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当前位置:首页 > 医学/心理学 > 药学 > 高浓度混合制药废水的中试处理王金梅
1,2*,2,2,2,2(1., 067000;2., 100012):--,,,,pH,,,3t/d.,,COD97.6%,COD.:;;--:X787 :A :0250-3301(2002)-04-0044:(1967~),,,.*APilotStudyontheTreatmentofHighConcentrationPharmaceuticalWastewaterWangJinmei1,WangQingsheng2,YuYanmin3,ChenDehui2,XiBeidou2,HaoYongli2(1.ChengdePetroleumCollege,HebeiChengde067000,China;2.ChineseRerearchAcademyofEnvironmentalSciences,Beijing100012,China)Abstract:Apilotstudyonthetreatmentantibioticpharmaceuticalwastewaterbyusinghydrolysisacidification-anaerobic-aerobicbiologicalprocess.Theeffectsofpreliminarytreatment,biochemicaltemperature,pHvalue,hydraulicretaintime(HRT)andinfloworganicconcentrationandotherfactorstobiochemicalprocesswerecheckedbyusinglaboratorytest.Theflowratewas3t/d.TheexperimentresultsundertheregularconditionshowedthatCODremovalratecameto97.6%.CODconcentrationoftheoutflowcouldbereducedtolessthen300mg/Ltomeetthenationalstandardofpharmaceuticalindustry.Keywords:pharmacueticalwastewater;treatmentofpilottest;hydrolysis-anaerobic-aerobicprocess ,..,,,.,COD,SS,,,[1].,--,3t/d,3.1 1.1 (),,.()、.,(),,,,,.(),,、CO2、H2S.,,,,[2].,,,23200212 ENVIRONMENTALSCIENCEVol.23,Sup.Dec.,2002DOI:10.13227/j.hjkx.2002.s1.010.1.2 ,,30℃,7d,,,.().,.1.3 ,、、,,1.1 /g·L-1Table1 Waterqualityofmixturewastewaterinpilottex/g·L-1COD2BOD5SO2-4SSpH12~184~83.0~5.03.5~7.56.8~7.21.4 1.4.1 1,(),UASB.1 Fig.1 Thetechnologicalprocessofthepilottest ,,UASB.,,,.1.4.2 (1) [4],COD,,,pH(2).(2) 2,,,COD.2 /g·L-1Table2 Thecoperatingconditionintest/g·L-1COD/g·L-1/℃/hpH1.20~13.035248.07.0~8.038248.02.5~2.020~25127.02 2.1 ()2.1.1 (),,500mg/L300kg,2.0g/L,,,120L/m,()2.45 2 ()Fig.2 Changeofdebuggingwaterwiththeoperatingtineinhydrolysis 2()COD40%,COD,,COD,,COD7g/L,(VFA,)2.0g/L.(),H2,,,[3]SO2-4,:CHCOO-+SO2-4=2HCO-3+HS-4C2H5COOHCO-3+3SO2-4=4CH3COOHCO-3+4HCO-3+3HS-+H+4H2+SO2-4+CO2=HS-+HCO-3+3H2OFe+HS-=FeS↑+H2 ,,pH,,,.2.1.2 ,COD2.0~13.3g/L,COD12.4kg/(m3·d),COD4.75kg/(m3·d),6.13kg/(m3·d),,3.2.2 2.2.1 UASB,,,,300kg2.0g/L,7d,120L/h,COD0.25kg/(m3·d)2.0kg/(m3·d),COD7.0g/L.4,COD3.5g/L,pH7.0,COD47.3%,3.0g/L.3 ()SO2-4Fig.3 ChangesofvolumeloadandSO2-4withtheoperatingtimeinhydrolysis4 CODFig.4 ChangesofCODconcentrationwithwithoperatingtimeindebuggingofanaerobic2.2.2 5.COD4.0kg/(m3·d),3.1kg/(m3·d),,,,,SVI20.2mL/g.46 23,20m/h,,,,.5 Fig.5 Changesoforganicloadwiththeoperatingtimeinanaerobic2.3 ,.300kg,,COD3.0g/L,,2d,6.6,COD2.5g/L,COD2.0g/L,.1,,..COD1.5g/L,58%.6 CODFig.6 ChangesofCODconcentrationwithoperatingtimeinaerobic2.4 ()--3,,203.3COD.,,,COD.3 21dTable3 Theaverageresultsinsteadyoperatingin21daysCOD/mg·L-1~13300~11830~6690~3670~1520~308/%43.554.99.7/%87.297.63 (1)()--..(2),().()-COD12.0g/L,COD87.2%,3.1kg/(m3·d),4kg/(m3·d),,COD97.6%.(3),()-:35℃~38℃,24h,COD12.0g/L,,COD2.0g/L,12h.(4),(),90%,Fe2+,H2S.:1 ,,.[J].,1997,18(3):83~85.2 ,.()-[J].,2000,(5):43~45.3 EaryLE,KaiD.Chromateremovalfromagueouswastesbyreductivewithferrousiron[J].Environ.Sci.Technol.,1998,(22):972~976.4 ,,.H/O[J].,2000,():150~152.47
本文标题:高浓度混合制药废水的中试处理王金梅
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