Karathanasis A D, Johnson D M C
University of Kentucky, Department of Agronomy. N-122K Ag. Science-North, Lexington, KY 40546-0091, USA.
Sci Total Environ. 2006 Feb 1;354(2-3):157-69. doi: 10.1016/j.scitotenv.2005.01.025. Epub 2005 Feb 26.
The potential of biosolid colloids to transport metals associated with organic-waste amendments through subsurface soil environments was investigated with leaching experiments involving undisturbed soil monoliths. The monoliths (25 cm in height and 18 cm in diameter) were carved from the upper solum of an Alfisol, a Mollisol, and an Entisol in the Bluegrass region of Kentucky. Biosolid colloids were fractionated from two municipal wastes (lime-stabilized/LSB, and aerobically-digested/ADB), and a poultry-manure (PMB) organic waste and applied onto the monoliths at a rate of approximately 0.7 cm/h. Eluents were monitored for soluble and sorbed Cd, Cr, and Mo concentrations over 16-24 pore volumes of leaching. Colloid-free solutions with metal concentrations similar to those of the biosolid colloids were used as controls. The results indicated significantly (P<0.05) higher (up to 4 orders of magnitude) cationic and anionic metal elutions in association with the biosolid colloids in both, total and soluble fractions, over the control treatments. The elution of significant soluble metal loads in association with the biosolid colloids is attributed to increasing organic-metal complexation and exclusion processes, and emphasizes their importance as contaminant carriers and facilitators. Eluted metal loads varied with metal, colloid, and soil type, following the sequences Mo>Cd>Cr for the metals, and ADB>PMB>LSB (Cd and Cr) or ADB>LSB>PMB (Mo) for the colloids. Metal elution was generally enhanced by soil macroporosity and increasing OM content, while pH and Fe-Al oxides had significant, but opposite effects for the elution of cationic and anionic metal forms. Colloid and metal breakthrough curves were correlated well, being mostly asymmetrical with several maxima and minima caused by multiple clogging and flushing cycles. Soil- and colloid-metal sorption affinities were not reliable predictors of metal attenuation/elution loads, underscoring the dynamic nature of transport processes. The findings demonstrate the important role of biosolid colloids as contaminant carriers and the significant risk they pose, if unaccounted, for soil and ground water contamination in areas receiving heavy applications of biosolid waste amendments.
通过涉及未扰动土壤整块体的淋溶实验,研究了生物固体胶体在地下土壤环境中运输与有机废物改良剂相关金属的潜力。整块体(高25厘米,直径18厘米)取自肯塔基州蓝草地区的一种淋溶土、一种软土和一种新成土的上部土层。从两种城市废物(石灰稳定化/LSB和需氧消化/ADB)以及一种家禽粪便(PMB)有机废物中分离出生物固体胶体,并以约0.7厘米/小时的速率施用于整块体上。在16 - 24孔隙体积的淋溶过程中,监测洗脱液中可溶性和吸附态镉、铬和钼的浓度。使用金属浓度与生物固体胶体相似的无胶体溶液作为对照。结果表明,与对照处理相比,生物固体胶体在总量和可溶部分中,阳离子和阴离子金属的洗脱量显著更高(高达4个数量级)(P<0.05)。与生物固体胶体相关的大量可溶性金属负荷的洗脱归因于有机 - 金属络合作用和排斥过程的增加,并强调了它们作为污染物载体和促进剂的重要性。洗脱的金属负荷随金属、胶体和土壤类型而变化,金属的顺序为钼>镉>铬,胶体的顺序为ADB>PMB>LSB(镉和铬)或ADB>LSB>PMB(钼)。土壤大孔隙度和有机物质含量增加通常会增强金属洗脱,而pH值和铁铝氧化物对阳离子和阴离子金属形态的洗脱有显著但相反的影响。胶体和金属的穿透曲线相关性良好,大多不对称,由于多次堵塞和冲洗循环导致有几个最大值和最小值。土壤和胶体 - 金属吸附亲和力不是金属衰减/洗脱负荷的可靠预测指标,这突出了运输过程的动态性质。研究结果表明生物固体胶体作为污染物载体的重要作用,以及如果不加以考虑,它们在大量施用生物固体废物改良剂的地区对土壤和地下水污染构成的重大风险。