PENGARUH PENAMBAHAN AIR LAUT TERHADAP PERUBAHAN ARUS LISTRIK DAN KEKERUHAN PADA PENGOLAHAN AIR LIMBAH INDUSTRI SECARA ELEKTROKOAGULASI

DOI: https://doi.org/10.32722/pt.v19i3.3503

Sutanto Sutanto

Abstract


In this research, electronics industry waste water has been processed into clean water. The study was conducted by flowing of 4.5 liters of waste water into the three cells of electrocoagulation process tank. Each cell is filled 1.5 liters of waste water without the addition of sea water. The electrocoagulation process is carried out at a voltage of 12 V and interval time for observation the change of current and the turbidity is done every 10 minutes. Subsequently, the same procedure was performed and added the sea water with variation of volume of  5, 10 and 15 mL. Measuring of current was done by amperemeter  and  turbidity by turbidimeter. The best conditions are recommended for use of  10 mL of sea water, 12 volt of voltage and 110 minutes for processing time. Under these conditions the current can be increased from 0.21 A to 1.52 A or equivalent 7.2 times to the initial current and then turbidity can be reduced from  44,10 NTU  to 3.25 NTU NTU  or equivalent to 92.63 %.

Keywords


waste water, electrocoagulation, sea water, electric current, turbidity

References


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Sewage Treatment Using Batch Stirred Tank Electrochemical Reactor. International Journal of ChemTech Research,Vol 3, No. 3.

Amelia, L.R. dkk., 2019. Pengaruh Jenis Elektrolit Support pada

Penurunan Logam Cr dalam Limbah Dengan Menggunakan Metode Elektrokoagulasi. Indo. J. Chem. Sci. Vol. 8,No.2.

. Rezki, M. A. S. dkk., 2019.

Pemanfaatan Air Larutan Garam Sebagai Kabel Penghantar Listrik Pengganti Tembaga. Buletin Ilmiah Sarjana Teknik Elektro, Vol. 01, No. 02.

Rios,K.C.,dkk.2014. Experimental

Design to Measure Escherichia Coli Removal in Water Through Electrocoagulation. International Journal of Electrocemical Science. Vol 9.

Gao, S . , dkk. , 2010. Electro-

Coagulation–Flotation Process for Algae Removal. Journal of Hazardous Materials,Vol. 177, Issues 1–3.

Abdelhay, A., dkk. 2017.Anodic

Oxidation of Slaughterhouse Wastewater on Boron-doped Diamond Process Variables Effect. Water Science & Technology, Vol. 76.

Nguyen, D.D., dkk. 2104. A New

Hybrid Treatment System of Bioreactors and Electrocoagulation for Superior Removal of Organic and Nutrient Pollutants from Municipal Wastewater. Journal of Bioresource Technology.Vol.153.

Wellner,D.B.,dkk.2018. Influence

of Operating Parameters During Electrocoagulation of Sodium Chloride and Sodium Bicarbonate Solutions Using Aluminium Electrodes. Journal of Water Process Engineering, Vol.22.

Brahmia,K.,dkk.2019.Investigation

of electrocoagulation reactor design parameters effect on the removal of cadmium fromsynthetic and phosphate industrial wastewater. Arabian Journal of Chemistry, Vol. 12.

Kowalski, M. S. , dkk. 2019.

Electrocoagulation of wastewater using aluminum, iron, and magnesium electrodes. Journal of Hazardous Materials, Vol. 368.

Prastuti, O.P., 2017. Pengaruh

Komposisi Air Laut dan Pasir Laut Sebagai Sumber Energi Listrik. J. Tek. Kim. Ling., Vol. l1, No 1.

Anglada, A., dkk. 2009.

Contributions of Electrochemical Oxidation to Waste-water Treatment: Fundamentals and Review of Applications. Society of Chemical Industry, Vol. 84..

Karichappan, K., dkk. 2014.

Optimization of Electrocoagulation Process to Treat Grey Wastewater in Bach Mode using Response Surface Methodology. Journal of Environmental Health Science and Engineering, Vol 12, No. 29.

Kumar, N.S., dkk. 2010. Factors

Influencing Arsenic and Nitrate Removal from Drinking Water in a Continuous Flow Electro coagulation (EC) Process. Journal of Hazardous Materials, Vol 173, Issues 1–3.

Shanthi, V., dkk. 2011. Domestic

Sewage Treatment Using Batch Stirred Tank Electrochemical Reactor. International Journal of ChemTech Research,Vol 3, No. 3.


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