阿特拉津在饱和砂质壤土中非平衡运移的模拟

针对农药阿特拉津在稳定流场饱和砂质壤土中的运移 ,根据平衡与非平衡假设条件下对流—弥散方程数学模型的解析解 ,基于易混合置换实验获得的阿特拉津和示踪溶质Br- 的穿透曲线及批量平衡法求得的阻滞因子 ,应用CXTFIT 2 0软件 ,通过拟合土柱实验中溶质的出流浓度变化 ,估算了模型的有关参数 ,在此基础上模拟分析了实验土柱不同埋深处阿特拉津的出流浓度和累积淋溶量动态 ,结果表明 ,化学非平衡的两点模型对本文实验条件下阿特拉津运移的仿真具有较高的精度     

阿特拉津在土柱中的淋溶规律研究

通过室内土柱淋溶试验,对阿特拉津在2种供试土壤中淋溶规律及其影响因子进行了研究.结果表明,淋溶速度由1.8 ml/min增至4.4 ml/min,阿特拉津的土壤残留量降低,淋出量分别增加10.8%(黑土),8.2%(草甸黑土);同时,增加土壤有机质含量,适当降低淋溶液中H+离子浓度,均有利于抑制土壤中阿特拉津的迁移与流...     

阿特拉津在饱和砂质壤土中非平衡运移的模拟

针对农药阿特拉津在稳定流场饱和砂质壤土中的运移 ,根据平衡与非平衡假设条件下对流—弥散方程数学模型的解析解 ,基于易混合置换实验获得的阿特拉津和示踪溶质Br- 的穿透曲线及批量平衡法求得的阻滞因子 ,应用CXTFIT 2 .0软件 ,通过拟合土柱实验中溶质的出流浓度变化 ,估算了模型的有关参数 ,在此基础上模拟分析了实验土柱不同埋深处阿特拉津的出流浓度和累积淋溶量动态 ,结果表明 ,化学非平衡的两点模型对本文实验条件下阿特拉津运移的仿真具有较高的精度     

坡耕地草篱系统中土壤阿特拉津残留的迁移规律

为探索坡耕地中等高草篱对土壤阿特拉津残留迁移的影响,采用模拟降雨试验,研究华北地区不同坡度(15%和20%)条件下草篱系统中土壤阿特拉津残留迁移分布特征。结果表明:降雨后,土壤阿特拉津残留纵向迁移占主导地位。草篱处理篱带区阿特拉津残留量远低于无草篱对照的对应区域,篱带区各土层阿特拉津残留量相近,而无草篱对照残留量随土层深度增加而降低,且表层(0-10cm)显著高于其他层。草篱系统中不同篱域土壤阿特拉津残留量差异显著,篱带区沉降区作物区。最优尺度回归分析结果表明,草篱系统中各因素对土壤阿特拉津残留量影响程度从大到小依次为草篱土层深度土壤含水量篱域坡度坡位,草篱的重要性超过其他因素。草篱显著影响坡耕地土壤阿特拉津的横向扩散和纵向迁移,可作为控制坡耕地农药流失的首选措施。     

阿特拉津对我国东北半干旱区黑钙土微生物活性影响研究

按照0.5～800 μg·g^-1 soil 施入量添加阿特拉津到黑钙土中培养54 d进行实验室培养试验,研究了阿特拉津对我国东北半干旱区黑钙土微生物量碳、土壤碳及氮矿化量、脲酶和脱氢酶活性影响。结果表明,阿特拉津添加到土壤中后,显著提高了（P〈0.05）土壤微生物量碳,增加了土壤碳及氮矿化量,提高土壤脱氢酶活性;多数情况下,各培养时间添加阿特拉津各处理间土壤脲酶活性的差异未达到显著水平（P〈0.05）。由此得出结论：土壤脱氢酶活性、土壤微生物量碳和土壤碳矿化量及氮矿化量是对阿特拉津处理土壤较敏感的生物学指标,适合作为半干旱区黑钙土微生物活性对阿特拉津响应的参数;而土壤脲酶活性不适合作为半干旱区黑钙土土壤微生物活性的指标,因为它不能敏感地反映阿特拉津作用下土壤脲酶活性差异。     

黄土丘陵区不同坡度撂荒草地入渗特征影响因素试验研究

降雨特征和坡度是影响土壤入渗过程的重要因素,在植被恢复过程中,其对土壤入渗特征的影响可能会有所不同。选取黄土丘陵区6个坡度(5°,10°,15°,20°,25°和30°)的撂荒草地(2年)径流小区(5 m×20 m),观测自然降雨条件下(共计34场降雨,产流11场)植被生长旺期(7—9月)土壤入渗特征,研究降雨过程参数(降雨量、平均雨强、降雨历时和I_(30))、坡度和植被盖度对坡面入渗特征的影响。结果表明:(1)11场产流降雨不同坡度土壤入渗量总体变化范围为6.58～70.91 mm,入渗补给系数为0.83～1.00,入渗率为0.22～19.35 mm/h;(2)土壤入渗量随降雨量呈线性增加(R~2=0.99,p0.01),入渗补给系数随I_(30)呈指数降低(R~2=0.91,p0.01),平均入渗率随降雨强度呈线性增加(R~2=0.71,p0.01),随降雨历时呈幂函数降低(R~2=0.99,p0.05);(3)坡度增大使得径流位移增长,导致入渗量、入渗补给系数和平均入渗率整体随坡度增大而呈幂函数增加,但当坡度25°时,因径流势能沿坡面方向分量增加,径流流速加快,上述入渗特征参数略有降低;(4)由于降雨量在植被生长周期内呈下降趋势,很大程度上导致植被对入渗特征的影响受控于降雨量,土壤入渗量表现出随着植被盖度的增加呈幂函数显著下降的趋势。总体而言,降雨特征和坡度是影响土壤入渗的主要因素,且土壤入渗特征参数可表示为降雨过程参数和坡度的综合幂函数方程;在入渗补给系数较高的情况下,植被覆盖对土壤入渗特征的影响减弱。研究结果对于坡面尺度降雨径流调控机制和生态水文过程研究具有重要意义。     

农田气象条件下阿特拉津在土壤中淋溶动态的数值模拟

阿特拉津(Atrazine)是我国华北地区夏玉米田常用的除草剂,而夏玉米生育期又是该地区的主要降雨时段,对这一时段Atrazine在田间尺度的淋溶风险进行评价,对保护浅层地下水环境具有重要意义。以北京市通州区永乐店试验站一块27 m×27 m的农田为背景,通过田间采样、测试分析土壤样品并收集2001年的气象数据,基于简化土壤水三维流场的柱模型假设,在同时考虑土壤水力学参数、Atrazine运移和吸附参数空间变异性的情况下,对该农药在农田尺度下淋溶动态的空间分布进行了数值模拟。在此基础上,对夏玉米不同生育期耕层20 cm深度处的土壤水负压、水流通量和Atrazine浓度的空间变异结构进行了地质统计学分析。结果表明,在整个夏玉米生育期内这三个参量的半方差模型基本上为球状模型,它们的变程多在8~10 m。本研究案例对布设农田尺度土壤水分和Atrazine动态监控网具有一定的参考意义。     

纳米Fe3O4/微生物联合体系对2,4-D和阿特拉津降解的研究

采用纳米Fe3O4/微生物联合体系降解溶液中2,4-D和阿特拉津,考察了不同2,4-D和阿特拉津初始浓度、微生物接种量、纳米Fe3O4投加量、溶液ｐＨ值等对降解效果的影响。结果表明,纳米Fe3O4/微生物联合体系对2,4-D和阿特拉津的降解率显著高于纳米Fe3O4和微生物单一体系;2,4-D和阿特拉津初始浓度在0～10 mg·L^-1、微生物接种量在0～12 mg·L^-1、纳米Fe3O4的投加量在0～200 mg·L^-1范围内,2,4-D和阿特拉津的降解率随其初始浓度、微生物接种量和纳米Fe3O4 投加量的增大而增加。溶液pH3．0左右、2,4-D和阿特拉津初始浓度10 mg·L^-1、微生物接种量12 mg·L^-1、纳米Fe3O4投加量200 mg·L^-1,是反应的最佳条件,此实验条件下反应7 d,2,4-D和阿特拉津的残留率分别降低至35．7％和54．0％。     

田间土壤剖面中阿特拉津的迁移试验

为了评价阿特拉津的污染风险,采用原位试验法研究了土壤剖面中阿特拉津、Br-与水分耦合迁移特征.结果表明,施用阿特拉津24 h后,模拟降雨1 h,降雨量为40 mm的处理(Ⅰ)和80 mm的处理(Ⅱ)的土壤含水率随土层深度增加先减小后增加;而施用阿特拉津前模拟降雨1 h,降雨量为10mm,施用24 h后,模拟降雨1 h,降雨量为40 mm的处理(Ⅲ)和80 mm的处理(Ⅳ)的则呈"S"形变化.Br-与阿特拉津在0～10 cm土层的残留浓度最大,分别为1.40、1.09、0.62、0.52 mol/kg和0.82、0.74、0.54、0.29 靏/g.处理Ⅰ、Ⅱ的各土层中Br-与阿特拉津的变异较小.土壤溶液中阿特拉津的浓度随土层深度的增加而降低,表层(20 cm)土壤溶液中阿特拉津残留浓度为:处理Ⅰ＞处理Ⅲ＞处理Ⅱ＞处理Ⅳ.     

固相萃取-气相色谱法测定土壤中毒死蜱和阿特拉津

应用带TSD检测器的气相色谱仪、CP—SIL19弹性石英毛细管柱,采用固相萃取技术提取土壤中毒死蜱和阿特拉津,对土壤中的毒死蜱和阿特拉津同时测定,回收率分别为81．5％～116．7％、80．3％～118．2％,方法的变异系数1．1％～4．8％和0．9％～5．3％,方法检出限分别为阿特拉津0．0006mg·kg^-1、毒...     

Water and Atrazine Movement in a Calcareous Compost Applied Soil During Simulated Multiple Storms Events

The retention and movement of water and atrazine (2-chloro-4-ethylamino-6-isopropylamino-s-triazine) was investigated in a calcareous soil (Krome) amended with three types of compost: (1) Clean organic waste (COW)- municipal solid waste cleaned of plastic materials and metal containers, (2) Biosolids (BSD)- sludge from municipal waste and (3) Bedminster (BDM)—a mixture containing 75% COW and 25% BSD. The research was conducted in two phases; a column-leaching study (dynamic) and a batch-equilibrium method (static). The column study demonstrated that while applying simulated rain, atrazine, leached out at a slower rate by 41, 24, and 18% from soil amended with BDM, BSD, and COW composts, respectively, during the first simulated storm event. BDM application resulted in lowest water movement and atrazine-leaching rate compared to the other composts tested. This study suggests that adding 134 t ha^?1 of compost to the calcareous soil increased soil water holding capacity, reduced water movement and increased atrazine detention and reduced leaching potential of atrazine thereby reducing the potential for groundwater pollution. This study further demonstrates that soil amendment (particularly BDM) is effective in reducing the leaching potential of atrazine at the low rainfall amounts (corresponding to 0.5 pore volume). However, such amendment may not be effective in preventing leaching under more intense rain conditions or multiple rainfall events (corresponding to 3 or more pore volumes).     

Water drainage and nitrate leaching under traditional and improved management of vegetable‐cropping systems in the North China Plain

Traditional irrigation and nitrogen (N) fertilization in North China may elevate water drainage and nitrate concentrations in soil and groundwater. A field experiment was conducted in an intensively irrigated vegetable (cauliflower, amaranth, and spinach) field for three consecutive years (1999–2002). The main objective was to test to what extent an improved water and fertilizer management, based on the maintenance of field capacity a defined range of the water content in the 0–50 cm soil layer and an N expert system, could reduce drainage and nitrate leaching without impairing vegetable yield. Rates of water drainage and related nitrate leaching were calculated based on measurements of soil water potential and soil‐water nitrate concentrations. Soil water potential was monitored with tensiometers at depths of 75 cm and 105 cm. Nitrate concentrations were analyzed in soil leachates collected at 90 cm soil depth using ceramic suction cups. The results revealed that the average annual drainage related to the cultivation season for cauliflower, amaranth, and spinach was reduced from 275 mm in the traditional system to 29 mm with improved management practice. The average annual cumulative nitrate leaching during the vegetable‐growing period amounted to 301 kg ha^–1 and 13 kg ha^–1 in the traditional and improved management practices, respectively. Vegetable yields were not significantly different under the traditional and improved management practices.     

Water flow patterns and pesticide fluxes in an upland soil in northern Thailand

Rapid percolation of water through soil facilitates both the recharge and the contamination of groundwater reservoirs. We have studied the variation of water flux and pesticide leaching through a soil in northern Thailand. At a depth of 55 cm, two pits were equipped with tensiometer-controlled glass suction lysimeters that were connected to a novel on-line solid-phase extraction device. Nine insecticides varying in water solubility from 10⁻² to 10⁺⁶ mg l⁻¹ were applied on the soil surface, and leaching was monitored for 8 weeks. Measured water fluxes were compared with simulated values. Total recovery ranged from traces (malathion, triazophos) to 1.3% (dimethoate) of the applied amount, showing a decreasing retardation with increasing polarity of the substances. All pesticides were detectable in the soil solution during the first rain after application. Due to fingering, 83% of the leachate was transported through 38% of the area at leaching rates of < 2 mm per day. A new adaptation of the Simpson Index revealed that the diversity of the flow pattern increased exponentially with decreasing rates of seepage water flux (R² = 0.80). No such correlation was found when leaching was faster, indicating that the flow pattern switched from a fingering- to a matric-dominated flux. No long-term leaching of insecticides was observed. The two profiles studied behaved similarly in terms of both water and pesticide transport. Therefore we suggest that the flow pattern is a stable property of the soil that can be accurately described by our combination of novel experimental setup and statistical analysis of the flow field.     

Amelioration of saline–sodic soil with mildly saline water in the Songnen Plain, northeast China

Abstract. The saline–sodic soils of the dryland Songnen Plain in northeast China are only slowly permeable to fresh water because of their large content of montmorillinite clay and sodium bicarbonate. Use of slightly saline groundwater containing adequate dissolved calcium and magnesium for leaching and reclamation can potentially prevent dispersion of the clay soil particles during treatment. Amelioration was evaluated using shallow, mildly saline groundwater to irrigate sorghum–corn rotations in a two-year field experiment. After two growing seasons during which a total of 400 mm of leaching water was applied, in addition to some supplemental irrigation water, the average electrical conductivity (EC_e) of the top 1.2 m of the soil profile decreased from 14.5±3.5 to 2.7±0.2 dS m⁻¹, and the sodium absorption ratio (SAR_e) decreased from 35.3±4.1 to 10.1±2.5 (meq L⁻¹)^0.5. The soil physical properties were improved: infiltration rate with mildly saline groundwater increased from 12.1 to 42 mm h⁻¹. Salinity changes in the top 1.2 m of soil layers after 700 mm of leaching produced no further improvement. Crop yields produced on plots undergoing amelioration increased by 64–562% compared with the rainfed control. The improved soil conditions after leaching resulted in 59–548% greater crop yields.     

Determination of the atrazine migration parameters in Vertisol

The parameters of the atrazine migration in columns with undisturbed Vertisol sampled from an irrigated plot in Guanajuato, Mexico were determined. A model of the convection-dispersion transport of the chemical compounds accounting for the decomposition and equilibrium adsorption, which is widely applied for assessing the risk of contamination of natural waters with pesticides, was used. The model parameters were obtained by solving the inverse problem of the transport equation on the basis of laboratory experiments on the transport of the ¹⁸O isotope and atrazine in soil columns with an undisturbed structure at three filtration velocities. The model adequately described the experimental data at the individual selection of the parameters for each output curve. Physically unsubstantiated parameters of the atrazine adsorption and degradation were obtained when the parameter of the hydrodynamic dispersion was determined from the data on the ¹⁸O migration. The simulation also showed that the use of parameters obtained at water content close to saturation in the calculations for an unsaturated soil resulted in the overestimation of the leaching rate and the maximum concentration of atrazine in the output curve compared to the experimental data.     

Der Einfluß des Wassergehaltes auf den Atrazin-Abbau im Boden

The influence of water-content on atrazine degradation in soil In samples of the standard soil 2.2 (loamy sand, 3 % C, pH 7,0) and of a Luvisol (Ap-horizon, loam 1,4 % C, pH 5,2), the degradation of [ethyl-1-¹⁴C]atrazine was investigated in dependence of the soil water content. The experimental conditions were choosen in accordance with the methods proposed by the Biologische Bundesanstalt to study the degradation of pesticides in the soil. The soil water content was varied to simulate the moisture conditions observed in a soil during plant growth. Therefore, besides a steady water content of 20, 40, 60, and 80 % of the maximum water holding capacity of the soils, the soil water contents were fluctuated by 20 to 60 % of the maximum water holding capacity by passing dry air through the soil. At a concentration of 10mg atrazin/kg of soil between 4 and 6 % of the ethyl-1-carbonatom of the atrazine molecule was mineralized to CO₂ within 71 days at a constant soil temperature of 22°C. In the standard soil 2.2 the mineralization in total was reduced to 2/3 compared to the degradation in the Luvisol. With decreasing water content increasing hydroxilated metabolites were formed. About 30–40 % of the applied radioactivity was determined as non-extractable residue in the soil. In general the degradation processes were more enhanced and more intense in the Luvisol as compared to the Standard soil 2.2 which again unterlines that for this type of experiments a fresh soil should be used. In conclusion, the variation of the soil water content did not have a pronounced influence on the mineralization rates of atrazine, but did influence the metabolism and the formation of certain metabolite fractions.     

Effect of long-term liquid pig manure application on atrazine mineralization in a soil cultivated with maize

Soil samples were collected in plots from a field experiment in maize monoculture receiving 0, 60 and 120 m³ ha^-1 liquid pig manure (LPM) for 19 years. Soils were sampled from the 0- to 20-cm layer in August and October 1997 and in June, July and September 1998. Subsurface samples were also evaluated in September 1998. Laboratory soil radiorespirometry was used to evaluate atrazine mineralization using [U-ring-¹⁴C]-atrazine mixed with commercially available product. The effect of atrazine dose (50, 100 and 500 mg atrazine kg^-1 soil) was evaluated on soils sampled in August 1997. For the other sampling dates, the soils were spiked with 50 mg atrazine kg^-1 soil. No LPM dose effect on atrazine mineralization was obtained in the different experiments. Increasing atrazine dose to 500 mg kg^-1 decreased significantly the mineralization rate (R_i) and the maximum of atrazine mineralized (MAX), while the time needed to mineralize 50% of MAX (DT-50%) was not significantly affected. Sampling time had a significant effect on atrazine mineralization. Atrazine mineralization in the soils sampled in June 1998 showed lower R_i and MAX than in the soils sampled at the other dates. Atrazine mineralization in subsurface soils (20–60 cm) was very variable and quite high in some samples. This may be due to atrazine pre-exposure in subsoils resulting from atrazine deep movement by preferential flow.     

Aspects of the adsorption and degradation of isoproturon in a heavy clay soil

Abstract. Degradation of isoproturon in a heavy clay soil followed first-order reaction kinetics with half-lives at 15 °C of 27 and 208 days in the topsoil and subsoil, respectively. Adsorption when shaken with 3 mm sieved samples of the soil fitted the empirical Freundlich relationship with k values of 3.25 in the topsoil and 1.06 in the subsoil. Adsorption in a static system with different sized aggregates of soil did not reach equilibrium, even after 24 hours contact, and the rate of adsorption was slower with larger aggregates. Following an adsorption period of 24 hours, desorption equilibrium was reached more rapidly with larger (6–10 mm) than with smaller (<3 mm) aggregates. Adsorption isotherms measured in a static system with a soil:water ratio typical of field conditions in winter also indicated less adsorption than that measured in shaken, laboratory systems with low soil:water ratios. The rate of change in water extractable residues of the herbicide was more rapid than that of total extract-able residues following application of isoproturon to the heavy clay soil in the field. The implications of the results for isoproturon leaching under field conditions are discussed.     

内蒙古河套灌区灌溉入渗对地下水的补给规律及补给系数

为准确估计内蒙河套灌区灌溉水入渗补给地下水量,采用试验研究与数值模拟相结合的方法,分别根据灌水前后地下水位变化和土壤含水率变化计算了灌溉水入渗补给地下水系数,并依据土壤水动力学原理,采用数值模拟验证,得到作物生育期灌溉补给地下水系数为0.15,秋浇灌溉补给地下水系数为0.3。河套灌区地下水位埋深相对较浅,通过灌水前后的土壤含水率变化情况和数值模拟结果显示,灌水2～4 d补给地下水量达到最大,8～10 d后即完成对地下水的入渗补给,不同灌水量灌溉水入渗规律基本一致,入渗补给量和入渗时间与灌溉水量直接相关。研究结果将为确定维持灌区生态环境良性发展的引水量阈值提供参考。