期刊文献+

不同炭化温度下玉米秸秆和沙蒿生物炭的结构特征及化学特性 被引量:36

The Structure Characteristics and Chemical Properties of Maize Straw Biochar and Artemisia ordosica Biochar Prepared at Different Carbonization Temperatures
在线阅读 下载PDF
导出
摘要 掌握不同生物炭材料的结构特征和化学特性是合理利用生物炭的基础。通过无氧炭化法制备了不同炭化温度下的玉米秸秆生物炭和沙蒿生物炭,对比了不同材料和不同炭化温度下生物炭性质的差异。结果表明:炭化温度低于400~C时,两种材料生物炭的孔隙结构保存完整,600℃以上时,两种材料生物炭的蜂窝状结构均遭到破坏,玉米秸秆生物炭被破坏得更严重;同一炭化温度下,玉米秸秆生物炭的比表面积及总孔容和平均孔径均大于沙蒿生物炭,两种生物炭的比表面积随炭化温度的升高均增大,总孔容呈“V”形变化;两种材料的生物炭均呈碱性,炭化温度越高,pH越大,400℃~800℃,每升高10℃,玉米秸秆生物炭和沙蒿生物炭的pH均以0.02的幅度增加,同一温度下,玉米秸秆生物炭的pH大于沙蒿生物炭,在400~C、600℃和800℃下分别比沙蒿生物炭高0.31、0.35和0.29单位;随炭化温度的升高,玉米秸秆生物炭和沙蒿生物炭的C、P、K和灰分含量增加,400℃~800℃,玉米秸秆生物炭的C、P、K含量以炭化温度每升高10~C分别增加2.94、0.11、0.20g/kg的幅度变化,沙蒿生物炭也以4.35、0.07、0.24g/kg的幅度增加,与此同时,玉米秸秆生物炭的N、H含量以每升高10℃分别以0.13g/kg和0.86g/kg的幅度降低,沙蒿生物炭的N、H含量分别以0.04g/kg和0.82g/kg的幅度下降,s含量无明显变化,C/N和C/H增大,且不同材料生物炭的元素含量差异显著;两种材料生物炭的N、P、K有效性随炭化温度的升高均下降,400℃~600℃,玉米秸秆生物炭和沙蒿生物炭的速效N含量分别下降了57.89%和19.05%,800℃时两种生物炭的速效N均接近0mg/kg,400℃~800℃玉米秸秆生物炭和沙蒿生物炭的速效P含量分别降低了67.41%和52.36%,此时速效K含量也分别降低了45.62%和90.16%。总之,不同材料和炭化温度对生物炭的物理特征和化学特性都有较大影响。 The structural characteristics and chemical properties of biochars generated from various materials were the basis for the rational utilization of the biochars in agriculture and environment. In this paper, maize straw biochar and Artemisia ordosica biochar were prepared through anaerobic carbonization method at different carbonization temperatures, and their chemical properties were measured. Results showed that the pore structure of the biochars from the two materials was intact below 400℃, while the honeycomb structures of the biochars were destroyed above 600℃. The honeycomb structures of maize straw biochar was destroyed more seriously compared with Artemisia ordosica biochar. The specific surface area, total pore volume and average pore diameter of maize straw biochar were greater than Artemisia ordosica biochar at the same carbonization temperature. The specific surface areas of the two kinds of biochars were increased with the increasing carbonization temperature. The total pore volume of the biochars changed with carbonization temperature as "V" type. The biochars are alkaline, and the higher carbonization temperature led to greater biochar pH. The pH of the biochars was increased by 0.02 units/10℃ in the range from 400℃- 800℃. The pH of maize straw biochar was higher than the Artemisia ordosica biochar at the same temperature, and at 400℃, 600℃ and 800℃ , the pH of maize straw biochar higher than the Artemisia ordosica biochar by 0.31,0.35 and 0.29, respectively. C, P, K and ash contents of the biochars increased with the increasing carbonization temperature. The rise of each 10~C led to the increase in the contents of C, P, and K of maize straw biochar by 2.94 g/kg, 0.11 g/kg, 0.20 g/kg, respectively, and the corresponding data were 4.35 g/kg, 0.07 g/kg, and 0.24 g/kg for Artemisia ordosica biochar. However, the rise of each 10℃ led to the decrease in contents of N and H by 0.13 g/kg and 0.86 g/kg for maize straw biochar, and 0.04 g/kg and 0.82 g/kg for Artemisia ordosica biochar. Therefore, C/N and C/H ratios of the hiochars increased with rising temperature. S contents of the biochars did not change with temperature obviously. The difference of element contents between maize straw biochar and Artemisia ordosica biochar was significant. Available contents of N, P, and K in the biochars decreased with the increasing carbonization temperature. When temperature was increased from 400℃ to 600℃, the available N contents of maize straw biochar and Artemisia ordosica biochar were decreased by 57.89% and19.05%, respectively. When temperature was increased to 800℃, the available N contents in both maize straw biochar and Artemisia ordosica biochar decreased to 0 mg/kg. When temperature was increased from 400℃ to 800℃, available P contents of maize straw hiochar and Artemisia ordosica biochar were reduced by 67.41% and 52.36%, respectively, and available K contents decreased by 45.62% and 90.16%, respectively. Therefore, different materials and carbonization temperature affected physicochemical characteristics and chemical properties of biochars.
出处 《土壤》 CAS CSCD 北大核心 2015年第5期886-891,共6页 Soils
基金 内蒙古自然科学基金项目(2015MS0309) 国家自然科学基金项目(31260502)资助
关键词 生物炭 沙蒿 玉米秸秆 孔隙度 比表面积 Biochar Artemisia ordosica Corn straw Porosity Specific surface area
作者简介 梁桓(1989-),女,内蒙古呼和浩特人,硕士研究生,主要从事优质高产农作物的营养与施肥研究。E-mail:1062757170@qq.com 通讯作者(pau198@sina.com)
  • 相关文献

参考文献18

  • 1Antal MJ, Gronli M. The art science and technology of charcoal production[J]. Industrial and Engineering Chemistry, 2003, 42:1 619-1 640.
  • 2高海英,陈心想,张雯,何绪生,耿增超,佘雕,郭永利.生物质炭及炭基硝酸铵肥料理化性质研究[J].干旱地区农业研究,2012,30(2):14-20. 被引量:13
  • 3Van Zwieten L, Kimber S, Morris S, Chan KY, Downie A, Rust J, Joseph S, Cowie A. Effect of biochar from slow pyrolysis of papermill waste on agromic performance and soil fertility[J]. Plant and Soil, 2010, 327(1/2): 235-246.
  • 4Schmidt MWI, Noack AG. Black carbon in soils and sediments: Analysis distribution, implications, and current Challenges[J]. Global Biogeochemical Cycles, 2000, 14(3): 777-794.
  • 5Novak JM, Busscher WJ, Laird DL. Impact of biochar amendment on fertility of a southeastern coastal plain soil[J]. Soil Science, 2009, 174(2): 105-112.
  • 6Keiluweit M, Nico PS, Johnson MG, Kleber M. Dynamic molecular structure of plant biomass derived black carbon (Biochar)[J]. Evironmental Science and Technology, 2010, 44(4): 1 247-1 253.
  • 7刘玉学,刘微,吴伟祥,钟哲科,陈英旭.土壤生物质炭环境行为与环境效应[J].应用生态学报,2009,20(4):977-982. 被引量:302
  • 8谢祖彬,刘琦,许燕萍,朱春悟.生物炭研究进展及其研究方向[J].土壤,2011,43(6):857-861. 被引量:197
  • 9李力,陆宇超,刘娅,孙红文,梁中耀.玉米秸秆生物炭对Cd(Ⅱ)的吸附机理研究[J].农业环境科学学报,2012,31(11):2277-2283. 被引量:227
  • 10Ogawa M. Symbiosis of people and nature in the trapics[J]. Fanning Japan, 1994, 28(5): 10-34.

二级参考文献218

共引文献753

同被引文献598

引证文献36

二级引证文献421

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部