method is to add up to 39 toxicants from each cigarette to provide overall toxic yield (TTY) for each brand. This method has limited utility because the TTY values of each brand depend mainly on tar, CO and nicotine, and many other toxicants do not contribute significantly to the total value. The second way is to sum up all toxic emissions from each cigarette (but exclude tar, nicotine, and CO emissions) to provide overall toxic sub-collection (TSY). The third normalization method provides a deeper understanding of all toxicant contributions, and it calculates the median value of each toxicant in the market data set. The median value of each 201247115 = object is normalized to 100, and corresponds to 100, and the poison is adjusted proportionally. The total normalized toxicant output (NTT) of each brand is obtained by taking the proportion of all poisons. Compare the TTY, TSY and NTT values of the EC with the values and rankings of all brands in the 10th to = map market dataset. The comparison results are not obvious. In various ways, the EC system ranks at the bottom of the ranking. In all ways, ImgEC has the least overall toxic yield, and 6mgE (: TSY* NTT is also lower than any commercially available brand. In the ττγ analysis, two of the 12 commercially available products have lower enthalpy than TSS6' Because it has lower tar and nicotine values, it also has a fairly low overall toxic value compared to the commercially available brand data set 'commercially available cigarettes CC1 and CC6, which fall below the smaller quartile of the values. The analysis shows that the EC provides some minimum machine poison yield for cigarettes that have access to open HCI smoking chemistry. Therefore, these comparisons confirm that there is less machine poison output than known commercial cigarettes. 3.4 Comparison with nicotine The amount of ec indicated by the ratio is limited to the evaluation of the machine yield of the poison. However, it is reported that the ratio of tobacco smoke to MS nicotine yield is better than the single MS yield value to predict the amount of toxicant smoked by the smoker. Therefore, the MS component measured here is calculated. The ratio of yield to MS nicotine output (measured under HCI smoking machine conditions) and the schedule (Table 10 '8A and 8B). Under HCI machine smoking conditions, NFDPM of BT1, TSS1 and CC1 Quite, but the nicotine yield of BT1 is slightly higher, and the nicotine yield of TSS1 is slightly less than CC1 (Table 4 and Table 7). The yield of EC is calculated by the ratio of nicotine yield and compared with CC1 and CC6. The trend is the same as the comparison of the volume per volume, but the value of BT1 is significantly smaller than CC1, and the value of TSS1 is not much less than that of cci. 5 42 201247115 3.5 The amount of sidestream smoke is the chemical analysis of EC emissions. It measures the amount of SS produced by the expanded smoking constituents under ISO smoking parameters. The ISO smoking parameter is chosen because it produces more SS yield than any other smoking custom. Usually, under any smoking custom, sidestream smoke is expected. It is related to tobacco consumption during static burning or smoking smoldering. The SS yield results are shown in Table 10 to compare EC BT1 and TSS1 with commercial cigarette CC1. Statistically, lateral flow NFDPM yield of BT1 (21%) And several components such as benzopyrene (28%), phenolic (28%-77%), carbonyl (22%-63%) and volatile hydrocarbons (20%-24〇/〇) are significantly more than CC1. Conversely, BT1 contains less nitrogen-containing SS components than CC1, such as TSNA (31%-82%), HCN (47%), aromatic amines (21%-40%), Oxides, pyridines and quinolines (19%-35°/〇). These changes have been previously described (Liu et al., 2010), but BT1 has more SS tannic acid output and less than expected TSNA yields. The chemical difference between Virginia and US blended tobacco will also affect the SS yield of individual components. Finally, the tobacco weight of BT1, which is 13% heavier than CC1, will also contribute to the increase in observations. Many SSs of EC Cigarette TSS1 The amount of smoke components is less than that of CC1. The maximum SS output difference is TSNA, where TSS1 is 28% to 52% less than cci. These observations are consistent with observations of MS yield trends for these species. The widespread reduction is highly likely to reflect the reduction in the quality of tobacco produced by the incorporation of TSS into cigarettes, thereby reducing the overall amount of smoke produced. Statistically, the amount of lateral component of TSS1 was significantly higher than that of CC1 (furfural 19%). More SS furfural yields were also observed to include higher TSS levels (McAdam et al., 2010), which means that furfural may be a by-product of combustion for organic materials produced by TSS. 43 201247115 4. Conclusions Participating in Zhao Heji shooting three Ec and smoking in four different machines + sighing chemical test can confirm that the Ec & MS no amount will reduce the total ants in the public Ms poison The value, although the BT1 seems to be more, but even if ranked according to the nicotine output, the performance of these ECs, good. The data in this paper supports the use of these Ec as a means of reducing the amount of machine production. The previous data from the EC produced by the TSS method showed that when the smoker made 24 ΜΥΡ, there were fewer biomarkers in contact with the MS toxicant. Although the target RMYp can obtain a low overall toxic machine output, its performance relative to the commercially available comparison group and other published toxic emissions data still requires a large amount of = learning data including contact biomarkers and biological action biomarkers to determine Whether this product is associated with a lower health risk, it is not certain that these RMYPs meet the I〇M definition of pREp. However, the results of the Xianxin study are sufficient to encourage further work, including the research and further application of these RMYP biomarkers and their manufacturing techniques. 5. Prototype Smoking Objects Three prototype RTP smoking articles were made in accordance with the present invention. The cigarette has an extra large size with a filter length of 27 mm and a tobacco rod of 56 mm. The prototype tobacco rod comprises a mixture of flakes, expanded tobacco and non-tobacco sheets or modified tobacco. Conventional rolls are used on paper to form tobacco rods and to ensure a burning rate and a subsequent number of cigarettes. The two prototype filters consist of a CA port end section (length 7 mm), a CA intermediate section containing CR20HD ion exchange resin (length 10 mm), and a spotted end grass section containing 201247115 carbon beads with processed microstructures (long 1Gmm) consists of a three-stage filter. Third, the prototype filter is a two-stage filter consisting of a CA mouth end section (length 15 mm) and a spotted tobacco end section (length 12 mm) containing a high activity polymer. The prototype cigarettes were manufactured to provide ISONFDPM yields of 1 mg (T562m3H671) and 6 mg (F752). Tables n through 13 detail the prototype volume specifications. .. ^ Grass Blend Specification Prototype _ TS62(lmg) H671(lmg) F752(6mg) Flake (%wwb) ___40 12.5 55.0 Expanded Grass a (%wwb) 40 --- — 12.5 Expanded in Grass b (% Wwb) 25.0 modified psyllium c (%wwb) _ 75 non-tobacco tablets d (%wwb) 20 20 added top spices 0.8 0.8 0.8 (AWOLS A) (%wwb) aa is 8.8 shame..^ .

Aurora : 100%火烤種终草。 bSCB : 50%火烤種、5〇〇/0白肋種。 C利用終草摻合物處理加工終草。 非菸草片係具下列規格的TSS:生石灰(78.5%)、Kelvis藻酸鹽 (7,5%)、甘油(I2.5%)和焦糖色素G 5%)(製造商:De丨i_HTL)。 妻12捲終規格 原型 - _* w ’钃、 TS62(lmg) H671(lmg) F752(6mg) 圓周(mm) 24.6 24.6 24.6 45 201247115 總長(mm) 83 83 83 於草棒長度(mm) 56 56 56 捲於紙 CP 50-23 VGM CP 50-23 VGM CP 50-23 VGM 2.0 KCM 2.0 KCM 2.0 KCM 通風孔類型 OML OML OML 通風孔總數 80 80 46 (ST+OML)(°/〇) 密度(毫克/立方公分) 216 247 235 捲菸壓降(mmWG) 97 91 109 捲菸堅實度(%) TBC TBC TBC 焦油(NFDPM)(毫克) 1.0 1.2 5.3 尼古丁(毫克) 0.08 0.10 0.43 一氧化碳(毫克) 1.0 1.0 4.9 表13濾嘴規格 編碼 T562(lmg) H671(lmg) F752(6mg) 濾嘴編碼(Filtrona,,美 SAM SAM SAM 國) 013108-031 013108-031 020608-040 總長度(mm) 27 27 27 口端段長度(mm) 7 7 15 中間段長度(mm) 10 10 - 菸草段長度(mm) 10 10 12 口端段纖維束 單一 CA 單一 CA 單一 CA 中間段纖維束a CA + 20mg CA + 20mg - ⑤ 46 201247115 菸草端段纖維束b 總體濾嘴壓降 (mmWG) CR20 HD CR20 HD b CA + 60mg CA + 60mg CA + 80mg ----— Blticher 石炭 Blticher 碳 Blticher 碳 ~-- 150 -------- 142 114 ----—, PW600043 PW600043 PW600043 化樹脂(製造商:三菱(商品名稱:Diaion 捲紙 a CR20HD = CR20D)。 B1UChei^球形碳珠粒(製造商:AdsorTech.)。 完成兩段或三段丨f嘴的捲紙。 6.煙毒物接觸試驗 此试驗為評估吸煙者體内的接觸毒物生物標記 (BoE) ’其從習用捲终換成根據本發明的減少毒物原型㊉丁巧 捲於。 結合以上詳述技術,製造一個6mg和兩個imgIS〇焦 油出量的RTP ’此如下表14所示。Aurora: 100% fire-boiled grass. bSCB: 50% fire-baked, 5〇〇/0 ribs. C uses the final blend to treat the final grass. Non-tobacco tablets TSS with the following specifications: quicklime (78.5%), Kelvis alginate (7,5%), glycerol (I2.5%) and caramel G 5%) (manufacturer: De丨i_HTL) . Wife 12-volume final specification prototype - _* w '钃, TS62 (lmg) H671 (lmg) F752 (6mg) circumference (mm) 24.6 24.6 24.6 45 201247115 total length (mm) 83 83 83 in the length of the straw (mm) 56 56 56 rolls on paper CP 50-23 VGM CP 50-23 VGM CP 50-23 VGM 2.0 KCM 2.0 KCM 2.0 KCM Vent type OML OML OML Total number of vents 80 80 46 (ST+OML)(°/〇) Density (mg /cubic centimeter) 216 247 235 Cigarette pressure drop (mmWG) 97 91 109 Cigarette firmness (%) TBC TBC TBC tar (NFDPM) (mg) 1.0 1.2 5.3 Nicotine (mg) 0.08 0.10 0.43 Carbon monoxide (mg) 1.0 1.0 4.9 13 filter specification code T562 (lmg) H671 (lmg) F752 (6mg) filter code (Filtrona, US SAM SAM SAM country) 013108-031 013108-031 020608-040 total length (mm) 27 27 27 mouth end segment Length (mm) 7 7 15 Intermediate section length (mm) 10 10 - Tobacco section length (mm) 10 10 12 End section fiber bundle Single CA Single CA Single CA Intermediate section fiber bundle a CA + 20mg CA + 20mg - 5 46 201247115 Tobacco end fiber bundle b Overall filter pressure drop (mmWG) CR20 HD CR20 HD b CA + 60mg CA + 60mg CA + 80m g ----— Blticher Carbon Charcoal Blticher Carbon Blticer Carbon ~-- 150 -------- 142 114 ----—, PW600043 PW600043 PW600043 Resin (Manufacturer: Mitsubishi (Product Name: Diaion Roll Paper a CR20HD = CR20D). B1UChei^Spherical carbon beads (manufacturer: AdsorTech.) Complete two or three stages of roll paper. 6. Tobacco poison contact test This test is to assess the exposure of smokers in smokers. Biomarker (BoE) 'It was replaced from a conventional roll to a poison-reducing prototype according to the present invention. In combination with the above detailed technique, an RTP of 6 mg and two imgIS tar yields was produced. Shown.

UlJ式驗原型產品 產品標識及說 明 務草換合物 菸草濾嘴 ISO*焦油 出量目標 (實際值) HCI# 焦 油出量 (實際值) CC6 以6mg ISO習 用捲菸為基料 100% US 型& 草換合物 ----— 單段: CA 6mg (5.0mg) 24.4mg 47 201247115 的對照組 TSS6 6mg ISO焦油 原型 80% US型菸草 摻合物 20%菸草代替片 兩段: CA +碳 (80mg) 6mg (5_3mg) 20.7mg CC1 以1 mg ISO焦 油市售捲菸為 基料的對照組 100% US型菸 草摻合物 單段: CA lmg (1.2mg) 18.9mg TSS1 1 mg ISO焦油 原型 80% US型菸草 摻合物20%菸 草代替片 三段: CA +碳 (60mg) + 樹脂(20mg) lmg (1-Omg) 17.3mg BT1 具菸草摻合物 改質的1 mg ISO焦油原型 25%維吉尼亞 型菸草摻合物 (未處理) 75%維吉尼亞 型菸草摻合物 (已處理) 三段: CA +碳 (60mg) + 樹脂(20mg) lmg (1.2mg) 17.8mg * ISO定制=煙團容積35毫升、持續時間2秒、間隔時間60 秒、濾嘴通風孔100%打開。 # HCI(Health Canada Intense)定制=煙團容積55毫升、持續時 間2秒、間隔時間30秒、濾嘴通風孔100%阻塞。 ⑤ 48 201247115 參見表15(第15圖)’與習用對照捲菸設計相比,煙化 學顯示毒物有效減少。 如第16圖所示,進行六週單中心、單盲隨機控制交換 研究且伴隨偶爾臨床禁閉。此研究共招募301名健康成人 受試者:100名吸煙者使用6-7mg ISO焦油出量捲菸(分配 到6mg組),151名吸煙者使用焦油出量捲菸(分 配到lmg組)及50名非吸煙者。招募的吸煙者隨機被分配 到其焦油組別的對照或s式驗組,每組約5 〇名。所有吸煙者 抽吸供應對照產品2週,之後進行第14天的基線測量。對 照組吸煙者持續抽吸對照產品再4週,試驗組吸煙者換成 抽吸RTP 4週。在各例中,於第28天(兩週)和第“天(四 週)進行測量。非吸煙者組提供生物標記的背景值指示。 在臨床禁閉的三段(吸煙者)和兩段(非吸煙者)短暫期 間(參見帛16圖)’收集24小時尿液樣本,及分析尿生物標 記接觸量而估計-祕成分接觸量。叫證的lc姻⑽ 方法分析尿生物標記接觸量。 比較RTP㈣學與對照祕時,錢測量純 少(10%-96%),實際量取決於設計和毒物(參見表叫。唯一 種產品(BT1)有較多出量,其產出16%以上的尼古丁和燃 以上的1,3-丁二烯,然此產品在所有其他毒物方面亦有最 大整體減:> ΐ。對應生物標記的方向和相關量級變 分與煙化學變化一致(表15和第17及18圖),但在少數情 況下,煙將隨生物標記增加而減少(TSS1的尼古丁與 NNK),或煙隨生物標記增加減少而増加(Βτι的丁一' 49 201247115 烯)。這些差異的原因不明,但可能涉及分析變異或吸煙者 行為。 第Π圖顯示第2組的生物標記結果,其從對照捲菸 CC6(第14天)換成試驗捲菸TSS6(第41天)。*表示第14天 至第41天的結果統計顯著差異(p^).01)。非吸煙者生物標 記量供作參考。所有非吸煙者量值明顯比第丨4天的量值小。 第18圖顯示從對照捲菸CC1(第14天)換成試驗捲菸 TSS1(第41天)的第4組和從對照捲菸CC1(第14天)換成試 驗捲菸BT1(第41天)的第5組的生物標記結果。 研究發現’換成減少毒物原型捲菸的捲菸吸煙者組平 均有較低的對應生物標記接觸量(BqE),其包括微粒與氣相 毒物的BoE:不同原型產生不同BqE減少量,在—些情況 下,=用七結合技術而定,減少量實質大於50%。通常, 生物^減少大多在換抽兩週後變得明顯。在所有情況 下及煙者組的平均生物標記量較低。 n、主^首度也實在^'煙者從習用捲於換成根據本發明之 /夕毋原型捲於後,能有效減少於草煙毒物的各種BoE。 【圖式簡單說明】 第1圖顯示表2, 第2圖顯示表4, 主要成分出量。 其列出捲菸成分細目。 其列出以不同吸煙機條件測試捲菸的 第3圖顯不表5 ’其Μ摻合金屬麟草特有亞确胺含 201247115 第4圖顯示表6,其列出在Health Canada Intense吸煙 機條件下測量金屬與TSNA的MS出量。 第5A、5B及5C圖顯示表7,其列出在Health Canada Intense吸煙機條件下測量其他煙成分的MS出量。 第6圖顯示表8,其列出在Health Canada Intense吸煙 機條件下測量對照及三段濾嘴EC中羰和混雜揮發性與氣 相煙成分的MS出量。 第7圖顯示表9,其列出在Health Canada Intense吸煙 機條件下測量對照及兩段濾嘴EC中羰和混雜揮發性與氣 相煙成分的MS出量。 第8A及8B圖顯示表10,其列出在ISO吸煙機條件下 的側流煙出量。 第9圖顯示比較EC(1毫克ISO)的HCI機器毒物出量 與公開資料來源的出量。 第10圖顯示比較EC(6毫克ISO)的HCI機器毒物出量 與公開資料來源的出量。 第11圖顯示比較EC出量與公開HCI出量資料的總體 毒物出量(TTY)。 第12圖顯示比較EC出量與公開HCI出量資料的總體 毒物子集出量(TSY)。 第13圖顯示比較EC與公開HCI出量資料的總體正規 化毒物出量(NTT)。 第14圖概要圖示製備高活性聚合物衍生碳的方法。 第15圖圖示表15,其列出與對照捲菸相比,試驗產品 的煙和生物標記變化。 51 201247115 第16圖圖示體内試驗設計。 第17及18圖顯示體内試驗結果。 【主要元件符號說明】 無 ⑤ 52UlJ type prototype product identification and description of the grass compound tobacco filter ISO* tar output target (actual value) HCI# tar output (actual value) CC6 with 6mg ISO custom cigarettes based on 100% US type &; grass compound----- single stage: CA 6mg (5.0mg) 24.4mg 47 201247115 control group TSS6 6mg ISO tar prototype 80% US type tobacco blend 20% tobacco replacement tablets two segments: CA + carbon (80mg) 6mg (5_3mg) 20.7mg CC1 Control group based on 1 mg of ISO tar commercial cigarettes 100% US type tobacco blend single section: CA lmg (1.2mg) 18.9mg TSS1 1 mg ISO tar prototype 80 % US Tobacco Blend 20% Tobacco Replacement Tablets: CA + Carbon (60mg) + Resin (20mg) lmg (1-Omg) 17.3mg BT1 1 mg ISO Tar Prototype with Tobacco Blend Modification 25% Virginia type tobacco blend (untreated) 75% Virginia type tobacco blend (treated) Three stages: CA + carbon (60 mg) + resin (20 mg) lmg (1.2 mg) 17.8 mg * ISO customization = 35 ml volume of cigarette, duration 2 seconds, interval 60 seconds, filter vents 100% open. # HCI(Health Canada Intense) Customized = 55 ml of cigarette volume, 2 seconds duration, 30 seconds interval, 100% blockage of filter vents. 5 48 201247115 See Table 15 (Figure 15). Tobacco chemistry shows an effective reduction in toxicology compared to conventional control cigarette designs. As shown in Figure 16, a six-week, single-center, single-blind, randomized controlled exchange study was conducted with occasional clinical confinement. A total of 301 healthy adult subjects were enrolled in the study: 100 smokers used 6-7 mg ISO tar cigarettes (assigned to the 6 mg group), 151 smokers used tar cigarettes (assigned to the lmg group) and 50 Non-smokers. The recruited smokers were randomly assigned to their tar group control or s test group, each group of about 5 。. All smokers were aspirated to supply control products for 2 weeks, followed by baseline measurements on day 14. The control group smokers continued to aspirate the control product for another 4 weeks, and the test group smokers switched to aspiration RTP for 4 weeks. In each case, measurements were taken on day 28 (two weeks) and on day (weeks). The non-smoker group provided background indications for biomarkers. Three segments (smokers) and two segments (non-smoking) in clinical confinement Smoker) During the short period (see Figure 16) 'Collect 24-hour urine samples, and analyze the amount of urine biomarker exposure to estimate the amount of exposure to the secret ingredient. The lc marriage (10) method for the analysis of urine biomarker exposure. Compare RTP (4) When learning and controlling secrets, the money is measured purely (10%-96%), the actual amount depends on the design and poison (see the table. The only product (BT1) has more output, and it produces more than 16% of nicotine. And the above-mentioned 1,3-butadiene, but this product also has the largest overall reduction in all other toxicants: > ΐ. The direction of the corresponding biomarker and the relevant magnitude change are consistent with the change in smoke chemistry (Table 15 and Figures 17 and 18), but in a few cases, smoke will decrease with increasing biomarkers (nicotine and NNK for TSS1), or smoke will increase with increasing biomarkers (Βτι的丁一' 49 201247115 ene). The reason for the difference is unknown, but may involve analysis Or smoker behavior. The chart shows the biomarker results for Group 2, which was changed from control cigarette CC6 (Day 14) to test cigarette TSS6 (Day 41). * indicates results from Day 14 to Day 41. Significant difference (p^).01). The biomarker amount of non-smokers is for reference. All non-smokers are significantly smaller than the fourth day. Figure 18 shows the control cigarette CC1 (Day 14) Replace the biomarker results of Group 4 of the test cigarette TSS1 (Day 41) with Group 5 from the control cigarette CC1 (Day 14) to the test cigarette BT1 (Day 41). The study found that 'replacement to reduce poisons The cigarette smoker group of the prototype cigarette had an average corresponding biomarker exposure (BqE), which included BoE of particulate and gas phase poisons: different prototypes produced different BqE reductions, and in some cases, = seven combination techniques However, the reduction is substantially greater than 50%. Usually, the reduction in biomass is mostly apparent after two weeks of pumping. In all cases, the average biomarker of the smoker group is lower. n, the main ^ first degree is also true ^ 'The smoker can be effective after switching from the customary volume to the prototype of the 毋 根据 according to the present invention. Less than the BoE poisons of various BoE. [Simple diagram of the diagram] Figure 1 shows Table 2, Figure 2 shows Table 4, the main component output. It lists the cigarette component breakdown. It is listed under different smoking machine conditions. Figure 3 of the cigarette is shown in Table 5 'The Μ Μ 金属 特 特 特 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 2012 Figures 5A, 5B, and 5C show Table 7, which lists the MS yield of other smoke components measured under Health Canada Intense smoking machine conditions. Figure 6 shows Table 8, which shows the MS yields of carbonyl and mixed volatile and particulate smoke constituents in the control and three-stage filter EC under Health Canada Intense smoking machine conditions. Figure 7 shows Table 9, which shows the MS yields of carbonyl and mixed volatile and particulate smoke constituents in the control and two-stage filter EC under Health Canada Intense smoking machine conditions. Figures 8A and 8B show a table 10 listing the amount of sidestream smoke under ISO smoking machine conditions. Figure 9 shows the output of HCI machine toxicants compared to EC (1 mg ISO) and published sources. Figure 10 shows the output of HCI machine toxicants compared to EC (6 mg ISO) and published sources. Figure 11 shows the overall toxic yield (TTY) of the EC yield and published HCI output data. Figure 12 shows the overall toxicant subset (TSY) of the EC yield and published HCI output data. Figure 13 shows the overall normalized toxicant output (NTT) comparing EC and published HCI data. Figure 14 outlines a method of preparing a highly reactive polymer-derived carbon. Figure 15 illustrates Table 15, which lists the changes in smoke and biomarkers of the test product compared to the control cigarette. 51 201247115 Figure 16 shows the in vivo test design. Figures 17 and 18 show the results of in vivo testing. [Main component symbol description] None 5 52

Claims (1)

201247115 七、申請專利範圍: 1,一種吸煙物件,包含下列至少二者: (a) 菸草摻合物,包含具低TSNA及/或金屬含量的一或更多 菸草或菸草等級; (b) 菸草摻合物,其已經處理移除多酚及/或胜肽; (c) 菸草代替片,包含不燃無機填料、黏結劑與氣溶膠 用具; (d)高活性碳’包含聚合物衍生碳材料;以及 (e)胺官能化螯合樹脂。 2.如申凊專利範圍第丨項之吸煙物件,包含可吸煙材料棒, 該可吸煙材料棒包含至多達60%的菸草代替片。 3. 如申請專·圍第2項之吸煙物件,包含可吸煙材料棒, 該:吸煙材料棒包含2〇%的於草代替片和跳的於草。 4. 如前述中請專利範圍中任一項之吸煙物件,其中甘油 來加入該菸草代替片與菸草的掺合物中。 · Μ 5. 如申請^彳範㈣丨項之錢物件,包含可吸煙材料棒, 該可吸,材料棒包含至多達1〇〇%的已處理終草推合物棒 6. 如申請專利範圍第5項之吸煙物件,包 吸煙材料棒一的已處理终草播合物=終 7.如前述f請專利範圍中任—項之吸煙物件 且 的滤嘴,其中口端段包含乙酸纖維素 :厂叫 維素與-胺官能化螯合樹脂,及柊草 二匕:乙酉夂纖 與高活性碳。 含乙酸纖維素 53 201247115 8. 如申請專利範圍第7項之吸煙物件,其中該中間段包含20 毫克的胺官能化螯合樹脂。 9. 如申請專利範圍第7或8項之吸煙物件,其中該菸草端段 包含60毫克的碳。 10. 如申請專利範圍第1至3項中任一項之吸煙物件,包含具 兩區段的濾嘴,其中口端段包含乙酸纖維素,及菸草端段 包含乙酸纖維素與碳。 11. 如申請專利範圍第10項之吸煙物件,其中該菸草端段包 含80毫克的碳。 12. 如申請專利範圍第7至10項中任一項之吸煙物件,其中 該碳係包含聚合物衍生碳材料的高活性碳珠粒。 13. 如申請專利範圍第7至10項中任一項之吸煙物件,其中 該胺官能化螯合樹脂係CR20。 14. 如申請專利範圍第1項之吸煙物件,包含至少一選自(a)、 (b)與(c)者和至少一選自(d)與(e)者。 15. 如申請專利範圍第14項之吸煙物件,包含(c)和⑷。 16. 如前述申請專利範圍中任一項之吸煙物件,具有大幅減少 的所有不欲主流煙成分。 ⑤ 54201247115 VII. Scope of application: 1. A smoking article comprising at least two of the following: (a) Tobacco blends containing one or more tobacco or tobacco grades with low TSNA and/or metal content; (b) Tobacco a blend that has been treated to remove polyphenols and/or peptides; (c) a tobacco substitute sheet comprising a non-combustible inorganic filler, a binder and an aerosol appliance; (d) a highly reactive carbon comprising a polymer-derived carbon material; And (e) an amine functionalized chelating resin. 2. The smoking article of claim 3, comprising a smokable material stick comprising up to 60% of the tobacco substitute sheet. 3. If you apply for the smoking item of section 2, including the smoking material stick, the smoking material stick contains 2% of the grass instead of the piece and the jumping grass. 4. A smoking article according to any of the preceding claims, wherein glycerin is added to the tobacco in place of the blend of the tablet and the tobacco. · Μ 5. If you apply for the money item of the 彳 (4) item, including the smokable material rod, the smokable material rod contains up to 1% of the processed medicinal turf rods. 6. If you apply for a patent Item 5 of the smoking article, the packaged smoking material bar of the treated terminal planting compound = the final 7. The filter of the smoking article of the above-mentioned patent scope, wherein the mouth end segment comprises cellulose acetate The factory is called vitamins and amine functionalized chelating resins, and valerian diterpenoids: acetaminophen and high activated carbon. Cellulose acetate 53 201247115 8. The smoking article of claim 7, wherein the intermediate section comprises 20 mg of an amine functionalized chelating resin. 9. The smoking article of claim 7 or 8, wherein the tobacco end section comprises 60 mg of carbon. 10. A smoking article according to any one of claims 1 to 3, comprising a filter having two sections, wherein the mouth end section comprises cellulose acetate and the tobacco end section comprises cellulose acetate and carbon. 11. The smoking article of claim 10, wherein the tobacco end section comprises 80 mg of carbon. 12. The smoking article of any one of clauses 7 to 10, wherein the carbon is a high activity carbon bead comprising a polymer derived carbon material. 13. The smoking article of any one of clauses 7 to 10, wherein the amine functionalized chelate resin is CR20. 14. A smoking article according to item 1 of the patent application, comprising at least one selected from the group consisting of (a), (b) and (c) and at least one selected from (d) and (e). 15. Smoking articles, including (c) and (4), in the scope of patent application No. 14. 16. A smoking article according to any of the preceding claims, which has a substantially reduced amount of unwanted mainstream smoke constituents. 5 54
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