AMD铁絮体改性生物炭对重金属吸附机理研究 ——以Pb(II)为例

以酸性矿山废水生成的铁絮体和秸秆生物炭为原料,采用化学改性和紫外辐射联用技术制备改性生物炭,并通过正交试验确定最佳改性条件,同时利用FTIR、SEM和BET等方法对吸附材料的形貌特征、孔隙结构及其表面化学性质进行表征.结果表明,通过改性使吸附材料比表面积增大,吸附位点增多,在25℃、pH为7时,吸附材料改性后比表面积为295.71 m²·g^-1,对Pb（II）的拟合吸附量可达278 mg·g^-1.改性材料对Pb（II）的吸附过程符合Langmuir吸附等温线模型和准二级动力学模型,主要为单分子层吸附,受化学吸附控制.     

安全农居四字歌

.....口..农村震害,建造街房,农民盖房,建址不当,建筑材料,物筑堵体,农居工租,场址选择,地羞安全,用料保质,堵体构架,结构科学,房塌最‘漆,大计育年,常按习惯,河启暗边,旧瓦碎砖,结构松傲,地震安全,德定地段,沟柑要宽,更乃关健,紧密相联,层层梁圈,人财     

China’s agricultural GHG emission efficiency: regional disparity and spatial dynamic evolution

Environmental Geochemistry and Health - Improving China’s agricultural greenhouse gases (GHG) emission efficiency has become an important way to cope with climate change in an...     

Influences of coal mining water irrigation on the maize losses in the Xingdong Mine area, China

In 2008, a maize underproduction disaster occurred in the Xianyu village after irrigation using the coal mining water from the Xingdong Mine, China. This disaster resulted in about 40 hectare maize underproduction and 20 hectare total loss of the maize yields. In order to study the reason, a total of 25 soil, water and plant samples were taken from the study area. These samples were analysed by inductively coupled plasma mass spectrometry and ion chromatography. The results indicate that the contents of both water-soluble fluorine and total fluorine are very high and resulting of maize underproduction and total loss of production. The possible pollution sources of fluorine in the study area could be from the coal mine water used for irrigation and glass chemical factory near the study area.