Lindsay Peddle, B.Sc. 600 Main St., Tonawanda, NY The Rapid Measurement of Chemical Oxygen Demand in a Variety of Sample Matrices Utilizing a New Green Technology An alternative means to standard COD methods based on photoelectrochemical oxidation in a microcell INTRODUCTION Objectives t5IJTQBQFSEFTDSJCFTBOBMUFSOBUJWFNFBOTUPTUBOEBSE$0%NFUIPETCBTFEPOQIPUPFMFDUSPDIFNJDBMPYJEBUJPOJOBNJDSPDFMM5IJTUFDIOPMPHZEJSFDUMZ NFBTVSFTUIFBNPVOUPGPYJEJ[BCMFNBUFSJBMJOBTBNQMFXJUIPVUUIFOFFEGPSIB[BSEPVTDIFNJDBMTBOEDBOBMTPCFVTFEGPSSBQJE#0%FTUJNBUJPOT 4BNQMFTGSPNWBSJPVTJOEVTUSJFTIBWFCFFOBOBMZ[FEBOEIBWFQSPWFOUPCFFYDFMMFOUDBOEJEBUFTGPSUIJTOFX$0%UFDIOPMPHZ Background Importance of Measuring OD Regulatory Uses t#PUI$0%BOE#0%BSFBNPOHUIFNPTUDPNNPOHFOFSJDJOEJDFTVTFEUPBTTFTTBRVBUJDPSHBOJDQPMMVUJPOXJUI#0%PGUFOCFJOHVTFEUPFWBMVBUFUIF CJPEFHSBEBCMFGSBDUJPOBOE$0%UIFUPUBMPSHBOJDQPMMVUJPOMPBEPGXBUFSTDPOUBNJOBUFECZSFEVDUJWFQPMMVUBOUT t&1"TSFHVMBUFFOWJSPONFOUBMDPNQMJBODFPGJOEVTUSZBOEQVCMJDVUJMJUJFT8851T UPXBUFSQPMMVUJPOMJNJUBUJPOTVTJOH$0%PS#0%5 Non-regulatory Uses t*OEVTUSZVTFT$0%#0%5JOUFSOBMMZGPSQSPDFTTNPOJUPSJOHBOEQSPDFTTSFmOFNFOU The Measurement of COD & BOD t#PUI$0%#0%JOWPMWFBTUFQQSPDFTT Step 1 - Oxidation of organic matter t#0%oEBZTXJUICJPMPHJDBMNBUUFS t$0%oIS8FUDIFNJTUSZBDJEIFBUQSFTTVSFDBUBMZTUXJUI&PW t1F$0%$0%oUPNJO1IPUPDBUBMZTU67FYDJUFETFNJDPOEVDUPSXJUI&PW Step 2 - Measurement of extent of oxidation t#0%5o%JSFDUNFBTVSFNFOUPGVQUBLFPG0CZNJDSPPSHBOJTNTPWFSEBZT t$0%o8FU$IFNJTUSZoJOEJSFDUNFBTVSFNFOUPG0%WJBFMFDUSPOTDPOTVNFEJOSFEVDJOH$SUP$S t1F$0%$0%o&MFDUSPDIFNJTUSZoEJSFDUNFBTVSFNFOUPG0%WJBJOTJUVNFBTVSFNFOUPGFMFDUSPOTHFOFSBUFEEVSJOHPYJEBUJPOQSPDFTT Dichromate Method (conventional) for COD Analysis t_ZFBSPMEXFUDIFNJDBMQSPDFTT t3FRVJSFTIB[BSEPVTDIFNJDBMTJFDPODFOUSBUFETVMGVSJDBDJEEJDISPNBUFTJMWFSTVMGBUFDBUBMZTU NFSDVSZTVMGBUFDIMPSJEFSFNPWBM QSPWJEFEDIMPSJEFQQN t)FBUBU¡$IPVSQSPDFTT t0WFSBMMNFBTVSFNFOUVODFSUBJOUZó o FTUJNBUFECZCPEJFTTVDIBT&1"4UBOEBSE.FUIPET o NBOZDPNNPODPNQPVOETOPUGVMMZPYJEJ[FE t&YQFOTJWFBOBMZTJTQMVTEJTQPTBMDPTUTPGUFOQFSWJBM UPUBMJOH_QFSTBNQMF PeCOD COD Analysis t/FXUFDIOPMPHZVTJOHQIPUPBDUJWF5J0OBOPNBUFSJBMTQSPWJEJOHBOBMUFSOBUJWFNFBOTUP$0%BOBMZTJT t#BTFEPOUIFSBQJEQIPUPFMFDUSPDIFNJDBMPYJEBUJPOPGPSHBOJDTJOBNJDSPDFMMFMJNJOBUJOHUIFOFFEGPSIB[BSEPVTDIFNJDBMT t6TFTBUJUBOJVNEJPYJEF5J0 TFOTPS o 5JUBOJVNEJPYJEFJTJMMVNJOBUFEXJUI67MJHIUBOECFDPNFTBQPXFSGVMPYJEBOU7WFSTVT7BTQSPWJEFECZEJDISPNBUF o 0YJEJ[FTBMMUIFPSHBOJDTJOBTBNQMFBOEEJSFDUMZNFBTVSFTUIFBNPVOUPGPYJEBUJPOTUSVF$0%NFBTVSFNFOU PeCOD Sensor Technology COD vs. Theoretical Oxygen Demand (ThOD) t5IF5I0%GPSDPNQMFUFPYJEBUJPOPGBHJWFOPSHBOJDTQFDJFTDBOCFEFUFSNJOFEGSPNUIFTUPJDIJPNFUSZPGUIFNJOFSBMJTBUJPOFRVBUJPO t*OBOJEFBMXPSMEBNFUIPEPG$0%BOBMZTJTXPVMEDPOGPSNUPUIFDPOTUSBJOUUIBU$0%5I0% t*OUIFSFBMXPSMEB$0%NFBTVSFNFOUNFUIPENBZZJFMEBSFTQPOTFGVODUJPO$0%WT5I0%FRVBUJPO XJUIBHSBEJFOUUIBUEJGGFSTTJHOJmDBOUMZ GSPNVOJUZEFQFOEJOHPOUIFPSHBOJDTQFDJFTGSPNXIJDIUIF$0%EFSJWFT PeCOD Sensor Technology 1 ,JNFUBMTUVEJFEUIFPYJEBUJPOFGmDJFODZPGUIFEJDISPNBUFMFGU BOE QFSNBOHBOBUFNFUIPETBOEBQIPUPDBUBMZUJD5J0TFOTPSSJHIU #PUIXFU DIFNJTUSZNFUIPETTJHOJmDBOUMZVOEFSFTUJNBUFEBMDPIPMTDBSCPYZBDJETBT UIFZTUSVHHMFUPPYJEJ[FUIFNGVMMZ5IFQIPUPDBUBMZUJDTFOTPSTIPXFEFYDFMMFOU DPSSFMBUJPOXJUIUIF5I0%GPSBMMDMBTTFTPGPSHBOJDTUFTUFESFHBSEMFTTPG TBNQMFNBUSJY C r 'SPN,JNFUBM"OBMZTU t$0%NFBTVSJOHUFDIOJRVFTBSFOPUFYBDU5IFZNBZPWFSFTUJNBUFPSVOEFSFTUJNBUFUIF$0%GPSEJGGFSFOUDIFNJDBMDPNQPVOETJOUIFTBNQMF 5IJTJTJNQPSUBOUUPDPOTJEFSXIFODIPPTJOHBiSFGFSFODFwPSiTUBOEBSEw t5IFJEFBMTUBOEBSETIPVMEDMPTFMZNBUDIUIFTBNQMFDPNQPTJUJPOPSCFDMPTFUPUIFNFEJBOSFTQPOTFPGUIFQBSUJDVMBS$0%UFDIOJRVFUPBSBOHF PGDIFNJDBMT t"TUBOEBSEUIBUJTTVJUBCMFGPSPOFUFDIOJRVFNBZOPUCFPQUJNBMGPSBOPUIFS APPLICATIONS t7BSJPVTNBSLFUTFDUPSTIBWFCFFOBTTFTTFECBTFEPOUIFJSBQQMJDBCJMJUZGPSVTFXJUIUIJTOFX$0%UFDIOJRVFCBTFEPOUIFUZQFBOEDPOTJTUFODZ PGUIFTBNQMFTBOEUIFQVSQPTFGPSXIJDIUIF$0%WBMVFTBSFVTFE t3FMFWBOUJOEVTUSJFTJODMVEF o o o o o o .VOJDJQBMXBTUFXBUFSUSFBUNFOUQMBOUT 1VMQ1BQFSNJMMT 'PPEBOECFWFSBHFNBOVGBDUVSFST #SFXFSJFT 1FUSPDIFNJDBMQMBOUT 4VHBSNJMMT t$PNNPOBQQMJDBUJPOTJODMVEF#0%TDSFFOJOHQSPDFTTNPOJUPSJOHDPOUSPMBOEFOWJSPONFOUBMNPOJUPSJOH BOD Screening: t5IFDPOUJOVPVTNPOJUPSJOHPGPSHBOJDMPBEJTCFDPNJOHFTTFOUJBMUPDPNQMZXJUISFHVMBUPSZSFRVJSFNFOUT5IFTUBOEBSE#0%UFTUSFRVJSFTmWFEBZTUPDPNQMFUFBOEJTUIFSFGPSF VOBCMFUPQSPWJEFUIJTJOGPSNBUJPOJOBUJNFMZNBOOFSTP$0%JTPGUFOVTFEUPQSPWJEFBOFTUJNBUFPGUIFCJPHFPDIFNJDBMJOUFSBDUJPOTJOXBUFSXBZT t5IFEJDISPNBUF$0%NFUIPEJTOPUXJUIPVUJUTMJNJUBUJPOTBTJUJTFYQFOTJWFTMPXBOESFRVJSFTUIFVTFPGIB[BSEPVTDIFNJDBMT t5IF1F$0%NFUIPEGPS$0%BOBMZTJTUIFSFGPSFCFDPNFTBEFTJSBCMFPQUJPOGPSFTUJNBUJOH#0%BTJUJTGBTUBOESFRVJSFTPOMZBTJNQMFFMFDUSPMZUFTPMVUJPO JFOPIB[BSEPVTDIFNJDBMTOFFEFE 900 800 700 600 500 400 300 200 100 0 Dichromate COD PeCOD COD BOD 1 2 3 4 5 6 7 8 9 COD/BOD Value (mg/L) COD/BOD value (mg/L) t 5IF$JUZPG$JODJOOBUJBNVOJDJQBMJUZTFSWJOHNJMMJPOQFPQMFJTBDVSSFOU1F$0%FOEVTFSVUJMJ[JOHUIFTZTUFNSFHVMBSMZBTB#0%TDSFFOJOHUPPM o 5IFBCJMJUZUPRVJDLMZQSFTDSFFOUIFJSTBNQMFTPOUIF1F$0%SFEVDFTUIFOVNCFSPGEJMVUJPOTSFRVJSFE o )BWFUXP."/5&$)BVUPNBUFE#0%TZTUFNTUPSFQPSUmOBMOVNCFST $PNQBSJTPOTUVEJFTIBWFCFFODPOEVDUFEGPSBOVNCFSPGTBNQMFTTFFHSBQITGPMMPXJOH 1200 1000 800 600 Dichromate COD 400 PeCOD COD BOD 200 0 1 10 2 3 4 5 6 7 8 9 10 Sample Sample Plot of Dichromate COD, PeCOD COD and BOD for influent sample. A similar pattern should be observed for each trend line, which is apparent for PeCOD COD and BOD, while Dichromate COD results are more variable. Plot of Dichromate COD, PeCOD COD and BOD for an effluent sample. PeCOD COD demonstrates a much stronger correlation to BOD than Dichromate COD values and in fact are almost equal. 80 60 50 40 Dichromate COD 30 PeCOD COD*0.6 20 BOD 10 COD/BOD Value (mg/L) COD/BOD Value (mg/L) 70 70 60 50 Dichromate COD 40 30 PeCOD COD 20 BOD 10 0 0 1 2 3 4 5 6 7 8 9 10 1 2 3 4 5 6 7 8 9 10 Sample Sample Plot of BOD, Dichromate COD and PeCOD COD with a factor of 0.6 applied to PeCOD values for a secondary combined sample. This factor was applied to COD values as it provides very close estimations of BOD for most of the samples. As noted by the enduser, 2 small outliers may be observed in this data set because of extremely dark and turbid samples which makes representative sampling more difficult. Plot of Dichromate COD, PeCOD COD and BOD for a final sample. A good correlation is observed between all trends, with PeCOD COD and BOD showing an excellent correlation. 5IJTTUVEZEFNPOTUSBUFTUIFFYDFMMFOUDPSSFMBUJPOPCTFSWFECFUXFFO1F$0%$0%BOE#0%BTFWJEFOUGSPNUIFHSBQIT t*OBMMDBTFTUIFDPSSFMBUJPOPCTFSWFEJTTUSPOHFSUIBOUIBUCFUXFFOEJDISPNBUF$0%BOE#0% t1F$0%$0%JTBCFUUFSFTUJNBUPSPG#0%TJODFOFJUIFSNFUIPESFRVJSFTUIFEJHFTUJPOTUFQOFFEFEGPSEJDISPNBUF$0%BOBMZTJT t1F$0%XJMMHJWFUIFUSFBUNFOUQMBOUBDDVSBUFBOEWBMVBCMFQSPDFTTDPOUSPMJOGPSNBUJPOJOBGSBDUJPOPGUIFUJNFSFRVJSFEGPSFJUIFSUIFEJDISPNBUF$0%PS#0%UFTUT t8JUINPSFSFMJBCMFFTUJNBUFTPG#0%BTQSPWJEFECZUIF1F$0%GFXFSEJMVUJPOTBSFSFRVJSFE WWT Plant Protection & Optimization: t$POTUBOU$0%NPOJUPSJOHDBOQSPUFDUXBTUFXBUFSUSFBUNFOUQMBOUTGSPNIJHI$0%FWFOUTCZQSPWJEJOHBEWBODFOPUJDFPGBOZQSPCMFNTUSFBNT t1SPWJEFTUIFPQQPSUVOJUZGPSQMBOUPQUJNJ[BUJPOBTBFSBUJPOBOEQPXFSDPOTVNQUJPOVTFEJOUIFQSPDFTTGPS$0%SFNPWBMDBOCFmOFUVOFECBTFEPOUIFSFRVJSFNFOUTPGUIFQMBOU SBUIFSUIBODPOTUBOUMZSVOOJOHBUBMFWFMIJHIFSUIBOOFDFTTBSZUPBMMPXGPSUIFQPTTJCJMJUZPGIJHI$0%MPBET t&WFOUNPOJUPSJOHJNQSPWFTUIFFOWJSPONFOUBMQFSGPSNBODFPGBQMBOUBOENBZIFMQMPXFSEJTDIBSHFDPTUT Wastewater Treatment Plant Inuent Stream 600 COD / [mg/L O2] 500 Online PeCOD COD 400 300 200 100 0 0 Online monitoring of COD in 15 minute cycles in the primary clarifier effluent at a WWTP. Major fluctuations in COD would be hard to see without continuous monitoring. 100 200 300 Sample 400 500 600 Online Monitoring of COD in 15 minute cycles over 6 days at the secondary stage influent of a WWTP. The expected regular diurnal variations are apparent, however it started high and then declined which was the result of someone illegally dumping high COD industrial waste into a public drain 2 APPLICATIONS Manufacturing Plant Performance Optimization: – – – Real-time analysis of COD on the effluent of an industrial plant will provide the operational feedback necessary to optimize production processes and cleaning practices. Spot-check COD at various locations throughout the process to identify any problem streams. Quick point-of-origin notification provides the information needed to optimize treatment processes. The lowering of discharge levels of COD will reduce the consumption of raw materials and reduce sewer discharge costs or internal wastewater treatment plant costs. Online PeCOD COD, Jan 2007 14000 0.61 × (PeCOD COD) 0.61 × (Dichromate COD) BOD5 7000 1-hour Avg COD BOD5 & Esmated BOD5 / (mg/L) COD / [mg/L O2] 8000 PeCOD COD 12000 10000 8000 6000 4000 2000 6000 5000 4000 3000 2000 1000 0 30-Jan 29-Jan 28-Jan 27-Jan 26-Jan 0 0 5 10 15 20 25 30 Day Daily monitoring of COD & BOD in Brewery wastewater effluent Online monitoring of COD in 15 minute cycles of a brewery effluent stream 6000 6000 5000 5000 PeCOD Results Dichromate COD Results 4000 4000 ppm COD ppm COD t0OFQBSUJDVMBS64#SFXFSZNVTUNPOJUPS$0%SFHVMBSMZBUWBSJPVTTUBHFTEVSJOHUIFJSUSFBUNFOUQSPDFTTUPFOTVSFFWFSZUIJOHJTSVOOJOHTNPPUIMZ – Treatment utilizes high COD waste to create energy – A spike in COD could create an over-production of methane gas, which would then need to be flared off – Also ensures final effluent is within discharge limitations 3000 2000 3000 2000 PeCOD Results 1000 1000 Dichromate COD Results 0 0 #101 #102 #114 #115 #116 #117 #118 #130 #131 #132 #146 24Mar 24Mar 25Mar 25Mar 25Mar 25Mar 25Mar 26Mar 26Mar 26Mar 31Mar Date/Sample #89 #94 #95 #105 #106 #121 #122 #123 #124 #138 #139 23Mar 23Mar 23Mar 24Mar 24Mar 25Mar 25Mar 25Mar 25Mar 29Mar 29Mar Sample Plot of Dichromate COD and PeCOD COD for a brewery anaerobic influent sample Plot of Dichromate COD and PeCOD COD for a brewery anaerobic digester effluent sample t.BJOMZJOUFSFTUFEJOTPMVCMF$0%JOGPSNBUJPOBTNPTUTPMJETQSFTFOUJOTBNQMFTDBOOPUCFCSPLFOEPXOEVSJOHUIFBOBFSPCJDQSPDFTT – PeCOD provides soluble COD information – The dichromate test is unable to differentiate between soluble and total COD (in this study, dichromate results were obtained by pre-filtering samples) – PeCOD is providing another valuable result that wasn’t available before t5IFTBNFUSFOEDBOCFPCTFSWFEGPSCPUIEJDISPNBUF$0%BOE1F$0%$0% t1F$0%DBOQSPWJEFBDDVSBUFBOEWBMVBCMFJOGPSNBUJPOJOBGSBDUJPOPGUIFUJNFSFRVJSFEUPSVOUIFEJDISPNBUF$0%UFTU t4MJHIUEJGGFSFODFTCFUXFFOUIFUXPNFUIPETNBZTUJMMCFPCTFSWFEJOTPNFJOTUBODFTBTBSFMBUJWFMZMBSHFQPSFmMUFSXBTVTFEUPSFNPWFTPMJETQSJPSUPEJDISPNBUFBOBMZTJT Plant Organic Source Monitor & Control: o o o 3FBMUJNF$0%BOBMZTJTBUBCJPMPHJDBMOVUSJFOUSFNPWBM#/3 QMBOUXIFSFNFUIBOPMPSBDFUJDBDJEJTCFJOHVTFEBTBGPPETPVSDF *ODSFBTFEFGmDJFODZPGUIFOJUSPHFOSFNPWBMQSPDFTTMPXFSFEOVUSJFOUEJTDIBSHFDPTUTSFEVDFEDIFNJDBMDPTUTBOEMPXFSFE#0%EJTDIBSHFQBZNFOUT #/3QSPDFTTFTBSFWFSZTFOTJUJWFUPJOnVFOUDPOEJUJPOTJOnVFODFECZXFBUIFSFWFOUTTMVEHFQSPDFTTJOHBOEPUIFSUSFBUNFOUQSPDFTTFT5IFSFGPSFDPOTUBOU monitoring of conditions is essential. Manufacturing Plant Water Feedstock Monitor o 1SPWJEFJOGPSNBUJPOPOUIFPSHBOJDDPOUFOUPGUIFXBUFSOPUBWBJMBCMFGSPN50$BOBMZTJT5IJTXJMMFOBCMFJNQSPWFEQSPEVDURVBMJUZBOESFEVDFEQMBOUNBJOUFOBODF Plant Effluent Discharge Monitor: – – – – Cooling tower monitoring High COD in outflow means loss of product for refinery and potential environmental breach penalties Real-time COD monitoring enables corrective action to be taken by the plant Avoid potential for bad publicity that could have a direct negative impact on perceived company value in the share market 14 BOD(5) 12 PeCOD Est. BOD(5) BOD5 / [mg/L O2] 10 8 6 BOD5 = 0.55 × COD 4 2 16:00 15:00 14:00 13:00 12:00 11:00 10:00 0 Time of Day Online Monitoring of COD/Estimation of BOD in a Sugarcane Mill Effluent Stream Potable Water Monitor: – – Similar to monitoring water feed stocks, TOC has been used for monitoring drinking water as the standard COD method is unable to provide real-time information and lacks sensitivity. TOC analysis is widely used in applications where the analysis of carbon levels is sufficient but it lacks important information about the environmental effects of the organic matter that COD would provide. e.g. TOC is the same for methanol and formic acid solutions given the single carbon in each compound. COD values however are different because of the different redox state of carbon in methanol compared to formic acid SUMMARY #FOFmUTPG1F$0%"OBMZTJT t-PX"OBMZTJTDPTUT t/PVTFEJTQPTBMPGUPYJDIB[BSEPVTSFBHFOUT t'BTUBOEBDDVSBUF#0%TDSFFOJOHUPPM t1SPUFDUSFHJPOBM8851TGSPNIJHI$0%MPBET t4BWFFOFSHZJO8851T t"WPJEFOWJSPONFOUBMOPODPNQMJBODFmOFT 3
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