Thiele-Bruhn S, Aust M O
Institute of Soil Science and Plant Nutrition, University of Rostock, Rostock, Germany.
Arch Environ Contam Toxicol. 2004 Jul;47(1):31-9. doi: 10.1007/s00244-003-3120-8.
Sorption of p-aminobenzoic acid (pABA) and five sulfonamide antibiotics to loess Chernozem topsoil amended with varied additions of pig slurry was investigated in batch trials. In unfertilized soil, partition coefficients (Kd) of sulfonamides ranged from 0.3 to 2.0. Strong sorption nonlinearity (1/n = 0.5 to 0.8) was best fitted by the Freundlich isotherm (R2 = 0.7 to 1.0) and was indicative for specific sorption mechanisms. Adsorption to pig slurry was much stronger, and nondesorbable portions were increased compared with soil. However, in a mixture of soil and slurry (50:1 w/w), sorption of the antibiotics was significantly decreased at a lower concentration range of pABA and the sulfonamides. This was attributed to competitive adsorption of dissolved organic matter (DOM) constituents from manure. An increase in pig slurry amendment resulted in increased total organic matter, DOM concentration, and ionic strength, but pH decreased. As a result, the nonadsorbed portions of pABA, sulfanilamide, and sulfadiazine (logD(ow) < -0.4) ranged from 47% to 82% of the applied concentration in the differently manured substrates. Dissolved fractions of the antibiotics reached a maximum at a soil-slurry ratio of 9:1 and decreased with further addition of manure. This decrease was related to the formation of less-effective DOM associates in solution. The adsorbed and desorbed portions of the less-polar substances--sulfadimidine, sulfadimethoxine, and sulfapyridine (logD(ow) > 0.1)--remained nearly constant in the presence of increased manure input. The pH changes caused by manure amendment strongly affected ionisation status of the latter compounds, thus resulting in increased adsorption, which compensated the mobilizing effect of DOM. It is suggested that the effect of manure be considered in test methods to determine the soil retention of pharmaceutical substances.
通过批次试验研究了对氨基苯甲酸(pABA)和五种磺胺类抗生素在添加不同量猪粪的黄土黑钙土表土中的吸附情况。在未施肥的土壤中,磺胺类药物的分配系数(Kd)在0.3至2.0之间。弗伦德利希等温线(R2 = 0.7至1.0)能很好地拟合强吸附非线性(1/n = 0.5至0.8),这表明存在特定的吸附机制。与土壤相比,抗生素在猪粪上的吸附更强,且不可解吸部分增加。然而,在土壤和猪粪的混合物(50:1 w/w)中,在较低浓度范围的pABA和磺胺类药物中,抗生素的吸附显著降低。这归因于粪便中溶解有机物(DOM)成分的竞争吸附。猪粪添加量的增加导致总有机质、DOM浓度和离子强度增加,但pH值降低。结果,在不同施肥的基质中,pABA、磺胺和磺胺嘧啶(logD(ow) < -0.4)的未吸附部分占施用浓度的47%至82%。抗生素的溶解部分在土壤-猪粪比为9:1时达到最大值,并随着粪便的进一步添加而降低。这种降低与溶液中形成效果较差的DOM缔合物有关。在粪便输入增加的情况下,极性较小的物质——磺胺二甲嘧啶、磺胺二甲氧嘧啶和磺胺吡啶(logD(ow) > 0.1)的吸附和解吸部分几乎保持不变。粪便添加引起的pH变化强烈影响后一种化合物的电离状态,从而导致吸附增加,这抵消了DOM的迁移作用。建议在测定药物在土壤中的保留情况的测试方法中考虑粪便的影响。