天堂国产午夜亚洲专区-少妇人妻综合久久蜜臀-国产成人户外露出视频在线-国产91传媒一区二区三区

濕式過(guò)氧化氫氧化活性艷藍(lán)KN-R的實(shí)驗(yàn)研究及機(jī)理分析

發(fā)布時(shí)間:2018-12-25 12:06
【摘要】:隨著印染行業(yè)的發(fā)展,染料廢水對(duì)水體的污染日益嚴(yán)重。由于染料廢水中含有大量的、難以被微生物降解的有毒有害物質(zhì),使印染廢水的污染治理成為人們關(guān)注的焦點(diǎn)。在所有染料中,蒽醌染料的使用量?jī)H次于偶氮染料。由于其具有十分穩(wěn)定的蒽醌結(jié)構(gòu),不易被生物降解,因而在環(huán)境中殘留時(shí)間長(zhǎng);钚云G藍(lán)KN-R是一種典型的蒽醌類染料。為了有效地處理印染廢水,本論文采用了濕式過(guò)氧化氫氧化法(Wet Peroxide Oxidation,簡(jiǎn)稱WPO)降解活性艷藍(lán)KN-R。通過(guò)篩選反應(yīng)因子,獲得最佳的條件是:H_2O_2的添加劑量為20.4μL,即反應(yīng)體系中H_2O_2的溶度為0.01 mol/L,反應(yīng)溫度為150°C,反應(yīng)時(shí)間為4 h,反應(yīng)壓強(qiáng)為0.5 MPa,p H為6.8。在最佳的條件下處理后,活性艷藍(lán)KN-R模擬廢水的顏色由深藍(lán)色變?yōu)闊o(wú)色。當(dāng)初始濃度為200 mg/L時(shí),在最優(yōu)條件下,活性艷藍(lán)KN-R的脫色率和TOC去除率分別為100%和68.54%。在120~150°C范圍內(nèi)考察了該反應(yīng)的動(dòng)力學(xué),結(jié)果表明活性艷藍(lán)KN-R的濕式過(guò)氧化氫氧化反應(yīng)符合準(zhǔn)一級(jí)動(dòng)力學(xué)方程,并且通過(guò)計(jì)算得到了反應(yīng)活化能為73.9 k J/mol(R2=0.96)。對(duì)活性艷藍(lán)KN-R經(jīng)WPO法降解后的產(chǎn)物,利用氣相色譜/質(zhì)譜聯(lián)用儀(GC-MS)進(jìn)行鑒定。結(jié)果表明其降解產(chǎn)物主要為小分子有機(jī)酸,如丁二酸、已二酸、鄰苯二甲酸,而這種小分子酸都是可生化的,這說(shuō)明經(jīng)過(guò)WPO降解后,活性艷藍(lán)KN-R的可生化性有所提高。通過(guò)添加自由基捕獲劑(叔丁醇)研究了自由基反應(yīng)機(jī)理,結(jié)果顯示,自由基捕獲劑的存在對(duì)WPO法降解活性艷藍(lán)KN-R有負(fù)面影響。150°C,0.5 MPa氧氣壓力,加入叔丁醇,反應(yīng)4 h后,溶液在596 nm處的吸光度從0.00725增加到0.40696,因此H_2O_2在反應(yīng)過(guò)程中產(chǎn)生了羥基自由基,并且高反應(yīng)活性的羥基自由基也參與了WPO法降解活性艷藍(lán)KN-R的反應(yīng)機(jī)制。
[Abstract]:With the development of printing and dyeing industry, dye wastewater pollution to water is becoming more and more serious. Because dye wastewater contains a lot of toxic and harmful substances which are difficult to be degraded by microorganisms, the pollution treatment of printing and dyeing wastewater has become the focus of attention. Of all the dyes, anthraquinone dyes are used second only to azo dyes. Because of its stable anthraquinone structure, it is difficult to biodegrade, so it remains in the environment for a long time. Reactive brilliant blue KN-R is a typical anthraquinone dye. In order to deal with printing and dyeing wastewater effectively, wet hydrogen peroxide oxidation (Wet Peroxide Oxidation,) method was used to degrade reactive brilliant blue KN-R. (WPO). By screening the reaction factors, the optimum conditions were obtained as follows: the amount of H_2O_2 was 20.4 渭 L, that is, the solubility of H_2O_2 in the reaction system was 0. 01 mol/L, the reaction temperature was 150 擄C, the reaction time was 4 h. The reaction pressure is 0. 5 MPa,p H is 6. 8. After treatment under the best conditions, the color of reactive brilliant blue KN-R simulated wastewater changed from dark blue to colorless. When the initial concentration was 200 mg/L, the decolorization and TOC removal rates of reactive brilliant blue KN-R were 100% and 68.54%, respectively. The kinetics of the reaction was investigated in the range of 120 擄C. The results show that the wet hydrogen peroxide oxidation reaction of reactive brilliant blue KN-R accords with the quasi first-order kinetic equation, and the activation energy of the reaction is 73.9 k J/mol (R20.96). The products of reactive brilliant blue KN-R degraded by WPO were identified by gas chromatography / mass spectrometry (GC-MS). The results showed that the degradation products were mainly small molecular organic acids, such as succinic acid, adipic acid and phthalic acid, which were biodegradable, which indicated that the biodegradability of reactive brilliant blue KN-R was improved after WPO degradation. The mechanism of free radical reaction was studied by adding free radical trapping agent (tert-butanol). The results showed that the existence of free radical trapping agent had a negative effect on the degradation of reactive brilliant blue KN-R by WPO method. After 4 h reaction, the absorbance of the solution at 596 nm increased from 0.00725 to 0.40696, so H_2O_2 produced hydroxyl radical during the reaction. The hydroxyl radical with high reactive activity also participated in the degradation mechanism of reactive brilliant blue KN-R by WPO method.
【學(xué)位授予單位】:湖南大學(xué)
【學(xué)位級(jí)別】:碩士
【學(xué)位授予年份】:2015
【分類號(hào)】:X791

【參考文獻(xiàn)】

相關(guān)期刊論文 前10條

1 戴曉紅;吳贊敏;甕亮;高婷;;微生物對(duì)酸性紅B染料的脫色研究[J];印染助劑;2006年09期

2 景曉輝;蔡再生;;三維電極法降解活性染料廢水[J];印染;2006年14期

3 汪曉軍;林德賢;顧曉揚(yáng);董方;;臭氧-曝氣生物濾池處理酸性玫瑰紅染料廢水[J];環(huán)境污染治理技術(shù)與設(shè)備;2006年07期

4 謝凱娜;吳浩汀;胡曉華;;水解-接觸氧化-混凝工藝處理印染廢水實(shí)例[J];工業(yè)用水與廢水;2006年03期

5 黎載波;王國(guó)慶;;改性雙氰胺-甲醛絮凝脫色劑的制備與應(yīng)用[J];化工環(huán)保;2006年03期

6 李雅婕;王平;;生物技術(shù)在印染廢水處理工藝中的應(yīng)用[J];工業(yè)水處理;2006年05期

7 胡文偉;屠繼延;劉娣;;“流炭法”處理印染廢水[J];印染助劑;2006年02期

8 李海紅,仝攀瑞,郭雅妮;關(guān)于印染工業(yè)污染防治的研究[J];西安建筑科技大學(xué)學(xué)報(bào)(自然科學(xué)版);2005年01期

9 趙偉榮,史惠祥,楊岳平,汪大,

本文編號(hào):2391090


資料下載
論文發(fā)表

本文鏈接:http://sikaile.net/kejilunwen/huanjinggongchenglunwen/2391090.html


Copyright(c)文論論文網(wǎng)All Rights Reserved | 網(wǎng)站地圖 |

版權(quán)申明:資料由用戶cef93***提供,本站僅收錄摘要或目錄,作者需要?jiǎng)h除請(qǐng)E-mail郵箱bigeng88@qq.com
国产一区二区在线免费| 欧美日韩一区二区午夜| 日本不卡在线视频你懂的| 欧美人妻免费一区二区三区| 亚洲一区二区亚洲日本| 91爽人人爽人人插人人爽| 亚洲熟女精品一区二区成人| 麻豆在线观看一区二区| 91免费精品国自产拍偷拍| 欧美日韩精品一区免费 | 久久人人爽人人爽大片av| 国产免费人成视频尤物| 国产欧美韩日一区二区三区| 精品国产日韩一区三区| 亚洲最新的黄色录像在线| 久久精品福利在线观看| 久久国产亚洲精品成人| 日韩在线视频精品视频| 91精品国产综合久久福利| 精品一区二区三区中文字幕| 久久亚洲国产视频三级黄| 精品人妻少妇二区三区| 色婷婷人妻av毛片一区二区三区| 亚洲视频一区自拍偷拍另类| 三级理论午夜福利在线看| 少妇特黄av一区二区三区| 午夜福利92在线观看| 99久久免费看国产精品| 久久老熟女一区二区三区福利| 午夜精品一区二区三区国产| 好吊色免费在线观看视频| 国产一区二区三中文字幕| 黄片美女在线免费观看| 免费在线播放不卡视频| 久久经典一区二区三区| 欧美在线观看视频免费不卡| 九九热精品视频在线观看| 日韩色婷婷综合在线观看| 亚洲天堂一区在线播放| 欧美同性视频免费观看| 在线播放欧美精品一区|