HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

16
 REACTION KINETICS AND VALIDITY OF BOD TEST FOR DOMESTIC WASTEWATER RELEASED IN MARINE ECOSYSTEMS REAKSI KINETIK DAN VALIDITAS UJI BOD UNTUK PELEPASAN LIMBAH DOMESTIK DI EKOSISTEM LAUT Hikmat Megandana Master Programme of Environmental Engineering, Ins tit ut Tek nolo gi Ban dung Jl Ga nesha No. 10, Bandung, 40132 E-mail: [email protected]

Transcript of HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

Page 1: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 1/16

REACTION KINETICS AND VALIDITY

OF BOD TEST FOR DOMESTICWASTEWATER RELEASED IN MARINE

ECOSYSTEMS REAKSI KINETIK DAN VALIDITAS UJI

BOD UNTUK PELEPASAN LIMBAH DOMESTIKDI EKOSISTEM LAUT

Hikmat Megandana

Master Programme of Environmental Engineering,Institut Teknologi Bandung

Jl Ganesha No. 10, Bandung, 40132

E-mail: [email protected]

Page 2: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 2/16

INTRODUCTION

Page 3: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 3/16

PURPOSE

Studies were conducted to evaluate the impact of salinity and temperature on biodegradation of 

synthetic organic compound and domesticwastewater commonly discharged into themarine water. This paper presents the findings of BOD exertion of glucose–glutamic acid underspecific salinities expressed in terms of chlorideconcentrations at 20°C and 27°C.

Page 4: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 4/16

METHODOLOGY

Start

Collecting data of BOD in various concentration of chlorideand temperature

Calculating BOD which decrease by the time invarious chloride and temperature

Calculating bioremediation reaction kinetics ofBOD (k) to the reaction time in variousconcentration of chloride and temperature

Analysis and Conclusion

Page 5: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 5/16

MATERIAL

The natural seawater with 35–36 parts per thousand (ppt) of salinity hasabout 20,000 mg/L of chlorides. During present study, the chlorideconcentrations were varied to represent creek, estuaries, and oceanconditions.

The experiments were conducted for a 10-day period to achievemaximum exertion of carbonaceous BOD.

To study the BOD exertion pattern under various salinities, the glucose–glutamic acid solution was selected as “test samples.” 

In view of the fact that BOD exerted at 20°C for 5 days is equivalent tothe BOD at 27°C for 3 days (CPCB 1991)  Central Pollution Control Board,,

temperatures of 20°C and 270 C were considered for incubation. Theincubated samples at various time slots were analyzed for the existenceand adequacy of heterotrophic microorganisms under various chlorideconcentrations using Zobel/nutrient agar media

Page 6: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 6/16

FORMULA

A first-order BOD decay equation has been widelyapplied to describe the degradation rate of carbona-ceous organic matter for most of the municipal waste.

The BOD curve can be described by a first-orderkinetics equation (Metcalf dan Eddy, Inc. 2003).

Dimana :

y Amount of oxygen consumed (or BOD) at time t

t Time elapsed since the start of the assay

L0 Total amount of oxygen consumed in the reaction

k Reaction constant

d Lo/dt = - k  Lo y =  Lo (1-10-k t /2.303)

Page 7: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 7/16

RESULT AND DISCUSSION

1. Percent exertion of BOD for glucose–glutamic acid solution at various chloride

concentrations at 20°C

Page 8: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 8/16

2. Percent exertion of BOD for glucose–glutamic acid solution at various chloride

concentrations at 27°C27o C

Page 9: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 9/16

BOD exertion was 10% to 15% higher at 27°C as comparedto 20°C.

BOD decreased with increase in chloride concentration

thereby indicating the negative impact of chlorides on theoxidation of carbonaceous matter.

Huge increase in oxidation of glucose–glutamic acid anddomestic wastewater at 27°C was observed as compared to20°C emphasizing the important role of temperature.

Sudden rise in BOD exertion was not observed after thesixth or seventh day. This indicates that adequate numberof organisms were not present in the system.

Adequate microorganisms were present at higher chlorideconcentrations for the whole test period at both the

temperatures.

Page 10: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 10/16

3. Values of   “k”  in exertion of BOD forglucose–glutamic acid solution at various

chloride concentrations at 20°C

Page 11: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 11/16

4. Values of   “k”  in exertion of BOD forglucose–glutamic acid solution at various

chloride concentrations at 27°C

Page 12: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 12/16

Higher values for  “k” were observed at 27°Cas compared to 20°C indicating faster rate of oxidation at elevated temperature.

The  “k” values had lowered with increase inchloride concentrations.

This finding confirmed the slowing down of the rate of biodegradation of organic matterwith elevation of chlorides (salinity). moretime will be required to break down thepollutants

Page 13: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 13/16

CONCLUSION

Based on the result, we can see that Tenpercent to 15% higher BOD was observed at 27°Cwhen compared to 20°C for glucose-glutamic acid.

Negative impact of chlorides on the oxidation of  organic matter was observed showing decrease inBOD exertion at higher chloride concentrations.

The values of    “k”  reduced significantly atelevated salinities. Good strength of the associationbetween degradation rate and chloride concentration.

The values of k indicate decreasing trend indegradation with increasing salinities. The findings of the study indicate the necessity for criticalconsideration of slow degradation rates while planningthe disposal options for organic wastes in the marineenvironment

Page 14: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 14/16

ATTENTION QUESTION THANK YOU

Page 15: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 15/16

DAFTAR PUSTAKA

A. Fatha, “Pemanfaatan Zeolit Aktif Untuk Menurunkan BOD dan COD Limbah Tahu. Skripsi”.Jurusan Kimia Fakultas Matematika Dan Ilmu Pengetahuan Alam., Universitas NegeriSemarang., Semarang (2007).

APHA, WPCF, AWWA (2005) Standard methods for the examination of water and wastewater.American Public Health Association, WPCF, AWWA. 21st Ed. NW, DC 2005.

B. Iswanto, W. Astono, Sunaryati, “Pengaruh Penguraian Sampah Terhadap Kualitas AirDitinjau dari Perubahan Senyawa Organik Dan Nitrogen Dalam Reaktor Kontinyu SkalaLaboratorium”. Volume 4 No. 1 (2007) 3.

Chaudhari, N., Tyagi, P. C., Niyogi, N., Thergaonkar, V. P., & Khanna, P. (1992). BOD test fortropical countries. Journal of Environmental Engineering, 118(2), 298–303.

CPCB (1998) CPCB water quality standards for coastal waters marine outfalls, GSR7, datedDecember 22, 1998.

CPCB (1991). Laboratory. Analytical Techniques Series LAT S/4/87-88, Validity of BODdetermination at higher temperature as against standard condition of 20°C for 5 days.Central Pollution Control Board, New Delhi.

Dhage S.S, Dalvi A.A, Wakdikar K.C, Prabhu D.V. (2008) Validation of biochemical oxygendemand exertion in marine ecosystems, First International Society BiotechnologyConference ISBT-2008 organized by International Society of Biotechnology, ResearchJournal of Biotechnology in collaboration with Sikkim Manipal Institute of Technology,December 30, 2008.

Page 16: HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

7/21/2019 HIKMAT MEGANDANA_25314705_PAPER DDTL_PPT.pdf

http://slidepdf.com/reader/full/hikmat-megandana25314705paper-ddtlpptpdf 16/16

Dimitrov, S., Pavlov, T., Nedelcheva, D., Reuschenbach, P., Silvani, M., Bias, R., et al. (2007). Akinetic model for predicting biodegradation. SAR and QSAR in Environmental Research,18(5–6), 443–457.

Gotaas, H.B. (1949) The effect of sea water on the bio-chemical oxidation of domesticwastewater. Domestic Wastewater Works Journal, 21(5).

HAMMER M.J. 1975. Biochemical Oxygen Demand. Water and wastewater tech-nology JohnWilley & Sons, Inc. New York, London, Sydney, chapter 3 : 79 -97J. F. Andrews, R. D. Cole and E. A. Pearson, “Kinetics and Characteristics of Multistage

Methane Fermentation” (1962).Loganathan, B., Ramadhas, V., & Venugopalan, V. K. (1985). New Dilution Technique for BOD

Estimation in Brackish and Sea Waters. Indian Journal of Marine Sciences, 14, 156–159.Metcalf and Eddy, Inc. (2003). Wastewater engineering treatment, disposal and reuse (3rd

ed.). New York: McGraw-Hill.Nitisoravut, S., & Klomjek, P. (2005). Inhibition kinetics of salt affected wetland for municipal

wastewater treatment. Water Research, 39(18), 4413–4419.Organization for Economic Cooperation and Development (OECD) test procedure 301 A and

301 D (1992a) Biological degradation study for marine environment for testing of chemicalsby using seawater test media.

OSPAR (2001) OSPAR convention for the protection of marine environment of the North-EastAtlantic. Meeting of working group on priority substances (SPS [2] 01/4), ARONA(SECRETARIAT/EC): October 15–19, 2001.

S. N. Chotimah, “Pembuatan Biogas dari Limbah Makanan dengan Variasi dan Suhu Substratdalam Biodigester Anaerob”. Universitas Negeri Sebelas Maret., Surakarta (2010).

Sawyer, C. N., MacCarthy, P. L., & Parkin, G. F. (2010). Chemistry for environmentalengineering (5th ed.) Columbus: McGraw Hill.

Thomann, R. (1974). Systems analysis and water quality management. New York: McGrawHill. G. Bitton, “Waste Water Microbiology”. Third Edition. New Jersey: John Wiley & Sons,Inc hal 59, 68, 215-216 (2005).