Batik Wastewater Treatment Using Simultaneous Process of Electrocoagulation and Electro-Assisted Phytoremediation (EAPR)

https://doi.org/10.22146/ijc.47898

Rudy Syah Putra(1*), Aprilia Dwi Annisa(2), Sigit Budiarjo(3)

(1) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Universitas of Islam Indonesia, Jl. Kaliurang km. 14, Yogyakarta 55584, Indonesia
(2) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Universitas of Islam Indonesia, Jl. Kaliurang km. 14, Yogyakarta 55584, Indonesia
(3) Department of Chemistry, Faculty of Mathematics and Natural Sciences, Universitas of Islam Indonesia, Jl. Kaliurang km. 14, Yogyakarta 55584, Indonesia
(*) Corresponding Author

Abstract


The aims of the study are to identify the effectiveness of wastewater treatment from the Batik industry using a simultaneous of electrocoagulation (EC) and electro-assisted phytoremediation (EAPR). Rough horsetail (Equisetum hyemale) was used as an accumulator plant in the EAPR system. Electrocoagulation was conducted for 1 h at a constant voltage of 20 V in 10 L solution, while EAPR was processed for 7 day at a constant voltage of 5 V in 17 L solution. The chemical oxygen demand (COD) of water was determined by closed reflux of colorimetric methods and heavy metal concentration was determined by flame-atomic absorption spectrophotometer. The results showed that the COD decreased by 69.6% after 1 h of electrocoagulation process and up to 80.9% after the EAPR process. The concentration of Cr and Pb decreased as much as 25% and 8.52%, respectively in the similar process. The simultaneous process could extend the heavy metal removal up to 0.28 mg/L for Cr and 0.09 mg/L for Pb in liquid wastewater from the initial concentration. These results showed that the levels of COD and heavy metal concentration in Batik wastewater have reduced in accordance with the Ministry of Environment Decree No. 5/2014 Republic of Indonesia regarding various industries wastewater standard with the threshold limit of 150 mg/L for COD and 1.0 mg/L for Cr on textile industry and 0.1 mg/L for Pb on Class I for another wastewater standard. The estimated cost of operation was US$ 1.509 m–3 indicating the viability of Batik industry wastewater treatment.


Keywords


electrocoagulation; EAPR; Equisetum hyemale; phytoremediation; batik wastewater

Full Text:

Full Text PDF


References

[1] Wardhana, W.A., 2001, Dampak Pencemaran Lingkungan, Andi Offset, 10–12.

[2] Pereira, L., and Alves, M., 2012, “Dyes-Environmental impact and remediation” in Environmental Protection Strategies for Sustainable Development, Eds. Malik, A., and Grohmann, E., Springer, Netherlands, 111–162.

[3] Jiang, J.Q., Graham. N., André, C., Kelsall, G.H., and Brandon, N., 2002, Laboratory study of electrocoagulation-flotation for water treatment, Water Res., 36 (16), 4064–4078.

[4] Smoczyński, L., Kalinowski, S., Ratnaweera, H., Kosobucka, M., Trifescu, M., and Pieczulis-Smoczyńska, K., 2017, Electrocoagulation of municipal wastewater - A pilot-scale test, Desalin. Water Treat., 72, 162–168.

[5] Adegoke, A.T., and Abayomi, E.T., 2020, A preliminary study on the treatment of restaurant wastewater using electrocoagulation technique, J. Degrade. Min. Land Manage., 7 (2), 2029–2033.

[6] El-Taweel, Y.A., Nassef, M.E., Elkheriany, I., and Sayed, D., 2015, Removal of Cr(VI) ions from wastewater by electrocoagulation using iron electrode, Egypt. J. Pet., 24 (2), 183–192.

[7] Butler, E., Hung, Y.T., Yeh, R.Y.L., and Al Ahmad, M.S., 2011, Electrocoagulation in wastewater treatment, Water, 3, 495–525.

[8] Barrera-Díaz, C., Linares-Hernández, I., Roa-Morales, G., Bilyeu, B., and Balderas-Hernández, P., 2009, Removal of biorefractory compounds in industrial wastewater by chemical and electrochemical pretreatments, Ind. Eng. Chem. Res., 48 (3), 1253–1258.

[9] Raskin, I., 2000, Phytoremediation of Toxic Metals: Using Plants Clean Up the Environment, Eds. Raskin, I., and Ensley, B.D., Wiley, New York.

[10] Terry, N., and Banuelos G.S., Phytoremediation of Contaminated Soil and Water, Lewis Publisher, Boca Raton.

[11] Hodko. D., Van Hyfte. J., Denvir A., and Magnuson, J.W., 2000, Methods for enhancing phytoextraction of contaminants from porous media using electrokinetic phenomena, US Patent No. 6145244A.

[12] Putra. R.S., Ohkawa, Y., and Tanaka, S., 2013, Application of EAPR system on the removal of lead from sandy soil and uptake by Kentucky bluegrass (Poa pratensis L.), Sep. Purif. Technol., 102, 34–42.

[13] O`Connor, C.S., Lepp, N.W., Edwards, R., and Sunderland, G., 2003, The combined use of electrokinetic remediation and phytoremediation to decontaminate metal-polluted soils: a laboratory-scale feasibility study, Environ. Monit. Assess., 84, 141–158.

[14] Aboughalma, H., Bi, R., and Schlaak, M., 2008, Electrokinetic enhancement on phytoremediation in Zn, Pb, Cu, and Cd contaminated soil using potato plants, J. Environ. Sci. Health. Part A Environ. Sci. Health Part A Environ. Sci. Eng., 43 (8), 926–933.

[15] Zhou D.M., Chen, H.F., Cang, L., and Wang, Y.J., 2007, Ryegrass uptake of soil Cu/Zn by EDTA/EDDS together with a vertical direct-current electrical field, Chemosphere, 67 (8), 1671–1676.

[16] Bi, R., Schlaak, M., Siefert, E., Lord, R., and Connolly, H., 2011, Influence of electrical fields (AC and DC) on phytoremediation of metal polluted soils with rapeseed (Brassica napus) and tobacco (Nicotiana tabacum), Chemosphere, 83 (3), 318–326.

[17] Kubiak, J.J., Khankhane, P.J., Kleingeld, P.J., and Lima, A.T., 2012, An attempt to electrically enhance phytoremediation of arsenic contaminated water, Chemosphere, 87 (3), 259–264.

[18] Putra, R.S., Cahyana, F., and Novarita, D., 2015, Removal of lead and copper from contaminated water using EAPR system and uptake by water lettuce (Pistia stratiotes L.), Procedia Chem., 14, 381–386.

[19] Putra, R.S., Novarita, D., and Cahyana, F., 2016, Remediation of lead (Pb) and copper (Cu) using water hyacinth (Eichornia crassipes (Mart.) Solms) with electro˗assisted phytoremediation (EAPR), AIP Conf. Proc., 1744, 020052.

[20] Khalik, W.F., Ho, L.N., Ong, S.A., Wong, Y.S., Yusoff, N.A., and Ridwan, F., 2015, Decolorization and mineralization of Batik wastewater through the solar photocatalytic process, Sains Malays., 44 (4), 607–612.

[21] Şahinkaya, S., 2013, COD and color removal from synthetic textile wastewater by ultrasound assisted electro-Fenton oxidation process, J. Ind. Eng. Chem., 19 (2), 601–606.

[22] Holkar, C.R., Jadhav, A.J., Pinjari, D.V., Mahamuni, N.M., and Pandit, A.B., 2016, A critical review on textile wastewater treatments: Possible approaches, J. Environ. Manag., 182, 351–366.

[23] Kabdaşli, I., Arslan-Alaton, I., Ölmez-Hancı, T., and Tünay, O., 2012, Electrocoagulation applications for industrial wastewaters: a critical review, Environ. Technol. Rev., 1 (1), 2–45.

[24] Anonymous, 2009, Air dan air limbah – Bagian 2: Cara uji kebutuhan oksigen kimiawi (Chemical Oxygen Demand/COD) dengan refluks tertutup secara spektrofotometri, SNI 6989.2, Badan Standarisasi Nasional (BSN), Indonesia.

[25] Moran, R., and Porath, D., 1980, Chlorophyll determination in tissue using N,N-dimethylforamide, Plant Physiol., 65 (3), 478–479.

[26] Kobya, M., Demirbas, E., and Akyol, A., 2009, Electrochemical treatment and operating cost analysis of textile wastewater using sacrificial iron electrodes, Water Sci. Technol., 60 (9), 2261–2270.

[27] da Mota, I.O., de Castro, J.A., Casqueira, R.G., and de Oliveira Junior, A.G., 2015, Study of electroflotation method for treatment of wastewater from washing soil contaminated by heavy metals, J. Mater. Res. Technol., 4 (2), 109–113.

[28] Geraldino, H.C.L., Simionato, J.I, de Souza Freitas, T.K.F., Garcia J.C., de Carvalho Júnior, O., and Correr, C.J., 2015, Efficiency and operating cost of electrocoagulation system applied to the treatment of dairy industry wastewater, Acta Sci. Technol., 37(3), 401-408.

[29] Tangahu, B.V., and Putri, A.P., 2017, The degradation of BOD and COD of Batik industry wastewater using Egeria densa and Salvinia molesta, JSTL, 9 (2), 82–91.

[30] Tangahu, B.V., Ningsih, D.A., Kurniawan, S.B., and Imron, M.F., 2019, Study of BOD and COD removal in batik wastewater using Scirpus grossus and Iris pseudacorus with intermittent exposure system, J. Ecol. Eng., 20 (5), 130–134.

[31] Viehweger, K., 2014, How plants cope with heavy metals, Bot. Stud., 55 (1), 35.

[32] Shahandeh, H., and Hossner, L.R., 2000, Plant screening for chromium phytoremediation, Int. J. Phytorem., 2 (1), 31–51.

[33] Kale, R.A., Lokhande, V.H., and Ade, A.B., 2015, Investigation of chromium phytoremediation and tolerance capacity of a weed, Portulaca oleracea L. in a hydroponic system, Water Environ. J., 29 (2), 236–242.

[34] Aldoobie, N.F., and Beltagi, M.S., 2013, Physiological, biochemical and molecular responses of common bean (Phaseolus vulgaris L.) plant to heavy metals stress, Afr. J. Biotechnol., 12 (29), 4614–4622.

[35] Rastgoo, L., Alemzadeh, A., Tale, A.M., Tazangi, S.E., and Eslamzadeh T., 2014, Effects of copper, nickel and zinc on biochemical parameters and metal accumulation in gouan, Aeluropus littoralis, Plant Knowl. J., 3 (1), 31–38.

[36] Rastgoo, L., and Alemzadeh, A., 2011, Biochemical responses of gouan (Aeluropus littoralis) to heavy metals stress, AJCS, 5 (4), 375–383.

[37] Indrayani, L., 2018, Pengolahan limbah cair industri batik sebagai salah satu percontohan IPAL batik di Yogyakarta, Ecotrophic, 12 (2), 173–184.



DOI: https://doi.org/10.22146/ijc.47898

Article Metrics

Abstract views : 2983 | views : 2973


Copyright (c) 2020 Indonesian Journal of Chemistry

Creative Commons License
This work is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License.

 


Indonesian Journal of Chemistry (ISSN 1411-9420 /e-ISSN 2460-1578) - Chemistry Department, Universitas Gadjah Mada, Indonesia.

Web
Analytics View The Statistics of Indones. J. Chem.