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استفادۀ همزمان فرایندهای فنتون و الکتروشیمیایی برای کاهش بار آلی لجن مازاد بیولوژیکی | ||
| محیط شناسی | ||
| مقاله 14، دوره 40، شماره 1، اردیبهشت 1393، صفحه 177-188 اصل مقاله (629.94 K) | ||
| نوع مقاله: مقاله پژوهشی | ||
| شناسه دیجیتال (DOI): 10.22059/jes.2014.50165 | ||
| نویسندگان | ||
| گاگیک بدلیانس قلی کندی* 1؛ حمیدرضا مسیحی2؛ مریم میرابی3 | ||
| 1دانشیار مهندسی محیط‌زیست،آب و فاضلاب، دانشگاه شهید بهشتی، پردیس فنی مهندسی شهید عباسپور | ||
| 2کارشناس ارشد مهندسی عمران، آب و فاضلاب، دانشگاه شهید بهشتی، پردیس فنی مهندسی شهید عباسپور | ||
| 3استادیار مهندسی محیط‌زیست، آب و فاضلاب، دانشگاه شهید بهشتی، پردیس فنی مهندسی شهیدعباسپور | ||
| چکیده | ||
| با ارائۀ راهکارهای فراوان در راستای ارتقای سامانه‌های تثبیت لجن مازاد بیولوژیکی در چند دهة گذشته، این موضوع همچنان مورد توجه ویژة بسیاری از متخصصان مربوطه است. در این تحقیق، بر اساس نتایج بررسی‌‌های اولیه در خصوص قابلیت و مشکلات عملکردی روش‌های فنتون و الکتروشیمیایی در مقیاس آزمایشگاهی، به کارگیری سامانة ترکیبی (همزمان) روش فنتون- الکتروشیمیایی و پارامترهای مؤثر در عملکرد سامانة آزمایشگاهی مزبور شامل نسبت آهن به پراکسیدهیدروژن، مقدار pH، مدت زمان ماند، غلظت پراکسیدهیدروژن، شدت جریان و غلظت آهن باقیمانده بررسی شد. همچنین، بررسی مقایسهای عملکرد روش فنتون با روش ترکیبی فنتون- الکتروشیمیایی انجام گرفت. مطابق نتایج و بررسی‌‌های انجام‌شده بهترین نسبت غلظت آهن به پراکسیدهیدروژن برابر 58/0، مقدار بهینة pH برابر 1/3، بیشترین مدت زمان ماند 6 ساعت با غلظت پراکسیدهیدروژن برابر mg/L1568 و شدت جریان mA650- 750 برای حذف بهینة VSSحاصل شد. همچنین، با توجه به نتایج حاصل میتوان گفت که افزایش کارامدی حذف VSS دارای همبستگی تصاعدی با میزان مصرف انرژی است. با توجه به اهمیت بسزای استفادة مجدد از لجن حاصل به ویژه کشاورزی، غلظت آهن باقیمانده نیز بررسی شد. در این خصوص با افزایش غلظت آهن ورودی به سامانة آزمایشی، افزایش غلظت آهن در لایة لجن قابل مشاهده است. بررسی مقایسهای سرعت تجزیۀ مواد آلی در سامانة ترکیبی به مراتب (حدود 3 برابر) بیشتر است. بنابراین، میتوان گفت گزینة فنتون- الکتروشیمیایی از بسیاری جوانب، راهکار مناسبی برای ارتقای عملکرد فرایند حذف VSS و کاهش بار آلی لجن مازاد بیولوژیکی است. | ||
| کلیدواژه‌ها | ||
| تصفیة فاضلاب شهری؛ روش فنتون و الکتروشیمیایی؛ کاهش بار آلی لجن؛ لجن مازاد بیولوژیکی | ||
| عنوان مقاله [English] | ||
| Simultaneous Application of Fenton – Electrochemical Reactor for Removal of Organic Loading in Biological Waste Sludge | ||
| نویسندگان [English] | ||
| Gagik Badalians Gholikandi1؛ Hamidreza Masihi2؛ Maryam Mirabi3 | ||
| 1Associate Professor of Environmental Engineering, Water and Wastewater, Shahid Beheshti University, A.C., Tehran, Iran | ||
| 2Master of Science in Civil Engineering, Water and Wastewater, Shahid Beheshti University, A.C., Tehran, Iran | ||
| 3Assistant Professor of Environmental Engineering - Water and Wastewater - Shahid Beheshti University, A.C., Tehran, Iran | ||
| چکیده [English] | ||
| Introduction Wastewater treatment using activated sludge process (ASP) produces huge amounts of sludge that must be treated by efficient methods. Wastewater sludge handling is one of the most important economic-technical challenges of wastewater treatment projects. Conventional methods for this purpose are very time consuming, expensive and in lots of cases have limited success. In recent years the electrochemical oxidation techniques have been progressively used for water and wastewater treatment process. Many reports showed that these methods are very effective to eliminate or decrease the organic loading content of wastewater and sludge. Combination of electrochemical reactions and Fenton process has widely been studied for the destruction of organics and bio-refractory pollutants contained in industrial wastewater by highly oxidative hydroxyl radicals formed from reaction of H2O2 with Fe2+. This method offers more advantages than the chemical Fenton process due to the high efficiency of Fenton reagents (e.g., H2O2) utilization and lower retention time. The integrated Fenton and electrochemical reactor were used to reduce concentration of volatile suspended solids in sludge. High consumption rate of divalent iron ions is one of the disadvantages of Fenton method compared with its reduction. In this research, the electrochemical method has been used to solve this problem. The electrochemical method increases the reduction rate of divalent iron by converting the trivalent iron ions into the bivalent ones and it reduces the production of iron sludge. In this research, the effective parameters including ratio of iron to hydrogen peroxide, pH, retention time, concentration of hydrogen peroxide and the amount of electric current were investigated. Materials and methods In the present study we have evaluated the efficiency of Fenton-Electrochemical process in reduction of organic contents of Secondary Sludge of Mahallati ASP wastewater treatment plant. This plant is located in Tehran, with treatment capacity of 4800m3 per day and operates in extended aeration process. Table 1 shows the specifications of the investigated sludge. Our reagents were H2O2 and Fe2+. The evaluated Fenton-Electrochemical reactor has been shown in figure1. The reactor contains two grafit anodes and two grafit cathods. The electrodes dimentions were 1mm*140mm*60mm, and the distance between them is 1.5 cm. The volume of reactor has been selected 0.9 L. We used the mechanical mixer instead of electromagnetic stirer because of the sensitivity of Fe2+ ions to electromagnetic materials. The temperature during the test was between 13.8 and 15.6 ˚C. All tests were conducted according to standard methods (APHA, 1999) and each part of experiments was repeated three times. property Value pH 6.53-7.33 Temperature(˚C) 13.8-15.6 COD (mg/lit) 6051-11164 VSS ( mg/lit) 3536-7782 VS ( mg/lit) 4086-8382 TSS (mg/lit) 4088-8432 VSS/TSS 0.86-0.92 Figure 1. the evaluated EF reactor Table 1. Investigated Sludge Specifications Result and discution The removal of volatile suspended solids (VSS) as the efficiency factor haveevaluted the effects of the ration of Fe2+ concentration on H2O2 concentration ( [Fe2+]/[ H2O2]), time, pH, H2O2 concentration and current density as the effective process operation parameters. To obtain the most efficient we have investigated the operational parameter serily. The firest parameter that is studied is [Fe2+]/[ H2O2] . Figure 2 showes the effect of [Fe2+]/[ H2O2] to removal of VSS. Regarding to the diagram, the removal of VSS increases sharply as [Fe2+]/[ H2O2] increases to 0.58 (optimum point) and reach its maximum in this point and is constant to about 1.015 and then decreases slightly. The second parameter is pH. It has been studied in the optimum point of [Fe2+]/[ H2O2]. Adjustment of pH has been done by 98% sulfuric acid. Figure 3 shows that the removal of VSS is constant by increasing the pH up to 3, and then starts to decrease. The maximum VSS removal (approximately 72%) was attained in pH=3.1. Oxidation efficiency essentially decreases at pH values lower than 3. Figure 4 shows the relation of VSS removal and time. The time was assessed in the maximum point of the last two parameters. According to the diagram, the VSS removal increases by time and reaches its maximum in approximately 6 hours and then is constant. Figure 2. VSS removal and [Fe2+]/[ H2O2] relationship Fig.3: VSS removal and pH relationship Fig.4: VSS removal and time relationship In order to attain the best concentration of Fe2+ and H2O2, we studied the effect of H2O2 concentration on VSS removal. The optimum ratio of [Fe2+]/[ H2O2] can be attained from figure2. Fe2+concentration are also resulted by determining the optimum H2O2 concentration. The tests carried out in the most effective point of prior parameters and the results has been shown in figure 5. According to the diagram, the highest VSS removal was obtained when the H2O2 concentration is approximately 1568mg/L. Finally, after determining the optimum point for ( [Fe2+]/[ H2O2]), detention time, pH, H2O2 concentration, and the effect of Current density was evaluated. Current density improves the reduction of trivalent iron to divalent iron, i.e., it enhances the efficiency of Fenton process. According to figure 6, the maximum VSS removal has been reached in (650-750) mA current density. The remained Fe2+ concentration has also been investigated. As shawn in the figure 7, approximately (40-70)% of inserted [Fe2+] adsorbed on the electrodes, (7-15)% was remained in the sludge layer and (23-45)% in the sludge liquor. Figure 5. VSS removal and [ H2O2] relationship Figure 6. VSS removal and current density relationship Figure 7. Remained and consumed [ Fe2+]relationship Fenton and electrochemical-Fenton were compared on an equal basis. According to the figure 8, the efficiency of electrochemical-Fenton is 76%, while the efficiency of Fenton is 22%. Figure 9 shows the current density of energy consumption. By increasing the current density rate, energy consumption increases exponentially. Figure 8. VSS removal efficiency of Fenton and Fenton-electrochemical regarding detention time Figure 9. Current density of energy consumption in Fenton- electrochemical Conclusions Even if in the recent decades many efforts have been done in order to enhance usual sludge treatment or commence novel more efficient methods, lots of researches have focused on techno-economical issues carefully. The key purpose of the researches is to eliminate the organic load of sludge and improve its quality in order to be reused in various applications like fertilizer in agriculture. In this study we have evaluated a combined Fenton-Electrochemical process with the aim of stabilizing excessive biological sludge of municipal wastewater treatment plant. For this purpose, several determining parameters have been selected and investigated in a lab-scale pilot. The results showed that the system has preserved its stability in a wide range of pH (3-7), also the organic load of the sludge decreased noticeably (maximum decreasing efficiency of the sludge was approximately 81%). Comparison of the results of Fenton or other usual systems and combined Fenton-Electrochemical process showed that the later system is appropriate and efficient method to get better quality of stabilized sludge and operational conditions. | ||
| کلیدواژه‌ها [English] | ||
| biological waste sludge, fenton– electrochemical method, organic loading reduction, Wastewater treatment | ||
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