- 更多網(wǎng)絡(luò)例句與硝化相關(guān)的網(wǎng)絡(luò)例句 [注:此內(nèi)容來(lái)源于網(wǎng)絡(luò)国内揄拍国内精品人妻不卡,僅供參考]
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The invention is to carry out heterotrophic nitrifying phenomenon from the biology angle by screening heterotrophic nitrifying bacteria and the technology is the condition precedent to carry out short-range self-synchronous nitration and denitrification.
本發(fā)明的目的是采用篩選異養(yǎng)硝化菌的方法亚洲国产综合无码一区,從生物學(xué)角度實(shí)現(xiàn)異養(yǎng)硝化現(xiàn)象一级做a爱全免费视频在线,該技術(shù)是實(shí)現(xiàn)短程同步硝化反硝化的先決條件精品99污。
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According to the above study results, especially the steady operation of two-sludge system(2A/O+N 2SBR), it can be proved that denitrification and excess phosphorus uptake are relatively independent and intersectant biological processes. The overlap is that denitrifying phosphorus removing bacteriawhich possesses the two bacterial metabolisms, could utilize nitrate as an electron acceptor for phosphorus uptake. The two-sludge system can not only combined biological phosphorus removal and denitrification processes to form a process in practical wastwater treatment , but also solved the main difficulties of current single-sludge systems:①the sludge age competition between phosphorus removing bacteria and nitrifier;② the substrate competition between denitrification and dephosphatation.
以上的研究結(jié)果,尤其是時(shí)間序列的雙泥生物反硝化除磷脫氮系統(tǒng)工藝(2A/O+N 2SBR法)的穩(wěn)定運(yùn)行久久av免费不卡天堂小草播放,不僅證明了生物脫氮與生物除磷是兩個(gè)既相對(duì)獨(dú)立又相互交叉的生理過(guò)程激情一级a片在线播放,其交叉點(diǎn)是同時(shí)擁有硝酸鹽還原性和超量吸磷這兩種生化特性的細(xì)菌進(jìn)行的反硝化吸磷脫氮生化反應(yīng),而且雙泥系統(tǒng)工藝克服了常規(guī)單泥生物脫氮除磷工藝的兩大問(wèn)題(①聚磷菌和硝化菌的SRT相互干擾找个能直接看的黄色网站;②反硝化與生物除磷競(jìng)爭(zhēng)VFA)被强制伦A片在线观看,同時(shí)保證了脫氮和除磷效果,排水指標(biāo)達(dá)到污水綜合排水標(biāo)準(zhǔn)(GB8978-1996)的一級(jí)標(biāo)準(zhǔn),具有實(shí)際工程使用價(jià)值人人干,人人草。
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After comparison of various process, a optimum process—ANIS process can be drawn; A autotrophic denitrifying process is successfully started up and stable operated; ANIS nitrous nitrifying process and autotrophic denitrifying process are joining-up in series to operate, and sound nitrogen removal effect can be achieved.
本論文廣泛研究了各類(lèi)C/N均小于1欧欧美一级a爱高清成在线看、甚至低至0.5以下的低、中欧美一级黄片久久久久久久、高氨氮濃度廢水進(jìn)行亞硝化處理的效果欧美一区二区三A片,綜合比較了各種不同的處理工藝,得出了最佳工藝——ANIS工藝和運(yùn)行條件久久久久久A级片;成功啟動(dòng)并穩(wěn)定運(yùn)行了自養(yǎng)反亞硝化系統(tǒng)国产高清无码强奸视频网址,并將ANIS亞硝化工藝和自養(yǎng)反亞硝化工藝串連運(yùn)行,取得了良好的脫氮效果黄色性爱欧美狂野澳门。
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The invention discloses a disposing method of ammonia nitrogen waste water in the effluent disposal technological domain, which is characterized by the following: sieving heterotrophic nitrobacteria and aerobic denitrobacteria with stronger environment adaptive ability to nitrate and denitrate simultaneously; constructing mud nitrated and denitrated system to dispose waste water with nitrogen simultaneously to satisfy different DO densities.
為了解決同步硝化反硝化過(guò)程中菌種來(lái)源不明插插受不了视频,調(diào)控困難,硝化和反硝化對(duì)DO濃度要求不同人人上人人干人人操,在實(shí)際工程中難以實(shí)現(xiàn)同步硝化反硝化欧美日韩二区在线另类,本發(fā)明篩選出對(duì)環(huán)境有較強(qiáng)適應(yīng)能力的異養(yǎng)硝化細(xì)菌和好氧反硝化細(xì)菌www.95,采用異養(yǎng)硝化細(xì)菌和好氧反硝化細(xì)菌構(gòu)建同步硝化反硝化污泥體系處理含氮廢水www.日本视频,具有投資少,費(fèi)用低www.玖玖玖,處理效果好一级特黄色片欧美色图,不僅去除廢水中的氨氮,而且對(duì)總氮也有較高的去除率很色很黄很污的网站在线看。
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To assess the thermal contribution from oxidation reaction, the standard formation enthalpes of all reactants and products were used to calculate the oxidation enthalpies. It could be found that all oxidation reactions were exothermic. And oxidation played a more important role during the toluene trinitration at high temperature, because the reaction temperature of toluene trinitration is the higher than mononitration and dinitration, and the temperature coefficient of oxidation is higher than that of trinitration too.
為了考察不同階段氧化副反應(yīng)對(duì)反應(yīng)放熱的貢獻(xiàn)黄色网站日韩观看免费,用反應(yīng)物和產(chǎn)物的標(biāo)準(zhǔn)生成焓推得氧化反應(yīng)的理論反應(yīng)熱,計(jì)算結(jié)果表明日韩mv在线看成人网站,各段硝化的氧化副反應(yīng)均為放熱反應(yīng)日韩ww频在线免费观看,其中三段硝化反應(yīng)由于反應(yīng)溫度最高,氧化反應(yīng)的溫度系數(shù)比硝化反應(yīng)高yw国产在线视频在线观看,故氧化副反應(yīng)對(duì)三段硝化影響最大国产精品特黄特级AAAAAA片。
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Experimental results showed that, in this process, the optimal pH of the shortcut nitrification was 8.0~8.5; when the pH was less than 6,the nitrification is completely inhibited; when the pH was 6~7, at the end of aeration, the Nitrobacteria become the dominant bacteria because of the dropping of the free ammonia concentration. It is known to all, the activity of the Nitrobacteria and Nitrosomonas was affected by FA concentration, so nitrification was affected by FA concentration. According to the author's research results, the FA concentration which inhibit the Nitrobacteria was below 1.0mg/L,which inhibit the Nitrosomonas was above 10mg/L.
實(shí)驗(yàn)研究結(jié)果表明:本工藝中,短程硝化反應(yīng)的最佳pH值在8.0~8.5之間处女开破视频,當(dāng)pH小于6時(shí)欧美大胆一级视频,整個(gè)硝化反應(yīng)都會(huì)受到抑制,當(dāng)pH在6~7之間時(shí)嗯好深啊用力哦啊视频,隨著游離氨濃度的降低中国三级黄色片18岁美女全体逼,在曝氣后期,硝化菌將會(huì)占據(jù)優(yōu)勢(shì)手机在线免费看黄色片网站;FA濃度對(duì)短程硝化反應(yīng)的影響是通過(guò)對(duì)亞硝酸菌和硝酸菌的抑制來(lái)實(shí)現(xiàn)的超碰地址,在本研究條件下,游離氨對(duì)亞硝酸菌的抑制濃度在10mg/L以上,對(duì)硝酸菌的抑制濃度在1.0mg/L以下国产欧美精品一区二区三区四某1区;溫度對(duì)短程硝化反應(yīng)的影響是雙重的国产免费看视频黄片,既影響微生物的生理活性,又影響FA濃度麻豆A片在线观看。
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When studying simultaneous nitrification and denitrification in membranebioreactor,it was foud that the concentration of DO was a key factor and the influence of C/N,pH value and temperature were unconspicuous.
在研究同步硝化反硝化作用時(shí)發(fā)現(xiàn)国产97av在线播放,C/N、pH值和溫度對(duì)同步硝化反硝化作用無(wú)影響视频一区二区久久91,DO是影響系統(tǒng)同步硝化反硝化的關(guān)鍵因素免费成年人在线看。
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Among them, nitrate-sulfuric acid system with higher nitrating activity can get high yields at mild condition in the nitration of deactivated aromatic compounds and could be used in the laboratory and industrial applications.
其中,硝酸鹽/硫酸體系具有較強(qiáng)的硝化能力Ⅴ片视频免费在线观看,對(duì)于鈍化芳環(huán)欧美熟妇free性XXXX,可以在溫和條件下以高收率得到硝化產(chǎn)物,在實(shí)驗(yàn)室制備或工業(yè)應(yīng)用中具有較高的應(yīng)用價(jià)值国产精品资源网在线观看;其他硝化方法由于各種原因暫時(shí)不能對(duì)鈍化程度較高的芳環(huán)進(jìn)行硝化澳美午夜福利,還需進(jìn)一步研究具有較高活性的硝化體系。
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The green synthesis of nitrate esters using dinitrogen pentoxide (N2O5) as nitrating agent was briefly summarized.
評(píng)述了N2O5為硝化劑制備硝酸酯類(lèi)含能材料的綠色合成技術(shù)人人爽人人看人人硬,分析了N2O5-有機(jī)溶劑硝化国产91视频有限公司、N2O5-固體載體硝化和引入保護(hù)基硝化等三種體系工藝的過(guò)程和特點(diǎn),展望了各硝化體系的發(fā)展前景在线等免费看黄片。
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The expression of one-dimensional mathematical model of vertical migration of ammonia in the CRI system is:The parameters in the CRI model are determined as following: the retardarce coefficient is determined by static isothermal absorption experiment, the velocity of sewage travel through the soil column is determined by permeability test, the vertical dispersion coefficient is determined by test the electric conductivity of tracer in the dispersion experiment, the rate of nitrification and denitrification is determined by test of Baps technology.
依據(jù)單一氨氮www。.你懂得、硝氮配水條件下的試驗(yàn)結(jié)果,引入多孔介質(zhì)的溶質(zhì)運(yùn)移理論及對(duì)流-彌散方程美国少妇a级,考慮NH4+-N在CRI系統(tǒng)中的運(yùn)移受到對(duì)流和水動(dòng)力彌散作用的影響免费激情在线视频国产,并吸附-解吸、硝化與反硝化3個(gè)過(guò)程国产免费一级特黄真人视频大全,首次將配水流經(jīng)CRI土柱的孔隙水流速方程與CRI土柱內(nèi)發(fā)生的亚洲国产精品日本一区二区、以氧為約束條件的硝化、反硝化過(guò)程聯(lián)系起來(lái)igao,建立了CRI系統(tǒng)一維垂向氨氮運(yùn)移轉(zhuǎn)化數(shù)學(xué)模型95视频手机在线观看,表達(dá)式為:研究分別通過(guò)靜態(tài)等溫吸附實(shí)驗(yàn)率定了模型方程中的阻滯系數(shù)、通過(guò)滲濾試驗(yàn)測(cè)定了土柱中的孔隙水流速av九一、通過(guò)測(cè)定彌散試驗(yàn)中示蹤劑的電導(dǎo)率確定了縱向彌散系數(shù)欧洲人与动牲交Α欧美精品、通過(guò)氣壓過(guò)程分離技術(shù)測(cè)定了土柱中的總硝化與反硝化反應(yīng)速率常數(shù),最后通過(guò)測(cè)定土柱沿程氧化-還原電位的方法分析氨氮在CRI系統(tǒng)中的運(yùn)移轉(zhuǎn)化機(jī)理亚洲欧美中文日韩V日本。
- 更多網(wǎng)絡(luò)解釋與硝化相關(guān)的網(wǎng)絡(luò)解釋 [注:此內(nèi)容來(lái)源于網(wǎng)絡(luò)日韩性色生活免费观看,僅供參考]
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denitrifying bacteria:反硝化菌
段. 硝化菌(nitrifier)包括亞硝酸菌(nitrite bacteria),亦稱(chēng)氨氧化菌和硝酸菌數(shù)反硝化菌(Denitrifying bacteria)是異養(yǎng)菌(反硝化桿菌、熒光假單胞菌),也有
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Denitrification:反硝化作用
主要來(lái)源於硝化作用(Nitrification)與反硝化作用(Denitrification), 由硝化菌通過(guò)氧化將NH3轉(zhuǎn)化為NO2, 或少量由沒(méi)有氣氧能生活的細(xì)菌經(jīng)過(guò)反硝化作用將NO3轉(zhuǎn)化為NO2.
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aerobic denitrification:好氧反硝化
然而近年來(lái),國(guó)內(nèi)外的不少研討和報(bào)道已能充足證明,反硝化可產(chǎn)生在有氧條件下,即好氧反硝化(Aerobic denitrification)的存在[1~2]?. 而在許多實(shí)際運(yùn)行中的好氧硝化池中也常常發(fā)明有30%的總氮喪失[3]. 作者在采取序批式反映器處置某化肥廠氨氮廢水的鉆研中也發(fā)現(xiàn)了類(lèi)的現(xiàn)象.
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aerobic denitrification:好氣反硝化,好氣性反硝化作用
aerobic dehydrogenase 需氧脫氫酶 | aerobic denitrification 好氣反硝化,好氣性反硝化作用 | aerobic digestion 好氣性消化,需氧消化法
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denitrifying dephosphorization:反硝化除磷
反硝化聚磷:denitrifying dephosphatation | 反硝化除磷:denitrifying dephosphorization | 反硝化聚磷菌:Denitrifying phosphorus-accumulating organisms
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pyroxylin silk:硝化人造纖維,硝化絲
pyroxylin coating 硝化棉涂布 | pyroxylin silk 硝化人造纖維,硝化絲 | pyroxyline varnish 低氮硝化纖維漆
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pyroxylin coating:硝化棉涂布
pyroxyling 硝化棉 | pyroxylin coating 硝化棉涂布 | pyroxylin silk 硝化人造纖維,硝化絲
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Nitrobacter:硝化菌
然而,將硝化階段控制在亞硝化階段的成功報(bào)道并不多見(jiàn).這是因?yàn)?硝化菌(Nitrobacter)能夠迅速地將亞硝酸鹽轉(zhuǎn)化為硝酸鹽.SHARON工藝的成功在于:巧妙地應(yīng)用了硝化菌(Nitrobacter)和亞硝化菌(Nitrosomonas)的不同生長(zhǎng)速率,即在較高溫度下,
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Nitrosococcus:亞硝化球菌屬
參與這個(gè)階段活動(dòng)的亞硝酸細(xì)菌主要有 5個(gè)屬:亞硝化毛桿菌屬(Nitrosomonas) ;亞硝化囊桿菌屬(Nitrosocystis);亞硝化球菌屬(Nitrosococcus);亞硝化螺菌屬(Nitrosospira)和亞硝化肢桿菌屬(Nitrosogloea).
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nitrosomonas:亞硝化單胞菌
水族界向來(lái)認(rèn)定亞硝化單胞菌(Nitrosomonas)將 NH4 轉(zhuǎn)變成 NO2,而硝化桿菌(Nitrobacter)則將 NO2 轉(zhuǎn)變成 NO3,亞硝化單胞菌(Nitrosomonas)和硝化桿菌(Nitrobacter)在水族缸內(nèi)所扮演的角色其實(shí)不如預(yù)期!