中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2014年
3期
780-785
,共6页
王菲菲%王先良%刘芳盈%吕占禄%钱岩%朋玲龙
王菲菲%王先良%劉芳盈%呂佔祿%錢巖%朋玲龍
왕비비%왕선량%류방영%려점록%전암%붕령룡
燃煤细颗粒物%PM 2.5%血管内皮细胞%EA.hy926%氧化损伤
燃煤細顆粒物%PM 2.5%血管內皮細胞%EA.hy926%氧化損傷
연매세과립물%PM 2.5%혈관내피세포%EA.hy926%양화손상
coal-fired fine particles%PM2.5%vascular endothelial cell%EA.hy926%oxidative injury
为了解细颗粒物不同组分在心血管系统损伤中的毒性机制,以大同散煤为样品煤,提取燃煤 PM 2.5全颗粒物、无机组分及有机组分,分别对人脐静脉内皮细胞EA.hy926进行染毒,采用超氧化物歧化酶(SOD)、谷胱甘肽过氧化物酶(GSH-PX)及丙二醛(MDA)指标检测PM 2.5不同组分对EA.hy926细胞氧化损伤程度的影响.结果表明,燃煤PM 2.5各组分对EA.hy926细胞染毒24h后,随着染毒剂量的增加,细胞上清液中SOD活力均下降,与对照组相比差异显著,而相同剂量组比较,其抑制SOD活力能力依次为:有机组分>无机组分>全颗粒物,且相同剂量组不同组分间的比较均有统计学差异;GSH-Px活力均下降,具有剂量依赖性,引起GSH-Px活力下降程度基本具有无机组分>有机组分>全颗粒物的趋势,但统计学意义不显著;MDA 含量分别有不同程度的增加,各组分所致的 MDA 含量大小存在低剂量组有机组分>全颗粒物>无机组分,高剂量组全颗粒物>无机组分>有机组分趋势,随着剂量增加,全颗粒物和无机组分引起MDA含量明显增加,而有机组分则变化趋于平缓.可见,燃煤PM不同组分均对血管内皮细胞EA.hy926氧化损伤作用明显,SOD 、GSH-PX等抗氧化酶的活性降低.2.5 inorganic compositions > organic compositions with statistically significance, and as the dose increased, MDA level caused by all particles and inorganic compositions increased significantly, while changes of organic compositions is leveling off. The results can be seen from the above, different compositions of PM2.5exerted oxidative damage to EA.hy926,reduced activities of SOD, GSH-Px, and increased MDA level. But the mechanisms underlying them need futher exploration.
為瞭解細顆粒物不同組分在心血管繫統損傷中的毒性機製,以大同散煤為樣品煤,提取燃煤 PM 2.5全顆粒物、無機組分及有機組分,分彆對人臍靜脈內皮細胞EA.hy926進行染毒,採用超氧化物歧化酶(SOD)、穀胱甘肽過氧化物酶(GSH-PX)及丙二醛(MDA)指標檢測PM 2.5不同組分對EA.hy926細胞氧化損傷程度的影響.結果錶明,燃煤PM 2.5各組分對EA.hy926細胞染毒24h後,隨著染毒劑量的增加,細胞上清液中SOD活力均下降,與對照組相比差異顯著,而相同劑量組比較,其抑製SOD活力能力依次為:有機組分>無機組分>全顆粒物,且相同劑量組不同組分間的比較均有統計學差異;GSH-Px活力均下降,具有劑量依賴性,引起GSH-Px活力下降程度基本具有無機組分>有機組分>全顆粒物的趨勢,但統計學意義不顯著;MDA 含量分彆有不同程度的增加,各組分所緻的 MDA 含量大小存在低劑量組有機組分>全顆粒物>無機組分,高劑量組全顆粒物>無機組分>有機組分趨勢,隨著劑量增加,全顆粒物和無機組分引起MDA含量明顯增加,而有機組分則變化趨于平緩.可見,燃煤PM不同組分均對血管內皮細胞EA.hy926氧化損傷作用明顯,SOD 、GSH-PX等抗氧化酶的活性降低.2.5 inorganic compositions > organic compositions with statistically significance, and as the dose increased, MDA level caused by all particles and inorganic compositions increased significantly, while changes of organic compositions is leveling off. The results can be seen from the above, different compositions of PM2.5exerted oxidative damage to EA.hy926,reduced activities of SOD, GSH-Px, and increased MDA level. But the mechanisms underlying them need futher exploration.
위료해세과립물불동조분재심혈관계통손상중적독성궤제,이대동산매위양품매,제취연매 PM 2.5전과립물、무궤조분급유궤조분,분별대인제정맥내피세포EA.hy926진행염독,채용초양화물기화매(SOD)、곡광감태과양화물매(GSH-PX)급병이철(MDA)지표검측PM 2.5불동조분대EA.hy926세포양화손상정도적영향.결과표명,연매PM 2.5각조분대EA.hy926세포염독24h후,수착염독제량적증가,세포상청액중SOD활력균하강,여대조조상비차이현저,이상동제량조비교,기억제SOD활력능력의차위:유궤조분>무궤조분>전과립물,차상동제량조불동조분간적비교균유통계학차이;GSH-Px활력균하강,구유제량의뢰성,인기GSH-Px활력하강정도기본구유무궤조분>유궤조분>전과립물적추세,단통계학의의불현저;MDA 함량분별유불동정도적증가,각조분소치적 MDA 함량대소존재저제량조유궤조분>전과립물>무궤조분,고제량조전과립물>무궤조분>유궤조분추세,수착제량증가,전과립물화무궤조분인기MDA함량명현증가,이유궤조분칙변화추우평완.가견,연매PM불동조분균대혈관내피세포EA.hy926양화손상작용명현,SOD 、GSH-PX등항양화매적활성강저.2.5 inorganic compositions > organic compositions with statistically significance, and as the dose increased, MDA level caused by all particles and inorganic compositions increased significantly, while changes of organic compositions is leveling off. The results can be seen from the above, different compositions of PM2.5exerted oxidative damage to EA.hy926,reduced activities of SOD, GSH-Px, and increased MDA level. But the mechanisms underlying them need futher exploration.
To explore the effects of different compositions of fine particles on the cardiovascular system. Coal sample taking Datong coal as a sample, Coal-fired PM2.5 was sampled by fixed source dilution channel in the laboratory. All particles, as well as isolated inorganic and organic compositions, were extracted to contaminate EA.hy926cells for 24h respectively. To evaluate oxidative damages of different compositions of coal-fired PM2.5 exposed to the EA.hy926cells, the assays of superoxide dismutase (SOD), malondialdehyde (MDA), Glutathione peroxidase (GSH-Px) were carried out using assay kits according to the manufacturer’s instructions. The results showed that as the dose increased, SOD activity decreased in EA.hy926exposed to different compositions of coal-fired PM2.5 24h. Each dose group was statistically different (P<0.01) compared with the control group, and there is a dose-response relationship. At the same dose, SOD inhibition of different compositions was: organic compounds> inorganic compositions > all particles, with statistically significance differences among the same dose. Compared to solvent control, as the dose increased, GSH-Px activity decreased in EA.hy926exposed to different compositions of coal-fired PM2.5. At the same dose, GSH-Px inhibition of different compositions was:inorganic compounds>organic compositions>all particles, with no statistically significance differences. As the dose increased, MDA levels in supernatants treated with all particles, inorganic compositions and organic compositions increased, respectively. At the low doses, MDA level of different compositions of coal-fired PM2.5 on EA.hy926was:organic compositions>all particles>inorganic compositions, while at the high doses:all particles>inorganic compositions > organic compositions with statistically significance, and as the dose increased, MDA level caused by all particles and inorganic compositions increased significantly, while changes of organic compositions is leveling off. The results can be seen from the above, different compositions of PM2.5exerted oxidative damage to EA.hy926 ,reduced activities of SOD, GSH-Px, and increased MDA level. But the mechanisms underlying them need futher exploration.