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。     

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   

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。     

Cd/Cu/Pb对磺胺嘧啶在土壤中吸附迁移的影响

通过室内批平衡实验和土柱出流实验,探讨了不同浓度镉(Cd)及相同浓度的Cd、铜(Cu)、铅(Pb)对磺胺嘧啶在土壤中吸附、迁移的影响,并分别用Freundlich、Langmuir、Linear方程及Hydrus-1D中的单点和两点吸附模型模拟其在土壤中的吸附、运移过程。结果表明:当Cd浓度为10.0mg·kg~(-1)时促进磺胺嘧啶的吸附;Cd浓度为1.0、300.0mg·kg~(-1)时抑制磺胺嘧啶吸附;Cd浓度为100.0 mg·kg~(-1)时对磺胺嘧啶的吸附无影响;300 mg·kg~(-1)的Cd、Cu、Pb存在时,磺胺嘧啶吸附量大小顺序为:CdCuPb。土柱出流实验中,当Cd浓度为10.0mg·kg~(-1)时,磺胺嘧啶在土柱中的迁移速度最慢,其他浓度对迁移影响不明显;Cd、Cu、Pb相比较而言,Cu存在时磺胺嘧啶的迁移最快,Cd存在时迁移最慢。在对静态吸附特征的拟合过程中,Linear方程拟合效果最好,决定系数R~2均在0.98以上;Hydrus-1D模拟时,两点模型可更好地拟合磺胺嘧啶的运移特征,R~20.907,均方根误差RMSE0.051,瞬时吸附f所占分数较高,说明磺胺嘧啶在迁移过程中存在较大程度的瞬时吸附。     

生物炭对两种典型植烟土壤养分、碳库及烤烟产质量的影响

为探讨生物炭对江西植烟土壤肥力和烤烟致香物的影响,2015年在江西省信丰县西牛镇进行水稻土和紫色土田间试验,生物炭穴施增施量设置为T1(0 kg hm~(-2))、T2(450 kg hm~(-2))、T3(900 kg hm~(-2))、T4(1350 kg hm~(-2))、T5(1800 kg hm~(-2))五个水平。结果表明:(1)增施生物炭后,水稻土和紫色土速效养分含量,全碳、有机碳、水溶性碳、C/N都有所增加。(2)水稻土pH随着生物炭施用量的增加而增加,T2降低了紫色土pH。(3)增施生物炭提高了紫色土易氧化态碳含量和碳库管理指数,以T2处理效果最为显著,水稻土除T3处理外,其他处理易氧化态碳含量和碳库管理指数均低于T1处理。(4)增施生物炭提高了水稻土有机碳氧化稳定性,降低了紫色土有机碳有机碳氧化稳定性,生物炭在水稻土中更加稳定。(5)施用生物炭对两种土壤不同部位烟叶中性致香物影响不同。(6)施用生物炭后水稻土和紫色土烤烟分别最高增产52.94%和122.75%。综上所述,在水稻土和紫色土中增施生物炭可以提高土壤质量和烤烟产质量,分别以常规施肥增施900 kg hm~(-2)和450 kg hm~(-2)时效果最好。     

氟喹诺酮类抗生素在农业紫色土中的吸附研究

抗生素被广泛作为抗菌药物和添加剂使用在畜牧业中,造成大量抗生素随着动物粪便进入到土壤环境。吸附行为是抗生素在土壤中迁移转化的重要过程,对抗生素的风险评估及污染控制具有重要的意义。本文采用吸附试验研究了两种氟喹诺酮类抗生素(诺氟沙星(NOR)和氧氟沙星(OFL))在重庆广泛分布的紫色土中的吸附特性以及影响因素。结果表明:NOR和OFL在紫色土上的吸附过程较快,5 h就能达到吸附平衡,吸附常数Kd能达到3 082 L/kg。Freundlich吸附等温模型能很好拟合紫色土对NOR和OFL的等温吸附过程。由吸附过程的吉布斯自由能ΔG和吸附能E可知,紫色土吸附NOR和OFL主要是通过物理吸附。溶液pH6会降低紫色土对NOR和OFL的吸附。当溶液离子强度从0.005 mol/L增加至0.05 mol/L时,NOR和OFL在紫色土上的吸附量分别降低了10.2%和11.7%。土壤有机质对NOR和OFL的吸附过程影响很小。     

磺胺嘧啶在土壤及土壤组分中的吸附/解吸动力学

抗生素在土壤中的吸附/解吸及迁移过程受其理化性质的强烈影响,其中土壤中的矿物成分,如高岭石、蒙脱石及腐殖酸等是重要控制因素。本文主要研究了磺胺嘧啶在土壤、高岭石、蒙脱石和腐殖酸中的吸附/解吸动力学过程,并对反应前后的高岭石、蒙脱石和腐殖酸进行傅里叶红外光谱(Fourier transform infrared, FTIR)表征,探讨其可能的吸附机理。结果表明:磺胺嘧啶的吸附(解吸)动力学过程,可以分为快速吸附(解吸)、吸附解吸动态平衡和吸附(解吸)平衡3个阶段;磺胺嘧啶在土壤及其3种组分中的吸附(解吸)均可在24 h内达到平衡,其浓度高低会导致土壤及其组分的吸附差异,不同土壤组分中的官能团含量、带电性质及氢键是造成吸附差异的主要原因;分别用伪一级动力学模型、伪二级动力学模型和Elovich模型对其吸附过程进行拟合,其动力学吸附过程更符合伪二级动力学模型,R20.99,主要受控于物理化学吸附;FTIR图谱表明磺胺嘧啶与高岭石以物理吸附为主,并有少量氢键作用,与蒙脱石之间主要以氢键作用完成吸附,而在腐殖酸中存在表面络合和π–π共轭作用。     

土壤磺胺类抗生素固相萃取-高效液相色 谱法的构建与优化

设计正交试验对红壤中磺胺甲恶唑(sulfamethoxazole, SMZ)的萃取方法进行优化,并结合高效液相色谱,构建了固相萃取-高效液相色谱联合测定法(SPE-HPLC),并将该方法应用于不同抗生素以及不同类型土壤中SMZ的提取测定。结果表明,在以乙腈–磷酸盐缓冲液为提取液、提取液量为10 ml、超声时间为15 min、9 ml甲醇淋洗固相萃取柱(HLB)的条件下,红壤中SMZ的提取效果最优,0.25 mg/kg的SMZ回收率达到85.58%,能够满足环境样品的分析要求。利用该法提取测定红壤中不同抗生素包括3种磺胺类抗生素(磺胺嘧啶、磺胺二甲基嘧啶、磺胺甲基嘧啶)和2种四环素类抗生素(土霉素、盐酸四环素),结果表明,当抗生素浓度为0.25 mg/kg时,磺胺类抗生素(SAs)的回收率范围在67.31%～85.58%,四环素类抗生素(TCs)的回收率范围在20.81%～59.33%。利用该法分别提取测定不同类型土壤中的SMZ回收率,得到潮土中SMZ的回收率最大,达到92.92%,其次为荒漠土、红壤、紫色土,最低的回收率出现在黄棕壤,仅为53.62%。据相关性分析表明,回收率与土壤电导率(EC)、微生物碳氮比(C/N)呈极显著负相关(P0.01),与阳离子交换量(CEC)、有机质(SOM)呈显著负相关(P0.05)     

高效液相色谱-串联质谱同时测定有机肥料中9种抗生素药物残留

采用高效液相色谱-串联质谱法(HPLC-MS/MS),同时测定有机肥料中3类9种抗生素(土霉素、四环素、金霉素、强力霉素、青霉素G和普鲁卡因青霉素、磺胺嘧啶、磺胺二甲基嘧啶、磺胺噻唑)残留,对于有机肥料中抗生素残留的快速检测具有重要的意义。样品用Na2EDTA-Mc Ilvaine缓冲液超声振荡提取后,采用固相萃取小柱净化,高效液相色谱-串联质谱法检测,标准曲线外标法定量。采用多反应监测模式检测,除负离子扫描青霉素G外其他均用正离子扫描。方法在0.1、0.5、1.0 mg/kg添加水平下,样品平均回收率为63.1%~93.4%;相对标准偏差为1.7%~9.5%;四环素类药物的方法检出限均可达到0.05 mg/kg,磺胺类和青霉素类药物的检出限可达0.02 mg/kg。本方法简便、快速,重现性良好,可用于有机肥料样品中抗生素残留的快速确证检测。     

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。     

添加生物质炭对红壤性水稻土Cd2+吸附解吸特性的影响

为探讨生物质炭对红壤性水稻土中镉(Cd)元素吸附解吸特性的影响,采用一次平衡法研究添加生物质炭后Cd2+在红壤性水稻土中的吸附动力学、等温吸附和解吸过程。结果表明:施用CK(0t/hm^2)、A10(10t/hm^2)、A20(20t/hm^2)、A30(30t/hm^2)和A40(40t/hm^2)生物质炭后,红壤性水稻土对Cd2+的吸附过程是以化学吸附为主、非均匀的多表面吸附。施用CK(0t/hm^2)、A10(10t/h2)、A20(20t/hm^2)、A30(30t/hm^2)和A40(40t/hm^2)生物质炭处理的最大吸附量和最大解吸量分别为2933~3346mg/kg和171~192mg/kg。添加生物质炭可以提高红壤性水稻土对Cd2+的吸附固持能力,同时增强土壤对外源Cd2+的缓冲能力。生物质炭添加量对红壤性水稻土的吸附解吸能力的改良效果具体表现为:A30>A40>A20>A10。高剂量的生物质炭处理使土壤吸附点位饱和,生物质炭吸附能力相对降低。因此,添加30t/hm^2生物质炭是一种有效预防和治理红壤性水稻土镉污染的措施。     

不同热解温度茶渣生物质炭对茶园土壤吸附解吸NH4-N的影响

生物质炭对铵根的吸附解吸影响着土壤的固氮效果,为探讨茶渣生物质炭对茶园土吸附—解吸NH_4~+—N性能的影响,减少土壤中氮素的淋失,提高氮素利用效率,通过模拟培养试验,采用平衡吸附法及HCL解吸法,研究了不同热解温度下制备的茶渣生物质炭在不同添加比例(0.35%,0.70%,1.40%,2.80%)下,茶园土对NH_4~+—N吸附解吸的特性。结果表明:施用生物质炭能有效增强茶园土对NH_4~+—N的吸附,并随生物质炭添加量的增加而增强。同一生物质炭添加量下,4种生物质炭处理下茶园土对NH_4~+—N的吸附量大小表现为BC400BC300BC500BC600。生物质炭的CEC含量是影响土壤吸附NH_4~+—N能力的主要因素。土壤对NH_4~+—N的吸附过程均以Langmuir方程拟合达到显著水平(0.953 7R~20.995 5),以单层吸附为主。施用生物质炭后,土壤产生了解吸滞后,有效降低了茶园土对NH_4~+—N的解吸率,BC400的解吸率最低。茶渣生物质炭能够增强土壤对NH_4~+—N的吸附,降低对NH_4~+—N的解吸,有利于提高土壤对氮素的吸持能力,其中BC400,2.80%处理下效果最佳。     

Long-term effects of bone char and lignocellulosic biochar-based soil amendments on phosphorus adsorption–desorption and crop yield in low-input acidic soils

Although the addition of biochar has been shown to reduce the phosphorus (P) adsorption capacity of soil, quantitative evidence of this has mainly been provided by incubation experiments and it is therefore essential to conduct long-term field trials to draw general conclusions. It is largely unknown whether bone char has a greater effect than lignocellulosic biochar on P adsorption–desorption processes and crop yield. The aim of this study was to determine the long-term (8 years) effect of bone char and biochar on P adsorption–desorption and crop yield in low-input acidic soils. The results showed that bone char decreased the maximum P adsorption capacity (Q_m) by 10% and increased the desorption capacity (D_s) by 150% compared with the control (i.e. without a soil amendment). The desorption ratio was highest for the bone char treatment (10.3%) and three times more than the control. Plant-available P was seven times greater under bone char than the control. There was no variation in adsorption–desorption characteristics, desorption ratio and plant-P available content between bone char and lignocellulosic biochar treatments. The average yield increment following the application of bone char and biochar was 1.7 and 1.4 Mg ha⁻¹ for maize and 1.8 and 1.9 Mg ha⁻¹ for soya bean, respectively. Despite the low application rate (4 t ha⁻¹ year⁻¹), these findings demonstrated that the long-term application of bone char and biochar-based amendments enhanced P availability in low-input cropping systems, mainly by altering the P adsorption and desorption capacity of soils.     

土壤对铜的吸附-解吸特征及对土地利用的响应

用吸附平衡法研究黄河三角洲地区土壤对Cu2+的吸附和解吸特征,对比了农田和未利用地土壤吸附与解吸能力的差异,并分析了差异形成的原因。结果表明,土壤对Cu2+的吸附量随着平衡液Cu2+质量浓度的增加而增加,其吸附作用可用Langmuir,Temkin和Freundlich方程来拟合,以Langmuir方程拟合结果最佳。根据Langmuir方程计算出的两种土壤最大吸附量分别为3 961mg/kg和3 521mg/kg,农田土壤对Cu2+的吸附能力强于未利用地土壤;土壤Cu2+的解吸量远远小于土壤对Cu2+的吸附量,与农田土壤相比,未利用地土壤Cu2+的解吸有滞后现象;农田土壤和未利用地土壤Cu2+的解吸率变化范围分别为0.1%～0.35%和0.15%～1.8%,农田土壤的解吸率明显低于未利用地土壤。综合分析认为,两种土壤吸附—解吸特征的差异与农田土壤具有较高的有机质含量,从而在土壤胶体表面形成较多的吸附位点有关。     

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.     

Effect of coffee husk and cocoa pods biochar on phosphorus fixation and release processes in acid soils from West Cameroon

Acid soil in West Cameroon has limited phosphorus (P) availability which limits plant growth. This is mainly because of low pH, high levels of exchangeable aluminium (Al) and iron (Fe) and fixation of P. In this study, acid soils, sampled in Bafang, were amended with biochar produced from coffee husks (CH) and cocoa pod husks (CP) at two different temperatures (350 and 550 °C) in other to evaluate the effect on the physicochemical properties of the acid soil and the effect on P sorption and desorption. The soil was amended with biochar at a rate of 0, 20, 40 and 80 g/kg and incubated for 7 and 60 days. Physicochemical properties of all soil–biochar samples were determined followed by sorption experiments and data fitted in the Langmuir and Freundlich isotherm models in other to evaluate soil P sorption capacity and its affinity to soil amended with biochar. Moreover, desorption studies were done to evaluate the availability of P in soil amended with biochar after sorption. The outcomes of this study reveal an increase in soil pH, electrical conductivity (EC), available P, soil organic carbon and a drastic decrease in exchangeable Al and Fe. The point of zero charge of biochar-amended soil was higher than the control and increased with amendment rate. The experimental data of the sorption of P on soils and soil–biochar samples fits into Langmuir and Freundlich models (R² > 0.9) suggesting that the P adsorption is controlled by both model mechanisms. Soil–biochar mixture results in a decrease in the sorption capacity as compared with the control and the decrease was predominant with increasing amendment rate. At amendment rates of 20, 40 and 80 g/kg after 7 days of incubation, $Q_{\max }$ for SCH350 were 2267, 2048 and 1823 mg/kg which increased to 2407, 2112 and 1990 mg/kg after 60 days of incubation. This tendency was observed for all biochar inputs with respect to the increase in incubation days. Furthermore, desorption of P from soil–biochar mixtures was enhanced with biochar added at greater rate and produced at higher temperature. The desorption percentage was increased by more than around 10% for all biochar types from 20 mg/kg to 80 mg/kg amendment. Thus, biochar addition to acid soils reduces P fixation to acid soil and improves P desorption to soil solution, thereby providing more available P in the soil solution and better conditions for plant growth.     

Characterization of Pterocarpus macrocarpus (pradoo wood) biochar and its effect on the retention properties of sandy soils in Northeast Thailand

Pradoo wood biochar has been tested in order to explore sustainable solutions to the development of agriculture on poor sandy soils in marginal areas in Northeast Thailand. Some basic physicochemical properties of biochar, for example pore size distribution, cation exchange capacity (CEC), specific surface area (SSA), and water and nutrient adsorption, were determined and compared to soil properties in order to determine appropriate biochar application to soil. Pradoo wood biochar showed important adsorption properties with high SSA, CEC and nutrient adsorption. The water retention properties were also improved on the dry end of the water retention curve. Phosphorous and ammonium adsorption–desorption isotherms were established and their respective affinity for the biochar surface was quantified, by the means of a retention index and thermodynamical parameters. We found that despite excellent retention properties, biochar needs to be added in large amounts (between 10 and 70 kg m⁻²) to soil to be able to modify noticeably the resulting soil properties.     

Sorption and transport of sulfonamides in soils amended with wheat straw-derived biochar: effects of water pH,coexistence copper ion,and dissolved organic matter

Purpose

Sulfonamides are widely used for the prevention and treatment of bacterial infections, hard-degraded contaminants distributed in the environment if they are discharged into the soil and water. Biochar could probably influence the geochemical behavior of ionized antibiotics in the soils.

Materials and methods

To determine the sorption/desorption of three representative sulfonamides (SAs) in soils amended with biochar, we investigated the effects of water pH, Cu²⁺, and dissolved humic acid on the sorption of sulfamethoxazole (SMX), sulfamethazine (SMZ), and sulfadiazine (SD) onto two different soil samples (S1 pH?=?5.13 and S2 pH?=?7.33) amended with wheat straw-derived biochar (size 0.5～0.6 mm).

Results and discussion

Batch experiments showed that the sorption/desorption isotherms of SAs on soil with/without biochar followed the Freundlich model. The biochar had a strong adsorption potential for SMX, SMZ, and SD both in S1 and S2 at low water pH. Except for SMX, the presence of Cu²⁺ inhibited the sorption of SMZ and SD through competing hydrophobic adsorption region in soils. HA suppressed the sorption of three sulfonamides in soil S2 by electrostatic repulsion under alkaline condition. The soil leaching column experiments showed the SA transport in soils, and S1 and S2 amended with biochar (0.5 and 1.0 wt%) brought about 12–20 % increase in SMX, SMZ, and SD retention compared to the untreated soil.

Conclusions

The results indicated that the presence of biochar effectively mitigated the mobility of ionized antibiotics such as SMX, SMZ, and SD in soils, which helps us reconsider the potential risk of antibiotics in the environment.