环境工程技术学报
環境工程技術學報
배경공정기술학보
JOURNAL OF ENVIR0NMENTAL ENGINEERING TECHNOLOGY
2014年
3期
205-211
,共7页
石应杰%都基峻%王红梅%王相凤%田刚%张凡%桑健
石應傑%都基峻%王紅梅%王相鳳%田剛%張凡%桑健
석응걸%도기준%왕홍매%왕상봉%전강%장범%상건
丙烯酸钠%萘磺酸钠%氯%钠%Hg0%氧化%燃煤烟气
丙烯痠鈉%萘磺痠鈉%氯%鈉%Hg0%氧化%燃煤煙氣
병희산납%내광산납%록%납%Hg0%양화%연매연기
sodium acrylate%naphthalene sulfonate%chlorine%sodium%Hg0%oxidation%coal-fired flue gas
在热态燃煤试验炉上,利用OHM法、氢化物发生-电感耦合等离子体原子发射光谱( HG-ICP-AES)法,研究了原煤燃烧气态单质Hg( Hg0)、气态二价Hg( Hg2+)及颗粒态Hg( Hgp )分布特性,废水中Cl与Na浓度、烟气中SO2与NO对Hg0的氧化影响。结果表明,试验燃煤F、Cl浓度低,1#和2#燃煤烟气中Hg0占输入总Hg( HgT )比例分别为68.3%和80.6%,而Hg2+比例仅占22.2%和13.1%;在烟气中喷射丙烯酸钠和萘磺酸钠废水的液气比为0.028 L/m3时,1#和2#燃煤烟气Hg2+所占比例分别达到80%和75%以上,而HgP 的比例变化不显著;当喷射废水液气比为0.028 L/m3时,1#和2#燃煤烟气的SO2浓度下降11.4%~15.7%和12.2%~17.7%,促进了Cl对Hg0的氧化;而NO对Hg0的氧化不显著。
在熱態燃煤試驗爐上,利用OHM法、氫化物髮生-電感耦閤等離子體原子髮射光譜( HG-ICP-AES)法,研究瞭原煤燃燒氣態單質Hg( Hg0)、氣態二價Hg( Hg2+)及顆粒態Hg( Hgp )分佈特性,廢水中Cl與Na濃度、煙氣中SO2與NO對Hg0的氧化影響。結果錶明,試驗燃煤F、Cl濃度低,1#和2#燃煤煙氣中Hg0佔輸入總Hg( HgT )比例分彆為68.3%和80.6%,而Hg2+比例僅佔22.2%和13.1%;在煙氣中噴射丙烯痠鈉和萘磺痠鈉廢水的液氣比為0.028 L/m3時,1#和2#燃煤煙氣Hg2+所佔比例分彆達到80%和75%以上,而HgP 的比例變化不顯著;噹噴射廢水液氣比為0.028 L/m3時,1#和2#燃煤煙氣的SO2濃度下降11.4%~15.7%和12.2%~17.7%,促進瞭Cl對Hg0的氧化;而NO對Hg0的氧化不顯著。
재열태연매시험로상,이용OHM법、경화물발생-전감우합등리자체원자발사광보( HG-ICP-AES)법,연구료원매연소기태단질Hg( Hg0)、기태이개Hg( Hg2+)급과립태Hg( Hgp )분포특성,폐수중Cl여Na농도、연기중SO2여NO대Hg0적양화영향。결과표명,시험연매F、Cl농도저,1#화2#연매연기중Hg0점수입총Hg( HgT )비례분별위68.3%화80.6%,이Hg2+비례부점22.2%화13.1%;재연기중분사병희산납화내광산납폐수적액기비위0.028 L/m3시,1#화2#연매연기Hg2+소점비례분별체도80%화75%이상,이HgP 적비례변화불현저;당분사폐수액기비위0.028 L/m3시,1#화2#연매연기적SO2농도하강11.4%~15.7%화12.2%~17.7%,촉진료Cl대Hg0적양화;이NO대Hg0적양화불현저。
The Hg0 , Hg2+and Hg p distribution of coal-fired flue gas was investigated by the OHM and hydride generation-inductively coupled plasma atomic emission spectrometry ( HG-ICP-AES ) method.The impacts of chlorine and sodium content of wastewater and SO 2 and NO concentration of flue gas on Hg 0 oxidation were tested on the coal-fired test furnace in hot state .The results showed that the ferrous and chlorine content in the test coal was low and the ratio of Hg0 to HgT was 68.3%and 80.6%for coal-fired flue gas 1# and 2# respectively, while Hg2+ratio was only 22 .2% and 13 .1% respectively .When the sodium acrylate and naphthalene sulfonate wastewater liquid to flue gas ratio was 0.028 L/m3 , the Hg2+ratio reached higher than 80%and 75%in coal-fired flue gas 1#and 2# respectively .While , there were no significance variations for Hg p ratio in flue gas .When the wastewater liquid to flue gas ratio was 0.028 L/m3 , the SO2 concentration decreased by 11.4%-15.7% and 12.2%-17.7%for coal-fired flue gas 1#and 2#respectively , which accelerated Hg 0 oxidation .There was no significant effect of NO in flue gas on Hg0 oxidation.