999精品在线视频,手机成人午夜在线视频,久久不卡国产精品无码,中日无码在线观看,成人av手机在线观看,日韩精品亚洲一区中文字幕,亚洲av无码人妻,四虎国产在线观看 ?

液相色譜串聯質譜法同時檢測DNA中3_甲基腺嘌呤和3_乙基腺嘌呤

2014-09-02 21:25:54田永峰等
分析化學 2014年8期
關鍵詞:煙氣方法

田永峰等

摘要利用陽離子交換固相萃取柱(Waters Oasis MCX)富集凈化DNA樣品,建立了液相色譜串聯質譜(LCMS/MS)同時檢測DNA中3甲基腺嘌呤(N3MeA)和3乙基腺嘌呤(N3EtA)的方法。采用氘代3甲基腺嘌呤(d3N3MeA)和氘代3乙基腺嘌呤(d5N3EtA)為內標; 進樣量3 μL,分析時間為13 min;親水相互作用色譜柱(Waters XBridge HILIC)進行液相分離,流動相為10 mmol/L甲酸銨乙腈溶液(5∶95, V/V, pH=4.0),流速250 μL/min;質譜條件:電噴霧離子源,多反應監測正離子掃描方式;電噴霧電壓:5500 V, 霧化氣: 369 Pa, 氣簾氣:185 Pa, 電離溫度: 400 ℃,駐留時間: 40 ms。本方法對N3MeA和N3EtA的檢出限分別為0.043和0.007 μg/L,方法回收率為87.8%~103.0%。采用本方法檢測了卷煙煙氣粒相物暴露的DNA中N3MeA和N3EtA含量。結果表明,卷煙煙氣粒相物暴露后的小牛胸腺DNA中3甲基腺嘌呤和3乙基腺嘌呤可被本方法定量檢出。1引言

卷煙煙氣中包含超過5000種化學物質\[1,2\],其中包含致突變并可導致DNA發生烷基化損傷的物質\[3\]。這些物質可與DNA反應形成烷化類的DNA加合物,已經成為多學科的研究熱點\[4~7\]。煙氣中致癌性的烷化試劑與DNA反應的主要位點是鳥嘌呤的N7位和腺嘌呤的N3位,DNA反應后形成7烷化鳥嘌呤和3烷化腺嘌呤\[8,9\]。3烷化腺嘌呤中比較重要的是3甲基腺嘌呤(N3methyladenine,N3MeA)\[10\]、和3乙基腺嘌呤(N3ethyladenine,N3EtA)\[8\],其結構式見圖1。3甲基腺嘌呤在3烷化腺嘌呤中突變性最強,并且具有基因毒性,3乙基腺嘌呤雖然不具有基因毒性,但是在經體內烷基糖基酶的修復后會在DNA中產生脫嘌呤的位點,這些位點被認為是引起基因突變并導致癌癥的主要因素\[11~16\]。因此,DNA中的3甲基腺嘌呤,3乙基腺嘌呤被認為是卷煙煙氣接觸后DNA發生烷基化損傷的標志物\[17,18\]。準確測定DNA中3甲基腺嘌呤和3乙基腺嘌呤,可用于評估DNA受到的破壞程度及可能的致癌風險\[19\]。

[TS(]圖13甲基腺嘌呤和3乙基腺嘌呤結構式

Fig.1Structures of N3methyladenine (N3MeA) and N3ethyladenine (N3EtA) [HT5][TS)]

目前,DNA中3烷化腺嘌呤的檢測方法有氣相色譜質譜法(GCMS)\[8\],該方法前處理比較繁瑣,需要化學衍生化,并且靈敏度低和專一性不強;酶聯免疫法(ELISA)解決了3烷化腺嘌呤檢測中的專一性問題,但是操作過程繁瑣,結果穩定性較差\[20\]。液相色譜串聯質譜技術因其具有靈敏度高、選擇性好、操作簡便、分析結果穩定可靠的特點,成為DNA加合物研究中的理想方法\[21,22\]。Hu 等首次報導了一種在線固相萃取結合液相色譜串聯質譜同時分析DNA中7甲基鳥嘌呤、3甲基腺嘌呤和O6甲基鳥嘌呤的方法\[23\],該方法檢測7甲基鳥嘌呤、3甲基腺嘌呤和O6甲基鳥嘌呤的運行時間為12min。目前,同時檢測DNA中3甲基腺嘌呤和3乙基腺嘌呤的液相色譜串聯質譜方法還未見報道。

本實驗建立了一種同時測定DNA中3甲基腺嘌呤、3乙基腺嘌呤的液相色譜串聯質譜方法。本方法靈敏度高,穩定性好。利用本方法研究了卷煙煙氣粒相物暴露后,DNA中3甲基腺嘌呤和3乙基腺嘌呤的含量。本方法可用于臨床上評估烷基化試劑暴露后DNA的損傷程度。

2實驗部分

2.1儀器、試劑與材料

1200快速液相色譜儀(美國安捷倫公司)配備G1367D自動進樣器、G1312B二元溶劑泵、G1316B柱溫箱; API 5500 三重四級桿串聯質譜儀(美國加州應用生物系統公司),配備電噴霧電離源(ESI); 數據采集與處理在Analyst 1.5.1軟件上實現。RH20吸煙機(德國伯格瓦特公司)。

氘代3甲基腺嘌呤(d3N3MeA)、氘代3乙基腺嘌呤(d5N3EtA)、3甲基腺嘌呤、3乙基腺嘌呤(純度≥98%,加拿大Toronto Research Chemical公司); 甲醇、乙腈、氨水、乙酸乙酯和甲酸銨(美國TEDIA有限公司),DMSO(上海安普公司),所有的試劑均為色譜純,實驗中所用的水為超純水。OASIS MCX 6cc固相萃取小柱(500 mg,6 mL,Waters公司)。3R4F標準參比卷煙購自美國肯塔基大學。

2.2.3標準工作溶液的配制分別準確稱10 mg的3甲基腺嘌呤、3乙基腺嘌呤、氘代3甲基腺嘌呤和氘代3乙基腺嘌呤固體于5個10 mL容量瓶中,用乙腈定容,分別得到1 g/L的3甲基腺嘌呤、3乙基腺嘌呤、氘代3甲基腺嘌呤和氘代3乙基腺嘌呤儲備液。然后用儲備液稀釋配制不同濃度的標準溶液和工作溶液。

3結果和討論

3.1質譜條件的選擇

用蠕動泵以10 μL/min的流速連續注射,分別將50 μg/L的3甲基腺嘌呤、3乙基腺嘌呤、氘代3甲基腺嘌呤和氘代3乙基腺嘌呤標準溶液注入ESI離子源中,在正離子模式下進行一級質譜掃描,得到相應的準分子離子峰\[M+H\]+,然后對準分子離子峰進行子離子掃描,得到碎片離子信息。選取豐度較強、干擾較小的作為定量離子對。為了達到更高的靈敏度,對碰撞能量、去簇電壓等參數進行了優化。在多反應監測掃描模式下,3甲基腺嘌呤優化結果為定量離子對m/z 150/123,定性離子對為m/z 150/108,內標離子對為m/z 153/126; 3乙基腺嘌呤優化結果為:定量離子對m/z 164/136,定性離子對為m/z 164/119,內標離子對為m/z 168/137。

3.3方法學考察

分別吸取0.1,0.2,0.5,1,2,5和10 μg/L 的3乙基腺嘌呤,1,2,5,10,20和40 μg/L的3甲基腺嘌呤標準溶液各3 μL,注入LCMS/MS系統進行分離分析。3甲基腺嘌呤和3乙基腺嘌呤的線性回歸方程分別為y=0.25x+0.0238和y=0.0145x-0.00135 (y為峰面積,x為濃度),線性良好,相關系數r均大于 0.999。利用加標稀釋得到方法的檢出限,3倍信噪比對應的濃度為檢出限,3甲基腺嘌呤和3乙基腺嘌呤的檢出限分別為0.043 和0.007 μg/L。采用樣本加標的方法獲得方法回收率,總共選取了3個添加水平,每個添加水平重復測定4次,得到方法的回收率和重復性,結果見表1。3甲基腺嘌呤和3乙基腺嘌呤的回收率分別為88.0%~102.3%和98.0%~102.0%,方法精密度小于10%,證明方法的準確性和重復性結果較好。

3.4方法應用

使用本方法對卷煙煙氣暴露的DNA中3甲基腺嘌呤和3乙基腺嘌呤進行分析,結果表明,3甲基腺嘌呤含量為1.17~3.78μg/L, 未檢出3乙基腺嘌呤。 由此可見,本方法對DNA樣本檢測靈敏度高,選擇性好,適用于卷煙煙氣暴露的DNA烷基化損傷研究以及環境中烷基化試劑對DNA暴露后的3甲基腺嘌呤、3乙基腺嘌呤的生物監測。

3Hu C W, Liu H H, Li Y J, Chao M R. Chem. Res.Toxicol., 2012, 25(2): 462-470

4Swenberg J A, Dyroff M C, Bedell M A, Popp J A, Huh N, Kirstein U, Rajewsky M F. Proc. Natl. Acad. Sci., 1984, 81(6): 1692-1695

5Scherer E, Timmer A P, Emmelot P. Cancer. Lett., 1980, 10(1): 1-6

6Kopplin A, Eberleadamkiewicz G, Glüsenkamp K H, Nehls P, Kirstein U. Carcinogenesis., 1995, 16(11): 2637-2641

7Singer B. Nature., 1976, 264(5584): 333-339

8Prevost V, Shuker D E G. Chem. Res. Toxicol., 1996, 9(2): 439-444

9Chao M R, Wang C J, Chang L W, Hu C W. Carcinogenesis., 2005, 27(1): 146-151

10Hu C W, Lin B H, Chao M R. Int. J. Mass. Spectrom., 2011, 304(23): 68-73

11Beranek D T. Mutat. Res., 1990, 231(1): 11-30

12Shuker D E G, Prevost V, Friesen M D, Eberle G, Rajewsky M F, Bartsch H. Environ. Health. Perspect., 1993, 99: 33-37

13Hecht S S. Mutat. Res., 1998, 424(12): 127-142

14Caldwell W S, Greene J M, Plowchalk D R, DeBethizy J D. Chem. Res. Toxicol., 1991, 4(5): 513-516

15Tricker A R, Ditrich C, Preussmann R. Carcinogenesis., 1991, 12(2): 257-261

16Hoffmann D, Brunnemann K D, Prokopczyk B, Djordjevic M V. J. Toxicol. Environ. Health., 1994, 41(1): 1-52

17Carmella S G, Borukhova A, Akerkar S A, Hecht S S. Cancer. Epidemiol. Biomarkers. Prev., 1997, 6(2): 112-120

18Hecht S S. Mutat. Res., 1999, 424(12): 127-142

19Vineis P, Perera F. Int. J. Cancer., 2000, 88(3): 325-328

20Pan J, Awoyemi B, Xuan Z, Vohra P, Wang H T, Dyba M, Greenspan E, Fu Y, Creswell K, Zhang L, Berry D, Tang M S, Chung F L. Chem. Res. Toxicol., 2012, 25(12): 2788-2795

21Feng S, Roethig H J, Liang Q, Kinser R, Jin Y, Scherer G, Urban M, Engl J, Riedel K . Biomarkers., 2006, 11(1): 28-52

22Hu C W, Chao R M. Chem. Res. Toxicol., 2012, 25(11): 2386-2392

23Hu C W, Chen C M, Ho H H, Chao M R. Anal. Bioanal. Chem., 2012, 402(3): 1199-1208

24Chen H, Lin C, Jiang X Y, Pang Y Q, Tang G L, Hou H W, Jiang J H, Hu Q Y. Food. Chem. Toxicol., 2012, 50(3): 612-618

AbstractA liquid chromatographytandem mass spectrometry (LCMSMS) method has been developed for the simultaneous determination of N3methyladenine (N3MeA) and N3ethyladenine (N3EtA) in calf thymus DNA. The DNA samples has been purified and enriched by cation exchange cartridge (Waters Oasis MCX). d3N3MeA and d5N3EtA were used as isotope internal standard. The DNA samples were injected with autosampler. The injected volume was 3 μL and analysis time was 13 min. The sample separation was carried out on hydrophilic interaction chromatograph (Waters XBridge HILIC) with 10 mmol/L ammonium formateacetonitrile (5∶92, V/V, pH=4.0) as mobile phase. The flow rate was set at 250 μL/min. Mass spectrometry was performed by electrospray ionization (ESI) with multireactions monitoring (MRM). The optimized operation conditions of MS were as follows: nebulizer gas 369 Pa; curtain gas 185 Pa, turbo ionspray temperature 400 ℃, ionspray voltage 5500 V, dwell time 40 ms. The limits of detection were 0.043 and 0.007 μg/L for N3MeA and N3EtA, respectively. The recoveries were between 87.8% and 103.0% for N3MeA and N3EtA. This method was successfully applied to the determination of N3MeA and N3EtA in calf thymus DNA by cigarette smoke condensate (CSC) exposure. This method is appropriate for routine analysis and accurate quantification of N3MeA and N3EtA by CSC exposure.

KeywordsN3Methyladenine; N3Ethyladenine; Liquid chromatographytandem mass spectrometry; Deoxyribonucleic acid

24Chen H, Lin C, Jiang X Y, Pang Y Q, Tang G L, Hou H W, Jiang J H, Hu Q Y. Food. Chem. Toxicol., 2012, 50(3): 612-618

AbstractA liquid chromatographytandem mass spectrometry (LCMSMS) method has been developed for the simultaneous determination of N3methyladenine (N3MeA) and N3ethyladenine (N3EtA) in calf thymus DNA. The DNA samples has been purified and enriched by cation exchange cartridge (Waters Oasis MCX). d3N3MeA and d5N3EtA were used as isotope internal standard. The DNA samples were injected with autosampler. The injected volume was 3 μL and analysis time was 13 min. The sample separation was carried out on hydrophilic interaction chromatograph (Waters XBridge HILIC) with 10 mmol/L ammonium formateacetonitrile (5∶92, V/V, pH=4.0) as mobile phase. The flow rate was set at 250 μL/min. Mass spectrometry was performed by electrospray ionization (ESI) with multireactions monitoring (MRM). The optimized operation conditions of MS were as follows: nebulizer gas 369 Pa; curtain gas 185 Pa, turbo ionspray temperature 400 ℃, ionspray voltage 5500 V, dwell time 40 ms. The limits of detection were 0.043 and 0.007 μg/L for N3MeA and N3EtA, respectively. The recoveries were between 87.8% and 103.0% for N3MeA and N3EtA. This method was successfully applied to the determination of N3MeA and N3EtA in calf thymus DNA by cigarette smoke condensate (CSC) exposure. This method is appropriate for routine analysis and accurate quantification of N3MeA and N3EtA by CSC exposure.

KeywordsN3Methyladenine; N3Ethyladenine; Liquid chromatographytandem mass spectrometry; Deoxyribonucleic acid

24Chen H, Lin C, Jiang X Y, Pang Y Q, Tang G L, Hou H W, Jiang J H, Hu Q Y. Food. Chem. Toxicol., 2012, 50(3): 612-618

AbstractA liquid chromatographytandem mass spectrometry (LCMSMS) method has been developed for the simultaneous determination of N3methyladenine (N3MeA) and N3ethyladenine (N3EtA) in calf thymus DNA. The DNA samples has been purified and enriched by cation exchange cartridge (Waters Oasis MCX). d3N3MeA and d5N3EtA were used as isotope internal standard. The DNA samples were injected with autosampler. The injected volume was 3 μL and analysis time was 13 min. The sample separation was carried out on hydrophilic interaction chromatograph (Waters XBridge HILIC) with 10 mmol/L ammonium formateacetonitrile (5∶92, V/V, pH=4.0) as mobile phase. The flow rate was set at 250 μL/min. Mass spectrometry was performed by electrospray ionization (ESI) with multireactions monitoring (MRM). The optimized operation conditions of MS were as follows: nebulizer gas 369 Pa; curtain gas 185 Pa, turbo ionspray temperature 400 ℃, ionspray voltage 5500 V, dwell time 40 ms. The limits of detection were 0.043 and 0.007 μg/L for N3MeA and N3EtA, respectively. The recoveries were between 87.8% and 103.0% for N3MeA and N3EtA. This method was successfully applied to the determination of N3MeA and N3EtA in calf thymus DNA by cigarette smoke condensate (CSC) exposure. This method is appropriate for routine analysis and accurate quantification of N3MeA and N3EtA by CSC exposure.

KeywordsN3Methyladenine; N3Ethyladenine; Liquid chromatographytandem mass spectrometry; Deoxyribonucleic acid

猜你喜歡
煙氣方法
固體吸附劑脫除煙氣中SOx/NOx的研究進展
化工管理(2022年13期)2022-12-02 09:21:52
學習方法
煙氣爐在干熄焦溫風干燥中的應用
山東冶金(2019年2期)2019-05-11 09:12:16
基于參數自整定模糊PID的SCR煙氣脫硝控制
測控技術(2018年2期)2018-12-09 09:00:52
用對方法才能瘦
Coco薇(2016年2期)2016-03-22 02:42:52
燒結煙氣脫硫工藝技術分析
基于非分散紫外吸收法的便攜式煙氣分析儀在煙氣二氧化硫監測中的應用研究
四大方法 教你不再“坐以待病”!
Coco薇(2015年1期)2015-08-13 02:47:34
賺錢方法
捕魚
主站蜘蛛池模板: 久久精品国产在热久久2019| 国产呦精品一区二区三区下载| 久久精品国产精品青草app| 无码日韩人妻精品久久蜜桃| 欧美亚洲激情| 国产精品久久久久久久伊一| 日韩毛片免费观看| 国产欧美亚洲精品第3页在线| 成人午夜免费视频| 91精品国产综合久久香蕉922| 亚洲美女久久| 亚洲色图欧美视频| 欧美另类一区| 日本精品αv中文字幕| 91亚洲精品国产自在现线| 19国产精品麻豆免费观看| 久久久久亚洲AV成人网站软件| 午夜国产精品视频| 91蜜芽尤物福利在线观看| 色网在线视频| 青青操国产视频| 久久精品人妻中文系列| 国产理论精品| 激情无码视频在线看| 伊人查蕉在线观看国产精品| 亚洲成aⅴ人片在线影院八| 一级毛片不卡片免费观看| 亚洲永久色| 日韩欧美国产综合| 国产sm重味一区二区三区| 九九九久久国产精品| 国产成人午夜福利免费无码r| 久久久精品无码一二三区| 不卡无码网| 色综合中文| 综合色亚洲| 日韩国产黄色网站| 再看日本中文字幕在线观看| 国产h视频免费观看| 欧美69视频在线| 在线播放国产99re| 日韩欧美91| 四虎成人精品| 亚洲黄色激情网站| 日韩成人免费网站| 女人18毛片一级毛片在线 | 欧美亚洲欧美区| 中文字幕在线看视频一区二区三区| 久草网视频在线| 亚洲欧美日韩另类在线一| AV色爱天堂网| 国产幂在线无码精品| 亚洲第一区在线| 都市激情亚洲综合久久| 久久精品无码一区二区国产区 | 中文字幕免费视频| 熟妇丰满人妻| 毛片久久久| 日韩欧美国产另类| 青青草一区| 五月婷婷精品| 97超级碰碰碰碰精品| a毛片免费观看| 无码一区二区三区视频在线播放| 99在线小视频| 日本午夜三级| 国产在线精彩视频二区| 国模极品一区二区三区| 亚洲娇小与黑人巨大交| 喷潮白浆直流在线播放| 波多野结衣一区二区三区四区视频| 国产视频久久久久| 久久国产拍爱| 2020精品极品国产色在线观看| 日韩在线观看网站| 国产真实乱人视频| 人妻无码中文字幕一区二区三区| 欧美在线黄| 亚洲国产成人麻豆精品| 亚洲天堂久久久| 在线不卡免费视频| 久操中文在线|