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| DC 欄位 | 值 | 語言 |
|---|---|---|
| dc.contributor.advisor | 黃耀輝(Yaw-Huei Hwang) | |
| dc.contributor.author | Hui Yeh | en |
| dc.contributor.author | 葉暉 | zh_TW |
| dc.date.accessioned | 2021-06-15T13:36:43Z | - |
| dc.date.available | 2021-02-24 | |
| dc.date.copyright | 2016-02-24 | |
| dc.date.issued | 2016 | |
| dc.date.submitted | 2016-01-27 | |
| dc.identifier.citation | Acharya S, Mehta K, Krishnan S, Rao CV. 2001. A subtoxic interactive toxicity study of ethanol and chromium in male wistar rats. Alcohol (Fayetteville, NY) 23:99-108.
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Environmental Health Perspectives 85:355-359. Yamanaka K, Ohtsubo K, Hasegawa A, Hayashi H, Ohji H, Kanisawa M, et al. 1996. Exposure to dimethylarsinic acid, a main metabolite of inorganic arsenics, strongly promotes tumorigenesis initiated by 4-nitroquinoline 1-oxide in the lungs of mice. Carcinogenesis 17:767-770. Yassine H, Kimzey MJ, Galligan MA, Gandolfi AJ, Stump CS, Lau SS. 2012. Adjusting for urinary creatinine overestimates arsenic concentrations in diabetics. Cardiorenal Medicine 2:26-32. Yuan C, Lu X, Oro N, Wang Z, Xia Y, Wade TJ, et al. 2008. Arsenic speciation analysis in human saliva. Clin Chem 54:163-171. Zaichick V, Tsyb A, Bagirov S. 1995. Neutron activation analysis of saliva: Application in clinical chemistry, environmental and occupational toxicology. Journal of Radioanalytical and Nuclear Chemistry, Articles 195:123-132. Zakharyan R, Wu Y, Bogdan GM, Aposhian HV. 1995. Enzymatic methylation of arsenic compounds: Assay, partial purification, and properties of arsenite methyltransferase and monomethylarsonic acid methyltransferase of rabbit liver. Chemical Research in Toxicology 8:1029-1038. Zschiesche W, Schaller KH, Weltle D. 1992. Exposure to soluble barium compounds: An interventional study in arc welders. International Archives of Occupational and Environmental Health 64:13-23. 許家晴,2004。攝食含有機砷食物後尿中砷物種分佈之情形,臺灣大學職業醫學與工業衛生研究所碩士論文。 | |
| dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/51505 | - |
| dc.description.abstract | 生物偵測是指藉由生物檢體之採樣,分析其中某化學物質或者是其代謝物的濃度,以評估人員的暴露或是健康效應,生物偵測常用的檢體類型包含血液、尿液、頭髮、指甲、唾液等。在重金屬暴露之生物偵測上,通常以血液、尿液為主,也有部分是以頭髮、指甲作為評估工具,僅有少數研究以唾液作為重金屬暴露之生物偵測指標。以砷為例,過去的研究通常以尿中砷濃度作為無機砷暴露之評估工具,然而尿中砷濃度容易受到受試者食用海鮮食品而造成無機砷暴露評估上的干擾,若有一生物偵測方式不受食用海鮮食品之影響,又可以反映出無機砷暴露,對於砷暴露之評估將是一項有力的評估方式。唾液作為生物偵測之工具的優點為採集簡單且非侵入性,受試者提供檢體之意願較高。本研究分析唾液中的多元素以及砷物種濃度,一方面研究唾液中多元素濃度以及尿液中濃度之相關性,並且探討影響唾液中元素濃度之因子,藉此評估唾液是否可作為暴露指標;另一方面則是評估唾液中的砷濃度是否會受到海鮮食品攝取之影響。
本研究分兩部分,第一部分分析34名受試者唾液與尿液中的多種元素以及砷物種,其中17人為台大醫院腎臟科之病患,17人為無泌尿系統相關疾病之受試者,此部分實驗探討:(1)唾液與尿液中之元素濃度之間是否有相關性,(2)比較健康受試者與泌尿系統相關疾病受試者之唾液中金屬元素濃度與砷物種濃度之間是否有差異,(3)藉由問卷調查分析不同的人口學變項是否會影響唾液中多元素以及砷物種之濃度。以感應耦合電漿質譜儀(ICP-MS)分析砷、鋇、鉻、鈷、鎘、鎵、銦、錳、鎳、鉛、鈀、硒、鍶、釩、鎢,並且以高效能液相層析儀串聯感應耦合電漿質譜儀(HPLC-ICP-MS)分析三價無機砷(arsenite)、五價無機砷 (arsenate)、單甲機砷酸(monomethylarsonic acid)、雙甲機砷酸(dimethylarsinic acid)、砷酸甜菜鹼(arsenobetaine)。結果發現,唾液中鎳濃度與尿液中鎳濃度之Spearman相關係數為0.503(p < 0.05),唾液中鎢濃度與尿液中鎢濃度之Spearman相關係數為0.703(p < 0.05),皆達到統計上顯著差異。唾液中的砷、鈷、鉻、錳、鎳、鉛、硒、釩等元素在不同年齡層中平均濃度有顯著差異;目前仍配戴口腔矯正器或假牙之受試者唾液中鉻濃度顯著較從未配戴之受試者高。有泌尿系統相關疾病之受試者,唾液中的五價無機砷濃度顯著較無疾病者高。本研究第二部分則是讓16名健康受試者食用海鮮食品,比較食用前後兩天尿液及唾液中的砷及其物種濃度變化,以評估海鮮攝取是否會對唾液中的砷濃度造成影響。結果顯示,尿中的砷濃度明顯會受到飲食海鮮食品而改變,但是唾液中的砷濃度在食用海鮮食品前後變化不大,表示唾液中砷濃度不受食用海鮮食品之影響。本研究之結果顯示,唾液中的鎢在唾液中的濃度與尿液中的濃度相關性高,表示可能可以作為鎢暴露的生物偵測指標。唾液中的砷濃度不受食用海鮮食品之影響,為避免食用海鮮食品對於尿中砷及砷物種濃度之影響,未來唾液中砷濃度可望作為評估無機砷暴露之工具之一。 | zh_TW |
| dc.description.abstract | Biomonitoring is the measurement of chemicals or their metabolites in body fluids or tissues, such as blood, urine, hairs, nails, and saliva. Blood and urine samples are the most widely accepted matrices for the biomonitoring of trace metal exposure, and there is less research on trace elements in saliva. Collection of saliva is simple and non-invasive, and saliva is much more accessible as compared to other sample mediums. In addition, dietary arsenic from seafood intake would be significant interference for the assessment of exposure to inorganic arsenic using urine arsenic levels as biological marker. Therefore, the purpose of this study was to determine the levels of trace elements in saliva and urine, including arsenic, barium, chromium, cobalt, cadmium, gallium, indium, lead, manganese, nickel, palladium, selenium, strontium, vanadium, and tungsten and arsenic species, i.e., arsenite (AsIII), arsenate (AsV), methylarsonic acid (MMA), dimethylarsinic acid (DMA) and arsenobetaine (AsB), and to evaluate the usability of saliva as biomonitoring medium. Mean while, fluctuation of salivary arsenic species levels after seafood intake was also examined to evaluate the effect of dietary arsenic intake on the inorganic metabolites in saliva.
There are two parts in this study. In the first part, the levels of arsenic species and trace elements were determined in 34 saliva and urine samples, respectively, from 17 healthy volunteers and 17 patients from the Division of Nephrology in National Taiwan University Hospital. The levels of trace elements were determined by inductively coupled plasma mass spectrometry (ICP-MS), and the arsenic species were determined by high performance liquid chromatography with inductively coupled plasma mass spectrometry (HPLC-ICP-MS). There were positive correlations between salivary nickel level and urinary nickel level (rs = 0.503, p < 0.05), and between salivary tungsten level and urinary tungsten level (rs = 0.703, p < 0.05). There were significant differences in the saliva levels of arsenic, chromium, cobalt, lead, manganese, nickel, selenium, and vanadium among various age groups. The mean chromium level in saliva samples of volunteers with fixed orthodontic appliances or dentures was higher than that of volunteers without them. Higher salivary arsenate levels were observed in volunteers with kidney diseases. In the second part of this study, 16 volunteers were asked to eat about 100 g oyster or cuttlefish in one meal, and their saliva and urine samples were collected before and after the seafood intake for the determination of arsenic species levels. Results showed that the levels of arsenic in urine samples increased significantly after the intake of seafood, while there was no difference between arsenic levels in saliva before and after the seafood intake. In conclusion, tungsten in human saliva could be a useful biomarker to assess human exposure to tungsten. So were saliva arsenic species for the evaluation of inorganic arsenic exposure since they would not be affected by seafood arsenic intake. | en |
| dc.description.provenance | Made available in DSpace on 2021-06-15T13:36:43Z (GMT). No. of bitstreams: 1 ntu-105-R02841004-1.pdf: 1296262 bytes, checksum: 80f2a8236181dcd8d4b469bca6209b4a (MD5) Previous issue date: 2016 | en |
| dc.description.tableofcontents | 口試委員會審定書 I
致謝 III 中文摘要 IV ABSTRACT VI 目錄 VIII 表目錄 XI 圖目錄 XII 第一章 前言 1 1-1 研究背景與目的 1 第二章 文獻探討 3 2-1 砷及其化合物的基本介紹 3 2-1-1 環境中的砷 3 2-1-2 砷的人體暴露 4 2-1-3 砷的健康危害 6 2-1-4 砷的代謝及其物種之毒性 6 2-1-5 砷物種的生物偵測 9 2-1-6 砷物種之分析 10 2-2 無機元素基本介紹及其生物偵測 11 2-2-1 鋇(Barium) 11 2-2-2 鎘(Cadmium) 12 2-2-3 鈷(Cobalt) 14 2-2-4 鉻(Chromium) 15 2-2-5 鎵(Gallium) 16 2-2-6 銦(Indium) 17 2-2-7 錳(Manganese) 18 2-2-8 鎳(Nickel) 19 2-2-9 鉛(Lead) 20 2-2-10 鍶(Strontium) 21 2-2-11 釩(Vanadium) 22 2-2-12 鎢(Tungsten) 22 2-3 唾液基本介紹與唾液中的金屬元素 23 2-3-1 唾液與生物偵測 23 2-3-2 唾液採樣 25 2-3-3 唾液中的元素 26 2-4 儀器分析原理介紹 29 2-4-1 感應耦合電漿質譜儀(ICP-MS) 29 2-4-2 高效能液相層析儀串聯感應耦合電漿質譜儀(HPLC-ICP-MS) 30 第三章 材料與方法 33 3-1 研究設計 33 3-1-1 唾液及尿液中多元素與砷物種之分佈研究 33 3-1-2 攝食海鮮後唾液與尿液中砷物種分佈特性比較 34 3-2 樣本採集 34 3-2-1 尿液採集方法 34 3-2-2 唾液採集方法 35 3-2-3 海鮮樣本採集 35 3-3 儀器設備 36 3-4 試藥與試劑 36 3-5 樣本前處理 38 3-5-1 尿液 38 3-5-2 唾液 38 3-5-3 海鮮樣本 39 3-6 砷物種分析 40 3-6-1 AsIII、AsV、DMA、MMA之分析 40 3-6-2 AsB之分析 41 3-6-3 上機樣本配置 42 3-7 多元素分析 42 3-7-1 檢量線配置 42 3-7-2 分析儀器條件 43 3-7-3 上機樣本配置 43 3-8 分析品質保證與品質管制 43 第四章 研究結果 50 4-1 唾液與尿液中多元素濃度分析 50 4-1-1 受試者基本變項資料 50 4-1-2 尿液與唾液中多元素濃度分佈 54 4-1-3 唾液與尿液中砷物種濃度分布 56 4-2 海鮮飲食控制實驗受試者尿中、唾液中砷物種分析 85 4-2-1 海鮮中砷物種濃度 85 4-2-2 受試者基本變項與海鮮攝取情況 85 4-2-3 受試者尿中及唾液中砷物種濃度分佈與攝食海鮮之關係 86 4-2-4 受試者攝食海鮮後之天數及各受試者基本變項與尿中及唾液中砷物種濃度 之關係 87 第五章 討論 92 5-1 唾液中元素濃度作為重金屬暴露指標之評估 92 5-2 唾液中金屬元素濃度與各變項之關係 95 5-3 尿液中金屬元素濃度與泌尿系統相關疾病之關係 98 5-4 唾液與尿液中砷物種與各變項之關係 103 5-5 海鮮攝取對唾液以及尿液中砷物種影響 105 第六章 結論 107 參考文獻 108 附件一、暴露調查問卷 122 | |
| dc.language.iso | zh-TW | |
| dc.subject | 砷物種 | zh_TW |
| dc.subject | 砷 | zh_TW |
| dc.subject | 唾液 | zh_TW |
| dc.subject | 感應耦合電漿質譜儀 | zh_TW |
| dc.subject | 液相層析儀串聯感應耦合電漿質譜儀 | zh_TW |
| dc.subject | 唾液 | zh_TW |
| dc.subject | 砷 | zh_TW |
| dc.subject | 砷物種 | zh_TW |
| dc.subject | 重金屬 | zh_TW |
| dc.subject | 生物偵測 | zh_TW |
| dc.subject | 感應耦合電漿質譜儀 | zh_TW |
| dc.subject | 生物偵測 | zh_TW |
| dc.subject | 液相層析儀串聯感應耦合電漿質譜儀 | zh_TW |
| dc.subject | 重金屬 | zh_TW |
| dc.subject | biomonitoring | en |
| dc.subject | saliva | en |
| dc.subject | arsenic | en |
| dc.subject | arsenic speciation | en |
| dc.subject | heavy metals | en |
| dc.subject | ICP-MS | en |
| dc.subject | HPLC-ICP-MS | en |
| dc.subject | saliva | en |
| dc.subject | arsenic | en |
| dc.subject | arsenic speciation | en |
| dc.subject | heavy metals | en |
| dc.subject | biomonitoring | en |
| dc.subject | ICP-MS | en |
| dc.subject | HPLC-ICP-MS | en |
| dc.title | 唾液中砷物種與多種金屬元素作為無機砷與重金屬暴露指標可行性評估 | zh_TW |
| dc.title | Evaluation of the Use of Arsenic Species and Heavy Metals in Saliva as Biological Marker of Inorganic Arsenic and Heavy Metals Exposure | en |
| dc.type | Thesis | |
| dc.date.schoolyear | 104-1 | |
| dc.description.degree | 碩士 | |
| dc.contributor.oralexamcommittee | 毛義方(I-Fang Mao),王碩盟(Shuo-Mong Wang) | |
| dc.subject.keyword | 唾液,砷,砷物種,重金屬,生物偵測,感應耦合電漿質譜儀,液相層析儀串聯感應耦合電漿質譜儀, | zh_TW |
| dc.subject.keyword | saliva,arsenic,arsenic speciation,heavy metals,biomonitoring,ICP-MS,HPLC-ICP-MS, | en |
| dc.relation.page | 129 | |
| dc.rights.note | 有償授權 | |
| dc.date.accepted | 2016-01-27 | |
| dc.contributor.author-college | 公共衛生學院 | zh_TW |
| dc.contributor.author-dept | 職業醫學與工業衛生研究所 | zh_TW |
| 顯示於系所單位: | 職業醫學與工業衛生研究所 | |
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