Faculty of Land and Food Systems, University of British Columbia, Vancouver, Canada.
Institute for Resources, Environment and Sustainability, University of British Columbia, Vancouver, Canada; Department of Earth, Ocean and Atmospheric Sciences, University of British Columbia, Vancouver, Canada.
J Environ Manage. 2015 Apr 1;152:140-4. doi: 10.1016/j.jenvman.2015.01.021. Epub 2015 Jan 23.
Nitrogen (N) enrichment of biochar from both inorganic and organic waste N sources has the potential to add economic and environmental value through its use as a slow release N fertilizer. We investigated the sorption of N by, and its release from, biochar made at pyrolysis temperatures of 400, 500 and 600 °C from three feedstocks: poultry litter (PL with a carbon (C) to N ratio (C:N) of 14), softwood chips of spruce-pine-fir (SPF with a C:N of 470), and a 50:50 mixture of PL and SPF (PL/SPF). The prepared biochars were enriched with ammonium nitrate (AN) and urea ammonium nitrate (UAN). PL biochars had the lowest C content (50-56% C), but the highest pH (9.3-9.9), electrical conductivity (EC, 780-960 dS m(-1)), cation exchange capacity (CEC, 40-46 cmol kg(-1)), and N content (3.3-4.5%). While N content and hydrogen (H) to C atomic ratio (H:C) decreased with increasing pyrolysis temperature irrespective of the feedstock used, both pH and EC slightly increased with pyrolysis temperature for all feedstocks. The PL and SPF biochars showed similar H:C and also similar N sorption and N release at all pyrolysis temperatures. These biochars sorbed up to 5% N by mass, irrespective of the source of N. However, PL/SPF biochar performed poorly in sorbing N from either AN or UAN. Biochar H:C was found to be unrelated to N sorption rates, suggesting that physical adsorption on active surfaces was the main mechanism of N sorption in these biochars. There were minor differences between N sorbed from NO3-N and NH4-N among different biochars. Very small amounts of sorbed N (0.2-0.4 mg N g(-1) biochar) was released when extracted with 1 M KCl solution, indicating that the retained N was strongly held in complex bonds, more so for NH4-N because the release of NO3-N was 3-4 times greater than that of NH4-N. NH4-N sorption far exceeded the effective CEC of the biochars, thereby suggesting that most of the sorption may be due to physical entrapment of NH4(+) in biochar pores. The results of this study suggest that biochar can be used to remove excess N from poultry and dairy manure and be a good mitigation option for reducing N leaching and gaseous losses.
氮(N)富集的生物炭来自无机和有机废物 N 源,通过作为缓释 N 肥料的使用具有增加经济和环境价值的潜力。我们研究了由三种原料(鸡粪(PL,C:N 比为 14),云杉-松-冷杉软木片(SPF,C:N 比为 470)和 50:50 的混合物)在 400、500 和 600°C 热解温度下制成的生物炭对 N 的吸附及其释放。制备的生物炭用硝酸铵(AN)和尿素硝酸铵(UAN)进行了富氮处理。PL 生物炭的 C 含量最低(50-56%C),但 pH 值最高(9.3-9.9),电导率(EC,780-960 dS m(-1)),阳离子交换量(CEC,40-46 cmol kg(-1))和 N 含量(3.3-4.5%)最高。尽管无论使用哪种原料,N 含量和氢(H)与 C 原子比(H:C)随着热解温度的升高而降低,但所有原料的 pH 和 EC 都随着热解温度的升高而略有增加。PL 和 SPF 生物炭的 H:C 相似,在所有热解温度下对 N 的吸附和解吸也相似。这些生物炭的 N 吸附量高达 5%(按质量计),与 N 的来源无关。然而,PL/SPF 生物炭在从 AN 或 UAN 中吸附 N 方面表现不佳。生物炭的 H:C 与 N 吸附速率无关,这表明物理吸附在这些生物炭的 N 吸附中是主要机制。不同生物炭中吸附的 NO3-N 和 NH4-N 之间存在较小差异。用 1M KCl 溶液提取时,仅释放了少量(0.2-0.4mg N g(-1) 生物炭)吸附的 N,这表明保留的 N 以牢固的复合键形式存在,NH4-N 更是如此,因为 NO3-N 的释放量是 NH4-N 的 3-4 倍。NH4-N 的吸附量远远超过了生物炭的有效 CEC,这表明大部分吸附可能是由于 NH4(+)在生物炭孔中的物理捕获。本研究结果表明,生物炭可用于从家禽和奶牛粪便中去除多余的 N,并成为减少 N 淋失和气体损失的一种很好的缓解措施。