“ 二噁英”污染与人类健康

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“ 二二二”二二二二二二二 二二二 Ph.D. 二二二二二二二二二二 2011.11.4 E-mail: [email protected] 二二6875 9982 QQ 1520357237

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“ 二噁英”污染与人类健康. 袁占鹏 Ph.D. 武汉大学公共卫生学院 2011.11.4 E-mail: [email protected] 电话: 6875 9982 ; QQ : 1520357237. 目的. 以“二噁英”为例了解一类(种)污染物从来源到公共卫生的系统考量. 内容. “ 二噁英”是什么? 来源 对环境的污染与在环境中的变迁 暴露途径 代谢与分布 毒性及其机制 公共卫生考量 — 健康危害与对策. “ 二噁英”. 是二噁英和二噁英样物质的统称 Polychlorinated dibenzodioxins, PCDDs - PowerPoint PPT Presentation

TRANSCRIPT

Page 1: “ 二噁英”污染与人类健康

“ 二噁英”污染与人类健康

袁占鹏 Ph.D.

武汉大学公共卫生学院2011.11.4

E-mail: [email protected]电话: 6875 9982 ; QQ : 1520357237

Page 2: “ 二噁英”污染与人类健康

目的• 以“二噁英”为例了解一类(种)污染物

从来源到公共卫生的系统考量

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• “ 二噁英”是什么?• 来源• 对环境的污染与在环境中的变迁• 暴露途径• 代谢与分布• 毒性及其机制• 公共卫生考量 — 健康危害与对策

内容

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“ 二噁英”• 是二噁英和二噁英样物质的统称

– Polychlorinated dibenzodioxins, PCDDs– Polychlorinated dibenzofurans, PCDFs– Polychlorinated biphenyls, PCBs

• 2,3,7,8-tetrachlorodibenzo-p-dioxin– 2,3,7,8-TCDD ,常简称 TCDD 或 dioxin– 是“二噁英”类物质的典型物– 俗称二噁英

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TCDD

Dibenzo-p-dioxin

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PCDDs

• Chlorine atoms are attached to this structure at any of 8 different places on the molecule– At positions 1–4 and 6–9– There are 75 PCDD congeners

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PCDFs (呋喃)

• Polychlorinated dibenzofurans

– 2,3,7,8-tetrachlorodibenzofuran

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PCBs (多氯联苯)

• Theoretically 209 different PCB congeners are possible, although only about 130 are found in commercial PCB mixtures

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小结• HAHs – halogenated aryl hydrocarbons

(卤代芳香烃)– PCDD/Fs, PCBs

Note: 卤代芳香烃– Chlorine ( 氯 ) and Bromide ( 溴 )

• Along with Polycyclic aryl hydrocarbons ( PAHs, 多环芳香烃)

• Form aryl hydrocarbons (AHs) family

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10

The term dioxin or dioxins is used almost exclusively to refer to compounds from the above groups which demonstrate the same specific toxic mode of action associated with 2,3,7,8-TCDD.

Incidents of contamination with PCBs are often reported as Dioxin Affair since it is this toxic characteristic which is of most public and regulatory concern.

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“ 二噁英”的理化特性• 高挥发性• 高脂溶性• 高绝缘性• 高(化学)稳定性

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Dioxins and dioxin-like compounds (DLC) are by-products of various industrial processes, except for occasional purposeful production, and are commonly regarded as highly toxic compounds that are also called persistent organic pollutants (POPs).

来源

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• 自然过程形成• 人为产生

– 商品– 工业活动的副产品

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PCDD/Fs 的历史• 工业化前低剂量“二噁英”即存在于环境

中– 自然燃烧– 地质过程:火山爆发等

• 最早产生副产品“二噁英”的工业活动– 1848 年德国 Leblanc Process (卤碱生产)

• 最早有意合成是在 1872 年

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PCBs 的历史• 1930 年代首次合成• 1946 年 Monsanto 最早开始商业合成

– 利用其绝缘性、高稳定性和良好的导热性– 变压器、电容器散热

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自然过程形成

• 深林火灾– PAHs

• BaP

– HAHs• dioxin

• 火山爆发– HAHs

• Dioxins/Furans, PCBs

– PAHs

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工业活动

• 卤碱工业 Leblanc Process– HAHs

• 造纸业– 氯气用于纸浆漂白

• Dioxins (TCDD), Furans, PCBs, etc.

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工业活动(续)• 废物焚烧• 商业合成

– PCBs, Herbicides (Agent Orange)

• 塑料工业– PVC

• 冶金业– HAHs

• Dioxins, furans, and PCBs

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Major Sources

According to the most recent US EPA data• Combustion sources

– municipal waste incinerators

• Metal smelting• Refining and process sources• Chemical manufacturing sources • Natural sources • Environmental reservoirs

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Concentration profile of PCDD in a 2001 sediment core from Esthwaite Water, Cumbria, UK

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“ 二噁英”在环境中的变迁

影响因素• 来源性质

– 热过程– 常温过程

• 物理不稳定性– 易于光裂解 (photolytic)

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“ 二噁英”的环境变迁 (1) 热过程

• 高稳定性和挥发性– 释放到大气中– 随大气运动扩散

• 常附着在有机颗粒上• 随雨、雪沉降地表

– 在土壤里浓度高– 空气中次之– 但因其化学稳定而不易代谢,且由于高脂溶性

而在动物脂肪组织中富集而浓度最高

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“ 二噁英”在大气中的分布与沉降

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“ 二噁英”的环境变迁 (2) 常温过程

• 随工业废物(水)进入环境– 流经的土壤

• 附着在颗粒有机腐质上– 环境生物

• 沉降到水底– 淤泥 (sediments)

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暴露途径

• 呼吸暴露– 汽车尾气

• 食物暴露– 一般人群– 特殊人群暴露—哺乳

• 事故性暴露• 废物场暴露

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食物暴露

• The major sources of human exposure (96%) are– Animal fats found in meats

– Full fat dairy products – Fatty fish (herring, mackerel, salmon,

sardines, trout, tuna)

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空气暴露

• Breathing incineration gases released from medical, municipal, and hazardous waste incinerators

• Breathing gases released by industrial processes from paper mills, cement kilns, and metal smelters

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职业暴露

• People who perform the following types of work can be exposed to dioxins– Production and handling of certain chlorinated phenols

(such as 2,4,5-trichlorophenol or pentachlorophenol [PCP]) – Production or handling of chlorinated pesticides, such as 2-

4-dichlorophenoxyacetic acid (2,4-D) and other herbicides – Chlorinated pesticide application – Pressure treatment of wood with PCP and handling of PCP-

treated wood – Production of chlorinated paper at pulp and paper mills – Operation of municipal solid waste or hazardous waste

incinerators – Hazardous waste clean-up operations

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其它暴露

• 事故性暴露 (accidental exposure)– Seveso, Italy (dioxin, 1976)–台湾食用油污染 (PCBs, 1960s)

• 废物场暴露• 婴儿哺乳

– Children are passed substantial body burdens by their mothers, so breast-feeding increases the child's body burden

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分布、代谢与排泄

• 代谢–微不足道

• 分布– 脂肪成分:肝及其它脂肪组织

• 排泄–缓慢

• The estimated half-life for highly chlorinated dioxins (4-8 chlorine atoms) in humans ranges from 7.8 to 132 years

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“ 二噁英”毒性

• Dioxins refer to such a broad class of compounds that vary widely in toxicity– the concept of toxic equivalent (TEQ) has been de

veloped to facilitate risk assessment and regulatory control.

– Toxic equivalent factors (TEFs) exist for selected congeners of dioxins, furans and PCBs

– The reference congener is the most toxic dioxin 2,3,7,8-TCDD which per definition has a TEF of one

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• 急性毒性– 消化系统脏器损伤、皮肤损伤等– 免疫毒性、神经毒性(行为变化)

• 慢性毒性– 消瘦症 (wasting syndrome)– 发育毒性 (developmental toxicity)– 生殖毒性 (reproductive toxicity – teratology)– 肿瘤发生 (carcinogenesis)– 免疫毒性 (immunotoxicity, immunological tox.)– 神经毒性 (neurotoxicity, neurological tox.)

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AH 毒性机制

• 绝大多数 AHs 的毒性(如果不是全部)是通过 AH 的受体 (AhR, Aryl Hydrocarbon Receptor) 介导的 (Hankinson, 1995)

• 问题–许多毒性得不到满意的解释

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AhR信号通道

XRE promoter gene (CYP1A1)

Translation

Increased expression CYP1A1 protein

Increased expression of other gene products

+

AhR/Arnt heterodimer

mRNA

IC

+

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AhR 的功能

• 动物感测细胞外信号和环境压力的一员– PAS (Per-AhR/Arnt-Sim)家族

• Per – circadian• Arnt – AhR• Sim – Drosophila single-minded, an orthologue of Arnt,

essential for midline differentiation

• AhR主动物的适应与对污染物的毒性反应• 正常生长发育和免疫细胞的重要调节因子• 也是一些生理平衡的重要调节因子

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AhR pathway participants

90

X XAP2/AIP

HSP90 x 2

L

L

Exogenous ligand

Endogenous ligand

AhR Arnt AhRR

IC Initiation complex

NuNu

Nucleosomes

Nuclear proteins?

XRE promoter gene (ie.CYP1A1)

Target DNA

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AhR信号通道调节

+

XRE

mRNAX

Translation

+XRE promoter gene (AhRR)

mRNA

IC

AhRR

Proteosome degradation

抑制调节

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AhR信号通道与其它通道的交互作用

http://www.helsinki.fi/science/dentenv/dioxin.html

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持久与短暂 AhR激活

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持久与短暂 AhR激活

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AhR 活力的调控• Rapid receptor degradation (2)

– Ubiquitination – proteosomal degradation– Only happen in SUSTAINED AhR activity

• The action of an AhR Repressor (AhRR) (3)

• Agonist depletion through an enzymatic negative feedback loop (5)

• The evolution of multiple mechanisms to suppress sustained AhR activity implies that its prolonged signaling is physiologically deleterious.

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持久与短暂激活• G1 arrest

Sustained +Transient –

• Constitutively active AhR (CA-AhR)– Marked incidence in gastric tumors– It is tempting to speculate that CA-AhR may a

ctually suppresses normal growth in the stomach and liver thereby conferring a growth advantage upon any transformed cells in the tissue

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• Transient and sustained AhR activation affect the transcriptome differently– culminating in distinct biological responses to

receptor activation– highlights the importance of tightly regulating

AhR signaling

• Suffice it to say that sustained AhR activity invokes a homeostatic disequilibrium– underscored by a dramatically altered transcri

ptome.

Conclusions

Page 46: “ 二噁英”污染与人类健康

其它重要效应

• 机体 /细胞的氧化还原稳态改变– 活性氧 (reactive oxygen species, ROS) 水平增高

• ROS– 分子和细胞氧化损伤

• DNA, RNA, Protein, peroxidization of lipids, organelles

– 组织氧化损伤– 免疫抑制(损伤),等

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DNA损伤 — 种类与修复

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DNA损伤修复模型

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DNA双链断裂• DNA Double SStrand Breaks (DSBs)

• 一种 DNA损伤– 最严重– 直接产生

• UV

– 间接产生•未能修复的 DNA损伤使其在复制时受阻而产生

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DNA SB RepairNature, 411:366-374, 2001

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DNA DSBs只是损伤的产物吗?

• No!– They operate in diverse biological settings

• V(D)J– Generating immune-receptor diversity

• Production of gametes for sexual reproduction– Meiosis I (减数 ) and II. Sister chromatin exchange p

roceeds M I, involving Spol I that bound DSBs

• Telomere homeostasis and ageing

– Transportable Elements

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端粒稳态与老化DDR protein Role at normal telomeres

MRN Telomere length regulator, role in end processingATM, CHK2 and ATR Maintain telomere length, phosphorylate Shelterin-

complex components, possible roles in telomerase activationand recruitment

Ku and DNA-PKcs Telomere components and telomere-length regulators, possible telomere-capping functions

RAD9–RAD1–HUS1 (9-1-1) Telomere component and telomere-length regulator; aids telomerase recruitment/activation

Nucleases EXO1, FEN1, Processing of telomeric termini to promote XPF/ERCC1 and Apollo telomerase action; regulate telomere integrityPARP1 Potential telomere-length regulatorBRCA1 Telomere maintenanceRPA Telomere component, in telomerase recruitmentWRN Maintains telomere structure and functions in

telomere replicationRAD51D and other HR proteins Regulate telomeric integrity

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DNA损伤与疾病• 癌症与 DNA损伤“亲密”关联

– HAHs cause ROS elevation)

• Neurodegenerative disorders– Remember Sim? And AhR belongs to PAS?

• Immune deficiencies and infertility– mutations in NHEJ factors yield B- and T-cell imm

une deficiency– Spermatogenesis

• Genome Instability in Other Heritable hDiseases

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Page 57: “ 二噁英”污染与人类健康

健康危害与对策• 致癌• 非致癌• 对策

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健康危害• 致癌

– TCDD, a Group 1 carcinogen by the Int’l Agency for Research on Cancer (IARC)

– US EPA• Potential human carcinogen ’94• non-cancer effects (reproduction and sexual de

velopment, immune system) may pose an even greater threat to human health

• No threshold dose ’00

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健康危害• 非致癌危害包括

– Developmental abnormalities– Central and peripheral nervous system pathology– Thyroid disorders – Damage to the immune systems– Diabetes– Exposure to dioxins changes the ratio of male to f

emale births among a population • More females are born than males

– etc.

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对策• 预防和控制“二噁英”暴露

– Proper incineration of contaminated material is the best available method of preventing and controlling exposure to dioxins

• 高温 >850°C

– 预防食物污染• 食品加工质量控制• 食品安全监控

• 个人如何减少“二噁英”风险– Trimming fat from meat and consuming low fat dairy pr

oducts– A balanced diet (adequate fruits, vegetables etc.)

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Identify and measure dioxins in the environment and food

• The quantitative chemical analysis of dioxins requires sophisticated methods– Time consuming– Capital consuming: > US$1700/sample

• Advocate for biological-based methods– Use for screening– Confirm by chemical analysis

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