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1)  CO 2 aeration
CO2曝气
2)  carbon dioxide gas
CO2气
3)  aeration [英][,eiə'reiʃən]  [美][,eə'reʃən]
曝气
1.
Treating dyeing wastewater by catalystic iron inner electrolysis process with aeration;
曝气催化铁内电解法对印染废水预处理的试验
2.
Discussion on aeration repair theory of oil pollution of groundwater;
地下水石油污染曝气修复理论探讨
3.
Renovation of Polluted River Water by Artificial Reaeration;
人工曝气复氧整治污染河流
4)  aerating [英]['eiəreit]  [美]['eə,ret]
曝气
1.
Design optimization were adopted in aerating and sedimentation when municipal sewage was treated by CASS(Cyclic Activated Sludge System),which was useful to save running power cost and process administration optimization.
采用循环式活性污泥法(CASS)工艺处理城市生活污水,并对曝气和沉淀排水阶段进行设计优化,利于节能及优化运行。
5)  Aerate [英]['eəreɪt]  [美]['ɛ'ret]
曝气
1.
92 mg/L(the addition is half of the theory),aerated pressure is 40 kg/cm2 and aerated time is 1 h,the water treated by this method may be met the criterion of drinking water.
采用在水中投加适量高锰酸钾并同时曝气的混合方法,来处理模拟地下水中的Mn2+。
2.
With being aerated for 4 to 12 hours ,the rate of removing COD Cr ,BOD 5 and NH 3 N from the outlet of SBR tanks reaches 85%~95%.
当曝气时间为 4~ 12h时 ,SBR泄出水CODCr、BOD5及氨氮的去除率分别能达到 85 %~ 95 %、90 %~ 95 %和 6 5 %~ 80 % ,从而大大降低了垃圾渗滤液治理工艺中后续处理阶段的负荷 。
6)  blower-aeration
鼓气曝气
1.
Two methods of blower-aeration and vacuum pump-aeratin were comparatively studied.
对鼓气曝气和抽气曝气两类曝气方法做了对比研究,结果显示:抽气曝气,稀释水DO始终达不到8mg/L,开放静置24h,DO几乎不增加;鼓气曝气30min,稀释水DO已稳定超过8mg/L,鼓气曝气120min后开放静置20h,DO仍有8mg/L。
补充资料:poly(bisphenol a-co-4-nitrophthalic anhy-dride-co
CAS:61128-46-9
分子式:(C31H20O8·C6H8N2)x
中文名称:5,5'-[(1-甲基亚乙基)双(4,1-亚苯氧基)]双-1,3-异苯并呋喃二酮与1,3-亚苯二胺的聚合物

英文名称:1,3-Isobenzofurandione, 5,5'-[(1-methylethylidene)bis(4,1-phenyleneoxy)]bis-, polymer with 1,3-benzenediamine

3-isobenzofurandione, 5,5'-[(1-methylethylidene)bis(4,1-phenyleneoxy)]bis- polymer with 1,3-benzenediamine

poly(bisphenol a-co-4-nitrophthalic anhy-dride-co

1,3-Isobenzofurandione,5,5'-[(1-methylethylidene)bis(4,1-phenyleneoxy)]bis-,polymer with 1,3-benzenediamine
说明:补充资料仅用于学习参考,请勿用于其它任何用途。
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