西南地区典型农田土壤中Cd~(2+)、Pb~(2+)的吸附特性研究

为了解西南地区土壤对污染毒性较强的Cd和Pb元素的吸附过程及作用机制,针对性地为预防和治理土壤污染提供理论依据,采用批试验的方法研究了典型黄棕壤和紫色土对Cd~(2+)、Pb~(2+)的吸附动力学、等温吸附过程以及土壤有机质、溶液pH对吸附过程的影响。结果表明:土壤吸附Cd~(2+)、Pb~(2+)均能在12 h内达到平衡,土壤对Pb~(2+)平衡吸附量远大于Cd~(2+),准二级动力学模型最适合表征其动力学过程(R~2≥0.99)。吸附等温线可用Langmuir方程和Freundlich方程拟合,土壤对Pb~(2+)的吸附能力和缓冲能力较Cd~(2+)更大,吸附是自发进行的物理化学作用并存的过程。黄棕壤对Pb~(2+)的吸附为放热反应,紫色土对Pb~(2+)以及两种土壤对Cd~(2+)的吸附为吸热反应。去除有机质的土壤对重金属的吸附量降低,Cd~(2+)在黄棕壤和紫色土中的试验最大吸附量分别减少了37.89%、29.62%;Pb~(2+)则分别减少了12.87%、20.71%。土壤对金属离子的吸附量随溶液初始pH的增加而增加。     

生物质炭施用及老化对石灰性紫色土中磺胺类抗生素迁移特征的影响

以长江上游低山丘陵区广泛分布的石灰性紫色土旱地的耕作层土壤为对象,采用室内批量平衡吸附试验和填装土柱穿透试验,研究了施用1%生物质炭及3年老化作用对2种磺胺类抗生素(磺胺嘧啶和磺胺二甲基嘧啶)吸附和迁移特征的影响。结果表明,Freundlich方程能更好地拟合抗生素在土壤中的等温吸附曲线,施用生物质炭提高了土壤对抗生素的吸附能力,吸附常数KF值依次为:老化1%施炭土新鲜1%施炭土对照土;土柱出流液的磺胺嘧啶和磺胺二甲基嘧啶相对浓度峰值均表现为:老化1%施炭土新鲜1%施炭土对照土,说明生物质炭的添加能有效减少控制紫色土中抗生素的淋失迁移,以对磺胺二甲基嘧啶的阻控效果较好;生物质炭老化3 a后土壤对抗生素的吸附作用与阻控效果均有所提高,主要归因于土壤pH的提高。     

pH对生物质炭吸附诺氟沙星和磺胺甲恶唑的影响

为解决水体中抗生素去除及芦苇秸秆资源化利用等问题,以芦苇秸秆制备的生物质炭为吸附材料,考察不同pH条件下诺氟沙星(NOR)和磺胺甲恶唑(SMX)在芦苇秸秆生物质炭上的等温吸附过程及吸附动力学。结果表明,生物质炭的吸附与NOR和SMX在不同溶液pH下的存在形态有关。随pH的增加,生物质炭对NOR的吸附量先增加后减小,最高吸附量为7.80 mg·g~(-1);生物质炭对SMX的吸附量在溶液pH 1～3时逐渐减小,在pH 3～5时逐渐增加,pH5时吸附量逐渐降低。拟二级动力学模型可较好地拟合NOR和SMX在生物质炭上的吸附,生物质炭吸附NOR和SMX受到表面吸附、颗粒内扩散等作用的共同影响。吸附等温线符合Langmuir方程,吸附过程以单分子层吸附为主。溶液不同的pH会影响芦苇秸秆生物质炭对NOR和SMX的吸附效果,这为生物质炭吸附水中抗生素的合理应用提供一定的数据支持。     

果园生态养鸡鸡粪DOM的淋溶特征及其对抗生素迁移的影响

为研究粪源溶解性有机物与抗生素的共迁移行为及机制,以川中丘陵区典型石灰性紫色土为对象,通过吸附平衡试验与填装土柱试验,结合光谱学表征手段,研究鸡粪溶解性有机物(Dissolved Organic Matter,DOM)的淋溶特征及其对磺胺嘧啶(Sulfadizine,SD)、氟苯尼考(Florfenicol,FFC)及泰乐菌素(Tylosin,TYL)吸附和淋溶的影响。结果表明:鸡粪DOM以色氨酸为主要成分,吸附性强于腐殖酸成分,可增加土壤表面对抗生素的吸附位点。3种抗生素的等温吸附过程均符合线性和Freundlich方程,并以物理吸附为主。SD和FFC在紫色土中吸附性较弱,当与鸡粪DOM(200 mg/L)同时进入土壤时,其吸附未发生显著变化;而当鸡粪DOM先与土壤作用后,SD和FFC与土壤表面已吸附的鸡粪DOM成分通过非共价作用结合,吸附显著增加,相应吸附容量参数(K_f值)分别增加77.28%和114.36%。TYL在紫色土中的吸附很强,对鸡粪DOM的影响不敏感。在模拟降雨条件(20 mm/h)下,SD和FFC极易淋溶,与平衡吸附试验结果一致,SD和FFC在鸡粪DOM预先与土壤作用的土柱中穿透分别延迟了0.49和0.25个孔隙体积,淋溶总量减少了12.04%和15.35%,而鸡粪DOM与抗生素同时进入土壤的处理也表现出减少抗生素迁移的趋势。TYL未发生穿透而主要分布在表层土壤中,鸡粪DOM对它的淋溶无显著影响。综上,鸡粪DOM与抗生素发生共迁移的过程中,大量鸡粪DOM中色氨酸物质在土壤中的吸附,对弱吸附性抗生素的淋溶迁移具有显著的阻滞作用。     

生物质炭对磺胺类抗生素在坡耕地紫色土中吸附-解吸及淋溶过程的影响

吸附–解吸是影响抗生素类污染物在土壤中迁移转化及生物有效性的重要过程,本文以川中丘陵区坡耕地紫色土为研究对象,通过批量平衡实验和柱实验研究生物质炭施用(投加量0(B0)、39.75 t/hm~2(B1)和198.75 t/hm~2(B2))及田间老化作用(夏季干湿交替)对3种典型磺胺类抗生素(磺胺嘧啶(SD)、磺胺二甲基嘧啶(SM2)及磺胺甲恶唑(SMZ))在紫色土中的吸附–解吸和淋溶行为的影响。结果表明:在几种处理中,3种磺胺类抗生素吸附强弱的顺序都表现为SDSMZSM2;与B0处理相比,添加生物质炭能增加土壤对3种抗生素的吸附能力,其中SM2的吸附显著增加(P0.05),但这种促进作用在经过老化过程后有所减弱。在解吸过程中,3种抗生素的Freundlich常数Kf大小顺序为SDSMZSM2,表明SD在土壤中吸附容量最大且不易解吸,其次是SMZ和SM2;相应的迟滞系数H大小顺序为SDSMZSM2,与Freundlich常数n值趋势一致,表明紫色土对SD亲和力最强,解吸最难,而SM2则解吸最易,可逆性最强。与B0处理土柱相比,3种磺胺抗生素在B1处理土柱中迁移更慢。     

长期秸秆还田下土壤铵态氮的吸附解吸特征

【目的】研究长期秸秆还田对不同轮作区域耕层和亚耕层的土壤铵态氮 (NH₄+) 的吸附、解吸特征差异,通过 Langmuir 等温吸附方程拟合得到 NH₄+ 最大吸附量 (q_max) 和吸附系数 (b),分析长期秸秆还田对不同土壤 NH₄+ 的吸附、解吸特征差异及影响因素。 【方法】2015 年 10 月水稻收获后,在湖南望城 (稻–稻轮作)、江西进贤 (稻–稻轮作)、重庆北碚 (稻–麦轮作) 三个长期定位试验点 (25 年) 采集不施肥 (CK)、长期施用化肥 (NPK) 和长期秸秆还田配施化肥 (NPKS) 三个处理、0—20 cm 和 20—40 cm 两个土层的土样,进行土壤 NH₄+ 的吸附–解吸室内试验,吸附试验为添加不同浓度的 NH₄Cl 溶液振荡、离心后,测定滤液 NH₄+ 浓度;解吸试验采用吸附试验后的土壤样品,经无水乙醇淋洗至无 NH₄+ 后,再加入 0.01 mol/L 的 KCl 溶液振荡、离心后测定滤液 NH₄+ 浓度。 【结果】长期秸秆还田对不同试验点土壤 NH₄+ 吸附–解吸特征的影响差异较大。处理间的差异主要表现在耕层土壤。当平衡溶液 NH₄+ 浓度 < 400 mg/L 时,不同试验点耕层和亚耕层处理间差异均不明显;当平衡溶液浓度 > 400 mg/L 时,处理间耕层土壤对 NH₄+ 吸附表现出差异,其中望城试验点土壤对 NH₄+ 的吸附表现为 CK > NPK > NPKS,北碚试验点则表现为 CK > NPKS > NPK,且北碚试验点的紫色土对 NH₄+ 的吸附显著高于望城和进贤试验点的红壤性水稻土。进贤试验点不同处理间差异不明显,且土壤对 NH₄+ 的吸附量最低。 通过相关性分析发现,q_max和土壤 pH、阳离子交换量 CEC 呈显著正相关,而与土壤有机质和全氮含量呈显著负相关;b 与土壤性质的相关性与q_max 则相反。从土壤对 NH₄+ 的解吸曲线来看,耕层和亚耕层土壤对 NH₄+ 的解吸在各试验点不同处理间均表现为差异不显著,其中望城和进贤试验点的红壤性水稻土 NH₄+ 的最大解吸量高于其吸附量,而北碚试验点的紫色土 NH₄+ 的最大解吸量 (541.89～742.38 mg/kg) 则远低于其吸附量 (1003.83～2014.79 mg/kg)。 【结论】长期秸秆还田对不同土壤 NH₄+ 的吸附–解吸作用影响不同,对于土壤吸附位点较多且钾离子含量丰富的紫色土而言,长期秸秆还田有利于土壤对氮的吸附;而对于土壤偏酸性的红壤性水稻土而言,长期秸秆还田则可能因为增加了土壤有机质含量而减少了土壤对铵态氮的吸附位点,从而降低了土壤对氮的吸附保持能力。     

生物质炭对磺胺类抗生素在坡耕地紫色土中吸附-解吸及淋溶过程的影响

吸附-解吸是影响抗生素类污染物在土壤中迁移转化及生物有效性的重要过程,本文以川中丘陵区坡耕地紫色土为研究对象,通过批量平衡实验和柱实验研究生物炭施用（投加量0(B0)、39.75 (B1)t/hm2和198.75 (B2) t/hm2）及田间老化作用（夏季干湿交替）对三种典型磺胺类抗生素（磺胺嘧啶（SD）、磺胺二甲基嘧啶（SM2）及磺胺甲恶唑（SMZ））在紫色土中的吸附-解吸和淋溶行为的影响。结果表明：在几种处理中,三种磺胺类抗生素吸附强弱的顺序都表现为SD>SMZ>SM2;与B0处理相比,添加生物炭能增加土壤对三种抗生素的吸附能力,其中SM2的吸附显著增加（P<0.05）,但这种促进作用在经过老化过程后有所减弱。在解吸过程中,三种抗生素的Freundlich常数Kf大小顺序为SD>SMZ>SM2,表明SD在土壤中吸附容量最大且不易解吸,其次是SMZ和SM2;相应的迟滞系数H大小顺序为SD相似文献   

紫色土NH4+、NO3-的吸附-解吸特性研究

试验在25±1℃恒温条件下研究了紫色土NH4 、NO3-的吸附-解吸特征。结果表明,紫色土对NH4 、NO3-的等温吸附曲线与Freundlich模型相关性强,均达到极显著水平。在低浓度时,NH4 、NO3-的等温吸附线斜率较大;在高浓度时,等温吸附线趋于平缓;土壤吸附态NH4 、NO3-的解吸曲线与Freundlich方程拟合度高,达到极显著水平,而与Langmiur方程拟合较差;通过K吸附和K解吸值的大小比较,找出了土壤NO3-比NH4 更易于流失的根本原因。     

pH和有机酸对酸性紫色土吸附-解吸镉的影响

选择酸性紫色土,研究pH和有机酸对紫色土吸附镉的影响。结果表明,pH在1.0~5.0的范围内,Cd2 的解吸率从接近100%急剧降低到20.0%。当pH>5.0,Cd2 的解吸率缓慢下降。相对较低的有机酸浓度(≤10-3mol/L)限制了Cd2 解吸,而较高的有机酸浓度则增加了Cd2 的解吸。柠檬酸和醋酸在较高浓度(>10-3mol/L)时极大地促进了Cd2 的解吸,其次是苹果酸,最小的是酒石酸。     

土壤和堆肥中四环素类抗生素的检测方法优化及其在土壤中的降解研究

在对土霉素(OTC)、四环素(TC)和金霉素(CTC)3种四环素类抗生素的高效液相色谱(HPLC)检测分析方法以及在土壤和堆肥中的提取方法进行改进和优化的基础上,采用该方法进行了3种抗生素在土壤中的降解试验。结果表明,选用Agilent Eclipse XDB-C8(4.6×150 mm,5μm)色谱柱,以0.01 mol/L草酸/乙腈/甲醇(79/10.5/10.5,v/v/v)为流动相,紫外检测波长268 nm,流速1.0 mL/min,进样量5μL,采用外标法定量,可使3种四环素类抗生素在20 min内全部洗脱并达到基线分离;在0～10 mg/L范围内,抗生素浓度与峰面积呈显著的线性关系,相关系数(r)均0.999。土壤和堆肥样品中的OTC、TC和CTC可用1 mol/L NaCl/0.5 mol/L草酸/乙醇(25/25/50,v/v/v)混合溶液提取,其回收率在76.0%～92.5%之间。加入到土壤中的抗生素在25℃下避光培养49 d后,在壤土和红土中的降解率分别是67%～72%和36%～46%,对应的半衰期分别为26～30 d和46～75 d,说明抗生素在壤土中比红土中容易降解。此外,3种抗生素在壤土中的半衰期没有显著性差异,而在红土中CTC和TC的降解速率显著高于OTC。     

Sorption Behavior of Ofloxacin to Kaolinite: Effects of pH,Ionic Strength,and Cu(II)

Sorption of antibiotics to clay minerals is a key process controlling their transport and fate in environment. In this study, the effects of pH, ionic strength, and Cu(II) on ofloxacin (OFL) sorption to kaolinite were investigated by batch sorption experiments. The results of sorption edge experiments suggested that OFL sorption to kaolinite was pH and ionic strength dependent. Cation exchange was a major contributor to the sorption of OFL⁺ to kaolinite. The decreased OFL sorption with increasing ionic strength indicated the formation of outer-sphere complexation. When solution pH was lower than 7.0, Cu-OFL complexes facilitated OFL sorption through electrostatic attraction or formation of kaolinite-Cu-OFL and kaolinite-OFL-Cu ternary surface complexes. However, existence of free Cu(II) cation in solution competed for sorption sites, and thus suppressed OFL sorption. When solution pH was higher than 7.0, Cu(II) existed as Cu(OH)₂, and the Cu-OFL complexes in aqueous phase and solid phase (precipitation) enhanced OFL removal efficiency from solution. The results imply that Cu(II) effects should be taken into account in the evaluation of OFL mobility in environment.     

Transport and adsorption of antibiotics by marine sediments in a dynamic environment

Background, aim, and scope  Bed sediments are the major sink for many contaminants in aquatic environments. With increasing knowledge of and research on the environmental occurrence of antibiotics, there has been growing interest in their behaviour and fate in aquatic environments. However, there is little information about the behaviour of antibiotics in a dynamic water/sediment environment, such as river and coastal marine water. Therefore, the aims of the present study were: (1) to study the transport and distribution of four common antibiotics between water and sediment in both dynamic and quiescent water/sediment systems and (2) to understand the persistence and possible degradation of the four antibiotics in the two different systems. Materials and methods  A lid-driven elongated annular flume, designed to reduce the centrifugal effect, was used to simulate a dynamic water environment. In addition, a quiescent water/sediment experiment was conducted for comparison with the dynamic water system. The seawater and sediment, used in both experiments of flowing and quiescent water/sediment systems, were collected from Victoria Harbour, a dynamic coastal environment in an urban setting. The four antibiotics selected in this study were ofloxacin (OFL), roxithromycin (RTM), erythromycin (ETM), and sulfamethoxazole (SMZ), the most commonly used antibiotics in South China. Results and discussion  Antibiotics in an overlying solution decreased very quickly in the flume system due to the sorption to suspended particles and surface sediment. There were significant differences in the adsorption of the four antibiotics in sediment. OFL showed a high tendency to be adsorbed by sediment with a high K _d value (2980 L/Kg), while the low K _d values of SMZ indicated that there was a large quantity in water. The four antibiotics reached a depth of 20–30 mm in the sediment over a period of 60 days in the flume system. However, the compounds were only found in surface sediment (above 10 mm) in the quiescent system, indicating the influence of the dynamic flume system on the distribution of antibiotics in sediment. OFL showed a moderate persistence in the dynamic flume system, while other three antibiotics had less persistence in sediment. However, all of the four compounds showed moderate persistence in the quiescent system. Recommendations and perspectives  The study showed the rapid diffusive transfer of antibiotics from water to sediment in the dynamic flume system. The four antibiotics exhibited larger differences in their adsorption to sediment in both dynamic and quiescent systems due to their different K _d values. The high sorption of antibiotics to marine sediment may reduce their availability to benthic invertebrates.     

Effects of soil organic matter on pH-dependent phosphate sorption by soils

Effects of soil organic matter (80M) on P sorption of soils still remain to be clarified because contradictory results have been reported in the literature. In the present study, pH-dependent P sorption on an allophanic Andisol and an alluvial soil was compared with that on hydrogen peroxide (H₂0₂)-treated, acid-oxalate (OX)-treated, and dithionite-citrate- bicarbonate (DCB)-treated soils. Removal of 80M increased or decreased P sorption depending on the equilibrium pH values and soil types. In the H₂O₂ OX-, and DCB-treated soils, P sorption was pH-dependent, but this trend was not conspicuous in the untreated soils. It is likely that 80M affects P sorption of soils through three factors, competitive sorption, inhibition of polymerization and crystallization of metals such as AI and Fe, and flexible structure of metal-80M complexes. As a result, the number of available sites for P sorption would remain relatively constant in the wide range of equilibrium pH values in the presence of 80M. The P sorption characteristics were analyzed at constant equilibrium pH values (4.0 to 7.0) using the Langmuir equation as a local isotherm. The maximum number of available sites for P sorption (Q _max) was pH-dependent in the H₂0₂-, OX-, and DCBtreated soils, while this trend was not conspicuous in the untreated soils. Affinity constants related to binding strength (K) were less affected by the equilibrium pH values, soil types, and soil treatments, and were almost constant (log K ≈ 4.5). These findings support the hypothesis that 80M plays a role in keeping the number of available sites for P sorption relatively constant but does not affect the P sorption affinity. By estimating the Q _max and K values as a function of equilibrium pH values, pH-dependent P sorption was well simulated with four or two adjustable parameters. This empirical model could be useful and convenient for a rough estimation of the pH-dependent P sorption of soils.     

Organic matter effects on phosphorus sorption in sandy soils

Phosphorus (P) sorption processes in soils contribute to important problems in agriculture: a deficiency of this plant nutrient and eutrophication in aquatic systems. Soil organic matter (SOM) plays a major role in sorption processes, but its influence on P sorption remains unclear and needs to be elucidated to improve the ability to effectively manage soil P. The aim of this research was to investigate the influence of SOM on P sorption. The study was conducted in sandy soil profiles and in topsoils before and after removal of SOM with H₂O₂. The results were interpreted with the Langmuir and Freundlich isotherms. Our results indicated that SOM affected P sorption in sandy soils, but that P sorption also depended on specific soil properties (e.g. values of the degree of P saturation (DPS), P sorption capacity (PSC) and pH) often related to land use. Removal of SOM decreased PSC in most of the topsoils tested; other soil properties became important in controlling P sorption. An increase in P desorption observed after SOM removal indicated that SOM was potentially that soil constituent which increased P binding and limited P leaching from these sandy soils.     

Low-molecular weight organic acids improve plant availability of phosphorus in different textured calcareous soils

Understanding the role of organic acids on phosphorus (P) sorption capacity of soils is very important for its economic and friendly management. Combining P application with low-molecular weight organic acids could result in its higher plant availability for prolonged time. Therefore, citric and oxalic acid (at the rate of 1.0 mM kg^?1 soil) were evaluated for their effect on P sorption capacity and its plant availability in two different textured calcareous soils. Organic acids decreased P sorption capacity and organic carbon partition coefficient (K_oc) whereas increased Gibbs free energy (ΔG) of P. Organic-acid-treated soils required lesser quantity of P fertilizer to produce soil solution P concentration optimum for plant growth (external P requirement [EPR_0.2]), that is, 0.2 mg L^?1. Citric acid was efficient than oxalic acid in the above effects. P sorption parameters of Freundlich model were negatively correlated with lime potential and ΔG whereas had positive correlation (P < 0.05) with EPR_0.2 and K_oc. Incubation with oxalic acid increased available P in loamy sand and loam soil by 20% and 30%, respectively. Thus, organic acids could help reduce application rate of P fertilizer through lowering its adsorption in highly P-fixing soils without compromise on yield.     

Phosphate sorption by Egyptian,Ethiopian and German soils and P uptake by rye (Secale cereale L.) seedlings

Phosphate sorption was studied in samples (0 - 20 cm depth) of five soils from Egypt (pH 7.4 - 8.7), four soils from Ethiopia (pH 3.9 - 5.3) and six soils from Germany (pH 3.3 - 7.2). Sorption parameters were calculated according to Pagel and Van Huay (1976) and according to Langmuir (Syers et al., 1973). Phosphate sorption parameters and oxalate extractable Fe and Al (Fe_ox, Al_ox) were related to the phosphate uptake by young rye plants in Neubauer pot experiments. P sorption parameter after Pagel and Van Huay (A) correlated significantly positively with the Fe_ox and Al_ox content in acid (r = 0.73) as well as in calcareous soils (r = 0.89) if the whole equilibrium concentration range (0 - 14 mg P/L) was considered. The relations calculated after Langmuir (B) were similar. P uptake by rye in acid soils was negatively correlated with the affinity constant n (r = ?0.76, (A)). In calcareous soils, a negative correlation between P uptake and affinity constant was calculated in the lower P equilibrium range (0 - 2.8 mg P/L) only for (B). Thus, P uptake decreased with increasing strength of P bonding to soil. From these results it is concluded that phosphate sorbed to Fe/Al oxides is an important P source for plants in acid and calcareous soils.     

2，4-二氯苯氧基乙酸在土壤中的吸附淋溶特性

农药在土壤中的吸附和淋溶特性是评价其环境行为的重要指标,特别是决定了其在土壤中的迁移性。本文分别利用振荡平衡法和柱淋溶法研究了2,4-二氯苯氧基乙酸（2,4-D）在不同土壤中的吸附和淋溶特性及其影响因素。结果表明,2,4-D在3种供试土壤上的吸附特性能较好地用线性吸附等温线拟合,吸附常数心在0．95-1．54L·kg^-1之间,很难被土壤吸附。影响2,4-D在土壤中吸附的因素主要是土壤pH值,其次是有机质含量。土壤pH值增高,离子态的2,4-D量增加,吸附减弱;2,4-D在土壤中具有较强的淋溶性,影响其淋溶性能的主要因素是土壤pH值,pH值越高,淋溶性能越强。     

Effect of pH on Zinc Sorption–Desorption by Soils

The objective of this study was to examine the effect of soil pH on zinc (Zn) sorption and desorption for four surface soils from the Canterbury Plains region of New Zealand. Zinc sorption by the soils, adjusted to different pH values, was measured from various initial solution Zn concentrations in the presence of 0.01 M calcium nitrate [Ca(NO₃)₂]. Zinc desorption isotherms were derived from the cumulative Zn desorbed (µg g^?1 soil) after each of 10 desorption periods by sequentially suspending the same soil samples in fresh Zn‐free 0.01 M Ca(NO₃)₂. Zinc sorption and desorption varied widely with soil pH. Desorption of both native and added Zn decreased continuously with rising pH and became very low at pH values greater than 6.5. The proportion of sorbed Zn that could be desorbed back into solution decreased substantially as pH increased to more than 5.5. However, there were differences between soils regarding the extent of the hysteresis effect.     

How Can Organic Amendments Help to Bind Sulfadiazine in the Soil? – An Iranian Soil Study

ABSTRACT

Veterinary antibiotics can enter the environment especially agricultural soils via animal manure application in which Sulfadiazine (SDZ) is considered as one of the most used antibiotic. After soil application, it may be transported into subsurface water. The sorption behavior of SDZ is not only influenced by the soil type but also by soil organic matters as well. Hence, an experiment was executed aimed to study sorption/desorption processes of SDZ under experimental conditions in three various soils treated by different bio fertilizers including rice husk compost (RHC), rice husk biochar (RHB) and Micrococcus yunnanensis (My) bacterium. Sorption/desorption data of soils with and without bio-fertilizers were well fitted with Freundlich model (R² = 0.97). Results showed that bio-amended soils had higher values of k_d sorption ranged from 1.16 to 52.4 without and with bio-fertilizers application respectively, proposing low sorption of SDZ with substantial risk of leaching without bio-fertilizers application. Also for the desorption cycle values of K_d increased from 1.03 to 39.1 without and with bio-fertilizers application, respectively. Furthermore, there was a hysteresis effect using organic matter. As a result of bio-fertilizers application, a significant value of SDZ was strongly adsorbed on the soil particles which was not desorb through desorption process.