Southern Regional Research Center, Agricultural Research Service, U.S. Department of Agriculture , 1100 Robert E. Lee Boulevard, New Orleans, Louisiana 70124, USA.
J Agric Food Chem. 2012 May 23;60(20):5035-44. doi: 10.1021/jf300825n. Epub 2012 May 10.
Phosphorus-rich manure biochar has a potential for stabilizing Pb and other heavy metal contaminants, as well as serving as a sterile fertilizer. In this study, broiler litter biochars produced at 350 and 650 °C were employed to understand how biochar's elemental composition (P, K, Ca, Mg, Na, Cu, Pb, Sb, and Zn) affects the extent of heavy metal stabilization. Soil incubation experiments were conducted using a sandy, slightly acidic (pH 6.11) Pb-contaminated (19906 mg kg(-1) total Pb primarily as PbCO(3)) small arms range (SAR) soil fraction (<250 μm) amended with 2-20 wt % biochar. The Pb stabilization in pH 4.9 acetate buffer reached maximum at lower (2-10 wt %) biochar amendment rate, and 350 °C biochar containing more soluble P was better able to stabilize Pb than the 650 °C biochar. The 350 °C biochar consistently released greater amounts of P, K, Mg, Na, and Ca than 650 °C biochar in both unbuffered (pH 4.5 sulfuric acid) and buffered (pH 4.9 acetate) systems, despite 1.9-4.5-fold greater total content of the 650 °C biochar. Biochars, however, did not influence the total extractable Pb over three consecutive equilibration periods consisting of (1) 1 week in pH 4.5 sulfuric acid (simulated leaching by rainfall), (2) 1 week in pH 4.9 acetate buffer (standard solution for toxicity characteristic leaching procedure), and (3) 1 h in pH 1.5 glycine at 37 °C (in vitro bioaccessibility procedure). Overall, lower pyrolysis temperature was favorable for stabilizing Pb (major risk driver of SAR soils) and releasing P, K, Ca, and other plant nutrients in a sandy acidic soil.
富磷有机肥生物炭具有稳定 Pb 和其他重金属污染物的潜力,同时可用作无菌肥料。在这项研究中,使用 350 和 650°C 下制备的肉鸡粪便生物炭来了解生物炭的元素组成(P、K、Ca、Mg、Na、Cu、Pb、Sb 和 Zn)如何影响重金属稳定化的程度。使用沙土、微酸性(pH 6.11)、含 Pb(主要为 PbCO(3)的 19906 mg kg(-1)总 Pb)的(<250 μm)轻度污染(小口径武器靶场)土壤部分进行土壤孵育实验,向土壤中添加 2-20 wt %的生物炭。在 pH 4.9 乙酸盐缓冲液中,Pb 的稳定化在较低(2-10 wt %)的生物炭添加率下达到最大值,且含有更多可溶性 P 的 350°C 生物炭比 650°C 生物炭更能稳定 Pb。在未缓冲(pH 4.5 硫酸)和缓冲(pH 4.9 乙酸盐)体系中,350°C 生物炭比 650°C 生物炭持续释放出更多的 P、K、Mg、Na 和 Ca,尽管 650°C 生物炭的总含量高 1.9-4.5 倍。然而,在包括(1)在 pH 4.5 硫酸中 1 周(模拟降雨淋洗)、(2)在 pH 4.9 乙酸盐缓冲液中 1 周(毒性特征浸出程序的标准溶液)和(3)在 37°C 的 pH 1.5 甘氨酸中 1 h(体外生物可利用性程序)的三个连续平衡期内,生物炭并没有影响总可提取 Pb 的含量。总的来说,较低的热解温度有利于稳定 Pb(SAR 土壤的主要风险驱动因素)并在酸性沙土中释放 P、K、Ca 和其他植物养分。