活化炭處理 的英文怎麼說

中文拼音 [huóhuàtànchǔ]
活化炭處理 英文
carbon treatment active
  • : Ⅰ動詞1 (生存; 有生命) live 2 [書面語](救活) save (the life of a person):活人無算 (of a goo...
  • : 名詞1. (木炭的通稱) charcoal 2. (像炭的東西) sth. resembling charcoal3. [方言] (煤) coal4. (姓氏) a surname
  • : 處名詞1 (地方) place 2 (方面; 某一點) part; point 3 (機關或機關里一個部門) department; offi...
  • : Ⅰ名詞1 (物質組織的條紋) texture; grain (in wood skin etc ) 2 (道理;事理) reason; logic; tru...
  • 活化 : [化學] activation radioactivation; activate活化處理 activating treatment; 活化分析 [核物理] activ...
  1. Practice of treatment of cyanogen - bearing tailing water from mineral processing with active carbon absorption oxidation method

    吸附氧選礦含氰尾水的實踐
  2. 2 ) lab experiment of gac : to find the suitable granual activated carbon to treat the slightiy polluted xiang rivel 3 ) production experiment : make use of the dates acquired from lab experiment and jar test to run the model water plant. by contrasting two series of treating processes, the effect of " improving gac performance by optimized coagulatiod " was investigated

    3 )中試:將小試試驗中所獲得的試驗參數帶入模型水廠試驗裝置中進行運行,通過兩種工藝的對比,對「強混凝與吸附技術聯用」工藝湘江微污染源水的效果進行考察。
  3. Adsorption isotherm of activated alumina and bone char can be described by langmuir adsorption isotherm in the form qe = 0. 72cy ( l + 0. 074ce ) and freundlich isotherm in the form qe = 0. 88ce1 / 1. ' 94 respectively. continuous - flow column experiments show there have higher removal capacity for activated alumina and bone char when empty - bed contact time was controlled within 12 ~ 15min and about 15min separately

    對可利用吸附容量和實際利用吸附容量的論分析說明,連續性氧鋁停留時間控制在12 15min較好,此時吸附容量利用率較高,約為80 ,骨停留時間控制在15min較好,吸附容量利用率約為75 。
  4. A deep treatment pilot test was made on micropolluted source water with combined technique of o3 preoxidizing biological pretreatment - coagulant sedimentation - sand filter - o3 after oxidizing biological activated carbon ( bac ) filter

    摘要利用臭氧預氧生物預混凝沉澱砂濾臭氧后氧生物濾池組合工藝對微污染水源水進行了深度中間試驗。
  5. The optimum conditions for air electrode preparation were shown as follow : 20 % ptfe and 20 % mno2 in active layer, thickness of active layer 0. 15 - 0. 25mm and the ratio of active carbon to ethine black 4 : 1 ; 60 % ptfe in the gas diffusion and waterproof layer, employing na2so4 as pore - making agents, thickness 0. 35 - 0. 45mm, colding forming and layer sequence catlytic layer / gas diffusion and waterproof layer / current collector layout ; employing 40 meshed nickel screen as current collector and thermal treatment temperature over 200

    確定了制備空氣電極的優工藝條件,催層中ptfe含量約20 , mno _ 2的最佳含量約為20 ,催層中和乙炔黑的比例為4 : 1 (質量比) ,厚度在0 . 15 - 0 . 25mm之間。防水透氣層中ptfe的含量約為60 ,以無水硫酸鈉作為造孔劑,厚度一般為0 . 35 - 0 . 45mm 。電極各層採用催層/防水透氣層/集流體的排布方式,冷壓成型,熱對空氣電極的性能影響較大,熱溫度不低於200 。
  6. The convential wate treatment process do n ' t work very well to this kind of water, the effluent of which have lots of thms that may cause cancer. the powered activated carbon ( pac ) was welcomed by most water sciticists for its flexible application, particularly to the water changing much duo to the season

    粉末以其應用靈、基建投資省而受到人們的歡迎,尤其適合於季節性變大的源水的凈。本文針對黃河微污染源水較系統的研究了粉末微污染源水中投加條件和效果。
  7. By experiments the conclusions were got that the actived carbon electrode could provide better capacitive character in 7mol / l potassium hydroxide solution after activation in ammonia

    通過大量的實驗發現氨水后的在濃度為7mol l的氫氧鉀溶液中具有良好的電容性能。
  8. Zhuxi activated carbon co., ltd. is a cooperative enterprise of caf, integrating manufacture, developing and marketing. it possesses fixed assets of over rmb15, 000, 000, senior technical personnel of 58 and site area of 30000m2, equipped with more than ten advanced carbon activation furnaces for different technology and end - treating facilities., enjoying annual output capacity of over10000t

    本公司系中國林科院林產工研究所科研所合作企業,也是一家集生產,開發,經營與一體的專業工廠,建地面積30000平方米,裝備有十多臺(套)較先進且適用於不同工藝的爐和后生產設備,年生產能力在10000噸以上。
  9. Effects of acid treatment to activated carbons on their properties and catalytic performance in hydrogen production by methane decomposition

    性質及其催裂解甲烷制氫性能的影響
  10. The resuit indicates : wheil treating siightiy polluted source water of xiang rivet, optimized coagulation will improve the effect of reducing organics remarkably ; gac has good effect in reducing the dbpfp and organics of xiang rivef, but the effect in reducing dbp is more obviously ; the process of " improving gac by optimized coaguiation " can not only has a wonderful result of reduction in dbppp and organics, but also improve the effect of gac evident1y and decreasing the capital cost for a gac facility ; although optimized coagulation increase the quantity of alum dose, but the level of aluminum of treated water will not beyond the standard level ; different processes will have different resu1ts in lessening the amount of organics and dbp, so we should adopt treatment process by considering the requirements of treated watel

    試驗結果表明:在對受到微污染的湘江源水的時,強混凝工藝對于去除有機物具有比較明顯的作用;吸附技術湘江源水時,其對去除水中消毒副產物前體具有明顯的效果,對去除水中有機物效果也很好,但對消毒副產物的去除效果好於對有機物的去除效果;與強混凝聯用工藝不僅能更有效地去除水中有機物以及消毒副產物前體,還能增加的吸附性能,從而減低費用;雖然強混凝投加了比傳統混凝多的混凝劑,但並不會使出水中鋁離子濃度超標;不同工藝對水中有機物和消毒副產物的去除效果各不相同,應根據出水要求而選擇不同的工藝。
  11. Based on advanced technology, this thesis bring forward the optimal scheme and set down general system - drawings and flow charts. using step7 - micro software, we achieve the auto - control aim in drinking water treatment. in practice, the complexity and non - linaerity exit in the system of water treatment, so we apply fuzzy control in water treatment and design a kind of controller which structure can be altered according to the using - rate of ozone and the variety of water quality

    實際飲用水系統由於存在復雜性、非線性、時變性,本文根據臭氧生物工藝存在復雜性、非線性、時變性等特點,將模糊控制應用在水這一不確定的非線性時變系統,針對不同水溫下臭氧利用率及水質的變,設計一種基於系統過程狀態的變結構的模糊控制器,以單片機作為主要控制硬體,按查表方式設計軟體,對進水閥門開度進行在線控制,調節臭氧氣體與進水的比例(臭氧流量及濃度不變) ,達到氣水比最優
  12. In the experiment of catalyst preparation, the catalytic activity of mno2 / c which was prepared with mn ( no3 ) 2 solution and active carbon by the means of thermal decomposition reached the highest among three kinds of catalysts, and the performance of mno2 / c was enhanced by acidification. moreover, the results showed that the catalytic activity of mno2 was also affected by different mode of catalyst and active carbon dispersed

    劑的制備實驗表明,採用硝酸錳溶液和共同熱分解得到的mno _ 2 / c ,具有最高的催性,對催劑進行酸能提高催劑的性,而且催劑和的分散方式不同對其性能的影響較大。
  13. And if we unite these them, we will get more advantages from them. this experiment made some prime lab research about the unition of the two ~, processes. it contents : 1 ) jar test of optimized coagulation : to determine the quantity of drug

    本試驗對強混凝和粒狀吸附技術聯用的工藝作了初步試驗研究,試驗內容包括: 1 )小試:通過杯罐試驗來確定對于不同濁度的湘江源水的混凝最佳劑投加量。
  14. In light of various pollution situations and various water treatment processes of two water factories, better solved the problems about throwing doses, throwing localities, throwing forms of composite potassium permanganate and powder activated carbon, as well as compared the enhanced coagulation efficacy of combined process of composite potassium permanganate and powder activated carbon, composite potassium permanganate pre - oxidation and pre - chlorination

    針對兩水廠不同的源水污染狀況和現有的水工藝,通過室內和生產性試驗,很好地解決了高錳酸鉀復合藥劑、粉末最佳投加點、投加量和投加方式的確定問題,並對兩者聯用的強混凝效果與預氯、單獨高錳酸鉀復合藥劑預氧進行了對比。
  15. Advanced water purification uses ozone treatment and bio - activated carbon treatment during the conventional sedimentation and rapid filtration processes. this treatment breaks down trihalomethane, and substances causing a moldy odor

    先進的水凈設備在傳統沉澱和快速的過濾過程中,使用氧氣,這一除去了三鹵甲烷等引起發霉味道的物質。
  16. Chromium - containing wastewater treatment with active carbon modified by hno3 oxidization

    硝酸氧改性含鉻廢水的研究
  17. Study on the extinguishing coke powder replacing the activated carbon comprehensive treatment coking waste water

    熄焦粉取代綜合廢水的研究
  18. Under the permitted conditions, the all - scale plant was made to pre - ozonation. the results showed : ( l ) the optimal advanced purification drinking water process should be " regular treatment + ozonation + biological activated carbon ". though pre - ozonation had no effects on ammonia nitrogen in the water of micro - pollution water source, instead the turbidity of pre - oxidation finished water was raised, it had effects on killing bacteria and removing algae, and controlling the growth of micro - organism

    得出如下結論: ( 1 )最優的深度飲用水的工藝應該是「常規+臭氧+生物」 ,如果投加預臭氧,對微污染水源水中的氨氮沒有效果,反而引起預氧出水的濁度升高,但是對滅菌除藻,控制微生物的生長有一定的作用。
  19. Water pollution was becoming intensified, while with the improvement of human ' s living standard, more attention was increasingly paid to the sanitation and safety of drinking water. so adopting advanced drinking water purification to obtain high quality water was necessary. by changing the different combination of drinking water ' s regular treatment process, ozonation, activated carbon and biological activated carbon, the paper chose the optimal treatment process, also the parameters of the process were analyzed through experiments, then the economic, reasonable process parameters were determined

    水污染不斷在加劇,而隨著人們生水平的提高,飲用水的衛生和安全越來越被關注,因此有必要採用先進的飲用水深度技術來獲得優質飲用水,本文通過改變飲用水常規工藝、臭氧與生物的不同組合的中試試驗研究,選擇出了最佳工藝,又對最佳工藝的各個參數進行試驗分析,確定出經濟合的工藝參數,在現有的條件下,對預臭氧進行了生產試驗。
  20. In comparison of gac adsorption and ozonation, it was presented that membrane technology will have bright future in water treatment

    通過吸附與臭氧氧技術的比較,提出它在飲用水方面將具有廣闊的應用前景。
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