中国给水排水
中國給水排水
중국급수배수
CHINA WATER & WASTEWATER
2010年
3期
14-17
,共4页
卜发平%罗固源%许晓毅%曹佳%舒为群
蔔髮平%囉固源%許曉毅%曹佳%舒為群
복발평%라고원%허효의%조가%서위군
微污染源水%生态浮床%美人蕉%菖蒲
微汙染源水%生態浮床%美人蕉%菖蒲
미오염원수%생태부상%미인초%창포
micro-polluted source water%ecological floating bed%Canna indica%Acorus cal-amus
利用美人蕉和菖蒲生态浮床净化微污染源水,在进水TN为0.91~1.17 mg/L、TP为0.12~0.18 mg/L、COD_(Mn)为5.48~9.36 mg/L、DO为3.6~6.1 mg/L时,两种生态浮床的出水水质均能满足集中式饮用水水源地水质标准(GB 3838-2002)的要求;其中关人蕉和菖蒲浮床对TN的平均去除率分别为42.5%和36.2%,对TP的平均去除率为48.1%和44.2%,对COD_(Mn)的平均去除率为42.3%和36.3%,美人蕉浮床的净化效果要好于菖蒲浮床.可见,生态浮床的除污效果较好,可用于微污染源水的净化.
利用美人蕉和菖蒲生態浮床淨化微汙染源水,在進水TN為0.91~1.17 mg/L、TP為0.12~0.18 mg/L、COD_(Mn)為5.48~9.36 mg/L、DO為3.6~6.1 mg/L時,兩種生態浮床的齣水水質均能滿足集中式飲用水水源地水質標準(GB 3838-2002)的要求;其中關人蕉和菖蒲浮床對TN的平均去除率分彆為42.5%和36.2%,對TP的平均去除率為48.1%和44.2%,對COD_(Mn)的平均去除率為42.3%和36.3%,美人蕉浮床的淨化效果要好于菖蒲浮床.可見,生態浮床的除汙效果較好,可用于微汙染源水的淨化.
이용미인초화창포생태부상정화미오염원수,재진수TN위0.91~1.17 mg/L、TP위0.12~0.18 mg/L、COD_(Mn)위5.48~9.36 mg/L、DO위3.6~6.1 mg/L시,량충생태부상적출수수질균능만족집중식음용수수원지수질표준(GB 3838-2002)적요구;기중관인초화창포부상대TN적평균거제솔분별위42.5%화36.2%,대TP적평균거제솔위48.1%화44.2%,대COD_(Mn)적평균거제솔위42.3%화36.3%,미인초부상적정화효과요호우창포부상.가견,생태부상적제오효과교호,가용우미오염원수적정화.
Canna indica and Acorus calamus ecological floating beds were used to purify micro-pol-luted source water. When the influent TN, TP, COD_(Mn) and DO are 0.91 to 1.17 mg/L, 0.12 to 0.18 mg/L, 5.48 to 9.36 mg/L and 3.6 to 6.1 mg/L, respectively, the effluent purified by the two floating beds can satisfy GB 3838 -2002. The ecological floating beds planted with Canna indica and Acorus cal-amus exhibit average removal efficiencies of 42.5% and 36.2% for TN, 48.1% and 44.2% for TP, 42.3% and 36.3% for COD_(Mn), respectively. Canna indica has better treatment performance than Acorus calamus. The ecological floating bed has a significant purification effect, and therefore can be applied to treat micro-polluted source water.