999精品在线视频,手机成人午夜在线视频,久久不卡国产精品无码,中日无码在线观看,成人av手机在线观看,日韩精品亚洲一区中文字幕,亚洲av无码人妻,四虎国产在线观看 ?

Photocatalytic Treatment of Waste Water from Rice Husk Alkaline Hydrolysate

2019-07-12 12:56:56OlgaArefievaMarinaVasilyevaEkaterinaErmolenkoAnastasiiaBychkova
Rice Science 2019年4期

Olga D. Arefieva, Marina S. Vasilyeva, Ekaterina V.Ermolenko, Anastasiia V.Bychkova

?

Photocatalytic Treatment of Waste Water from Rice Husk Alkaline Hydrolysate

Olga D. Arefieva1, 2, Marina S. Vasilyeva1, 2, Ekaterina V.Ermolenko3, Anastasiia V.Bychkova1

(Far Eastern Federal University, Vladivostok 690950, Russian Federation; Institute of Chemistry, Far-Eastern Branch, Russian Academy of Sciences, Vladivostok 690022, Russian Federation; )

SUMMARY We carried out photocatalytic treatment of a lignin-free solution of rice husk alkaline hydrolysate [pH of 2, chemical oxygen demand (COD) of 12.8 g/L] using photo-Fenton process in the ultraviolet (UV, wavelength of 365 nm) and visible spectrum. Oxidation of lignin was performed at a constant mass ratio of COD:H2O2as 1:2 and Fe2+concentration of 80 mg/L. It was established that for the destruction of alkaline lignin, exposure to visible or UV radiation was necessary. Decolorization efficiency of a lignin-free solution depends on the dilution rate of the solution. The advanced oxidative photo-Fenton process (UV/Н2О2/Fe2+) made it possible to reduce the color of lignin-free solution at a dilution ratio of 1:5 by94% of decolorization efficiency, 87% of phenolic compound and 79% of COD. With the help of gas chromatography, the products of lignin destruction were low-toxic and usable.

In the recent years, there have been many proposals in the literature for involving non-wood plant raw materials (multi-tonnage agricultural crops of annual plants such as flax, kenaf, hemp, rice, oats and others) into the production of fibrous materials. Huge renewable waste generated in the production of rice cereals has long attracted the attention of researchers in different countries as a source of fibrous materials and a number of chemicals (Sarkar et al, 2017). But in the production of fibrous products, large volumes of waste water andalkaline hydrolysates, which contain mineral components, lignin, polysaccharides, low molecular weight resinous substances and others, are formed.

A number of studies showed that lignin-containing biomass (plant waste) can be processed by oxidative degradation in the presence of a multifunctional environmentally friendly catalyst based on Fe3+oxides(Amat et al, 2005; Xu et al, 2007; Sevimlia et al, 2014). As an oxidizing agent, it is possible to use Н2О2and/or air oxygen (Kasaikina et al, 2012; Lesin et al, 2012). Thus, oxidative processes using hydrogen peroxide and iron compounds are of interest for the treatment of lignin-containing waste water and processing of lignin-containing plant material (Catalkaya and Kargi, 2007; Lucas et al, 2012). The goal of this work is to choose the conditions for the effective oxidation of lignin in lignin-free solution of rice husk alkaline hydrolysates using photo-Fenton process in the ultraviolet (UV, wavelength of 365 nm) and visible (VIS) spectrum with the Fenton (in dark) process as the control (Pérez et al, 2002; Ahmaruzzaman and Gupta, 2011).

The husk of rice variety Krasnodar Krai was chose for the research. The experiments were carried out with a lignin-free solution that was obtained from the silica-free solution when the pH was changed to 2, while the alkaline lignin with a higher molecular weight precipitates, and the solution retains a low molecular weight soluble lignin [chemical oxygen demand (COD) of 12.8 g/L]. The process was carried out at a constant mass ratio of COD:H2O2as 1:2, and Fe2+concentration of 80 mg/L. Fig. 1 presents the decolorization efficiency of the lignin-free solution with a dilution ratio of 1:10 and 1:5. The results showed that at a higher dilution multiplicity of the solution (1:10), decolorization efficiency is lower, which is possibly connected with an increase in the pH value to 3 when the solution is diluted (Fig. 1). It is known that with increasing pH, alkaline lignin dissolves and the color of the initial solution increases (Minu et al, 2012). Using only Fenton’s reagent (experiment in the dark) leads to negative values of the decolorization efficiency (Fig. 1).

Fig. 1.Decolorization efficiency of lignin-free solution with a dilution ratio of 1:10 and 1:5 in photo-Fenton and Fenton conditions.

We observed the change in the optical density of the lignin-free solutions at different dilution rates when exposed to light for 10 d after irradiation in the UV region for 3 h. Fig. 2-A shows that after UV irradiation, decolorization efficiency sharply increases, but varies insignificantly in the visible spectrum between the dilution ratio of 1:10 and 1:5.And it reaches 86% at 10 d (240 h) with a dilution ratio of 1:10, and 94% at a dilution ratio of 1:5. Fig. 2-B shows kinetic curve of the decolorization efficiency change of the lignin-free solution in the UV and VIS spectrum for 3 h, and subsequent oxidation of lignin in the VIS spectrum for 10 d (240 h). For 3 h of irradiation, the decolorization efficiency in the UV spectrum increases, while in the VIS spectrum it has a negative value, which indicates the formation of organic substances with stronger chromophore groups in the solution as a result of the destruction of lignin. Further, the process of lignin destruction in the VIS spectrum proceeds quite intensively and on the 4th day (96 h), the kinetic curves of decolorization efficiency had no change in the UV and VIS spectrum. The decolorization efficiency of the lignin-free solution stabilizes and reaches 94%. The presence of UV or VIS radiation in the Fenton system made it possible to achieve a high degree of decolorization. The presence of the UV spectrum leads to an increase in the initial rate of the decomposition of alkaline lignin, apparently associated with the formation of more hydroxyl radicals. Evaluation of the destruction is also carried out by COD and phenolic equivalent (Fig. 2-C and -D).The kinetic curves of the change of COD and the content of phenolic compounds in the UV and VIS spectrum are similar.After 3 h of irradiation, the parameters are significantly reduced and the process continues steadily. On the 10th day (240 h), the removal efficiency of phenolic compounds from solution is 87%, while that of COD is 79%. Experiments in the dark have shown that the degree of decolonization reaches only 22% (Fig. 2-A and -B). COD values are practically unchanged (Fig. 2-C), while the content of phenolic compounds is reduced to 42.3% (Fig. 2-D). The results show that the oxidation of the alkaline lignin in dark practically does not occur, and it is therefore necessary to expose to the UV or VIS irradiation.

The color of the solution diluted five times, after oxidation in the UV and visible spectral spectrum, practically reaches the regulatory requirements, while the COD value of the solution does not meet the regulatory requirements (Table 1). However, undissolved organic substances remain in the solution, as evidenced by high values of COD solutions (550–540 mg/L).

Table 1. Characterization of lignin-free solution before and after oxidative degradation.

Table 2. Extract components identified by chromatographic-mass spectrometric analysis.

UV and VIS represent the ultraviolet (wavelength of 365 nm) and visible spectrum.

MPC, Maximum permissible concentration; ‘+’ means presence in extract; ‘–’ means absence in extract.

The composition of organic compounds after the destruction of lignin-free solution using the photo-Fenton process in the UV and VIS spectrum is almost the same. The resulting aqueous solution contains low molecular weight oxidation products of lignin-aromatic hydrocarbons and carboxylic acids (Table 2). The resulting low-molecular products are mainly low-toxic and have biological activity (antiseptic, insecticidal, fungicidal, antibiotic and other properties). The standards for reservoirs of cultural, domestic and domestic-drinking purposes were established for only three compounds.

It should be noted that the concentration of residual iron in solution exceeds the normative value for water objects for domestic and drinking purposes. Such waste water is not allowed to be discharged into water bodies or transferred to urban sewage systems (Vidal et al, 2001; Raj et al, 2007). Iron is a biologically active element, and it is necessary for plants to form chlorophyll (Khataee et al, 2014). Therefore, considering that biologically active organic compounds and iron cations remain in the solution formed after lignin oxidation, it can be used after additional studies.

Thus, this study showed the possibility of using the photo-Fenton process for the destruction of lignin in lignin-free solutions of rice husk alkaline hydrolysates. It was established that the decolorization efficiency of lignin-free solution depends on the dilution rate of the solution. At a dilution ratio 1:5 (COD:H2O2as 1:2), the decolorization efficiency was 94%. It is shown that the action of the VIS or UV irradiation is necessary to destroy alkaline lignin. Under photo-Fenton process (UV/Н2О2/Fe2+), the removal efficiency of phenolic compounds is 87%, and that of COD is 79%. With the help of gas chromatography, the products of lignin destruction, which are low-toxic, can be applied, for example, as antiseptic agents.

SUPPLEMENTAL DATA

The following material is available in the online version of this article at http://www.sciencedirect.com/science/journal/16726308; http://www.ricescience.org.

Supplemental File 1. Materials and methods used in this study.

Ahmaruzzaman M, Gupta V K. 2011. Rice husk and its ash as low-cost adsorbents in water and wastewater treatment., 50: 13589–13613.

Amat A M, Arques A, Miranda M A, López F. 2005. Use of ozone and/or UV in the treatment of effluents from board paper industry., 60(8): 1111–1117.

Catalkaya E C, Kargi F. 2007. Color, TOC and AOX removals from pulp mill effluent by advanced oxidation processes: A comparative study., 139(2): 244–253.

Kasaikina O T, Pisarenko L M, Lesin V I. 2012. Colloidal catalysts based on iron(III) oxides: 2. Features of catalyzed palm oil oxidation., 74(4): 483–488.

Khataee A, Vahid B, Behjati B, Safarpour M, Joo S W. 2014. Kinetic modeling of a triarylmethane dye decolorization by photoelectro-Fenton process in a recirculating system: Nonlinear regression analysis., 92(2): 362–367.

Lesin V I, Pisarenko L M, Kasaikina O T. 2012. Colloidal catalysts based on iron(III) oxides: 1. Decomposition of hydrogen peroxide., 74(1): 85–90.

Lucas M S, Peres J A, Amor C, Prieto-Rodríguez L P, Maldonado M I, Malato S. 2012. Tertiary treatment of pulp mill wastewater by solar photo-Fenton., 225/226: 173–181.

Minu K, Jiby K Kurian, Kishore V V N. 2012. Isolation and purification of lignin and silica from the black liquor generated during the production of bioethanol from rice straw., 39(4): 210–217.

Pérez M, Torrades F, Garcia-Hortal J A, Domenech X, Peral J. 2002. Removal of organic contaminants in paper pulp treatment effluents under fenton and photo-Fenton conditions., 36(1): 63–74.

Raj A, Reddy M M K, Chandra R. 2007. Decolourisation and treatment of pulp and paper mill effluent by lignin-degrading, 82(4):399–406.

Sarkar P, Moyez S A, Dey A, Roy S, Das S K. 2017. Experimental investigation of photocatalytic and photovoltaic activity of titania/rice husk crystalline nano-silica hybrid composite., 172: 93–98.

Sevimlia M F, Deliktas E, Sahinkay S, Guclu D. 2014. A comparative study for treatment of white liquor by different applications of Fenton process., 7(6): 1116–1123.

Vidal G, Videla S, Diez M C. 2001. Molecular weight distribution ofkraft mill wastewater treated by anaerobic digestion., 77(2): 183–191.

Xu M J, Wang Q S, Hao Y L. 2007. Removal of organic carbon from wastepaper pulp effluent by lab-scale solar photo-Fenton process., 148:103–109.

12 August 2018;

29 October 2018

Olga D. Arefieva (arefeva.od@dvfu.ru)

Copyright ? 2019, China National Rice Research Institute. Hosting by Elsevier B V

This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/)

Peer review under responsibility of China National Rice Research Institute

http://dx.doi.org/10.1016/j.rsci.2018.10.008

(Managing Editor: Wang Caihong)

主站蜘蛛池模板: 亚洲精品午夜无码电影网| 国产精品粉嫩| 国产精品大白天新婚身材| 综合网久久| 亚洲男人天堂2020| 热re99久久精品国99热| 精品久久久久成人码免费动漫| 在线不卡免费视频| 亚洲精品视频网| 91视频国产高清| 国产乱子伦精品视频| 成人毛片在线播放| www.91在线播放| 一级毛片基地| 伊人久久婷婷| 日本午夜在线视频| a级高清毛片| 手机成人午夜在线视频| 2020国产在线视精品在| 国产资源站| 欧美天堂在线| 精品久久人人爽人人玩人人妻| 欧美高清视频一区二区三区| av在线无码浏览| 一本色道久久88亚洲综合| 91精品国产一区自在线拍| 国产在线精品网址你懂的| 欧美成人精品一级在线观看| 丰满少妇αⅴ无码区| 日本人妻一区二区三区不卡影院 | 永久在线精品免费视频观看| 欧美精品在线视频观看 | 国产在线视频福利资源站| 免费看的一级毛片| 亚洲欧美色中文字幕| 在线中文字幕网| 亚洲第一色网站| 1769国产精品免费视频| 久久精品电影| 波多野结衣一区二区三区AV| 全免费a级毛片免费看不卡| 全部毛片免费看| 国产精品久久自在自线观看| 国产传媒一区二区三区四区五区| 人人澡人人爽欧美一区| 日本国产一区在线观看| 国产成人精品免费视频大全五级| 国产精品视频猛进猛出| 国产成年无码AⅤ片在线| 91久久精品日日躁夜夜躁欧美| 精品第一国产综合精品Aⅴ| 日韩午夜伦| 精品国产欧美精品v| 2021亚洲精品不卡a| 日本午夜精品一本在线观看| swag国产精品| 国产无码精品在线播放| 婷婷综合亚洲| 亚洲最新地址| 亚洲无限乱码| 狠狠亚洲婷婷综合色香| 精品久久久无码专区中文字幕| 99视频全部免费| 99在线观看免费视频| 久久久久人妻精品一区三寸蜜桃| 97色婷婷成人综合在线观看| 日本免费一区视频| 少妇高潮惨叫久久久久久| 人人爱天天做夜夜爽| 久久永久视频| 午夜人性色福利无码视频在线观看| 爱爱影院18禁免费| 色综合久久久久8天国| 国产在线欧美| 香蕉久久永久视频| 久久这里只有精品8| 欧美亚洲日韩不卡在线在线观看| 欧美视频二区| 99re精彩视频| 青青网在线国产| 91区国产福利在线观看午夜| 亚洲色图欧美|