Methyl isothiocyanate volatilization from fields treated with metam‐sodium

Emission of methyl isothiocyanate (MITC) from fields treated with metam‐sodium (sodium N‐methyldithiocarbamate) is a potential environmental and human safety hazard. Concentrations of MITC at three heights above four arable fields were measured following the application of metam‐sodium at a rate of 480 litre ha⁻¹ (166 kg AI ha⁻¹). Two of these fields were treated by injection into a center‐pivot irrigation system (chemigation), while in the other two fields the fumigant was applied through injection directly into the soil. Generally, higher MITC air concentrations were observed above chemigated than above injected fields. Maximum MITC air concentrations were 11.2 and 7.4 µg m⁻³ recorded 10 cm above ground 6–8 h following application and the minimum concentrations were 0.7 and 0.2 µg m⁻³ observed at 200 cm 30–35 h after application above chemigated and injected fields, respectively. The estimated MITC respiratory exposure a worker might encounter during the re‐entry period ranged between 1.37 and 0.03 mg day⁻¹ in chemigated fields and between 0.35 and 0.02 mg day⁻¹ in the injected fields. These results suggest that application of the fumigant through injection reduced MITC volatilization losses in comparison with the chemigation method, thus posing a relatively lower risk of exposure to MITC emissions. © 2000 Society of Chemical Industry     

Model Predictions and Field Measurements of Chlorsulfuron Leaching under Non-steady-state Flow Conditions

Model simulations of chlorsulfuron (1-(2-chlorophenylsulfonyl)-3-(4-methoxy-6-methyl-1,3,5-triazin-2-yl)urea) leaching in a loamy soil were made with the mechanistic dual-porosity model MACRO. Comparisons were made with a data set obtained in a lysimeter experiment in which leaching was measured during an 11-month period after applying chlorsulfuron at two rates (4 and 8 g ha⁻¹). In this experiment, peak concentrations appeared c.6 months after pesticide application, reaching levels of 14 and 21 ng litre⁻¹ in the low- and high-dose treatments, respectively. These peak concentrations appeared after c.70 mm of accumulated leachate, implying that some of the herbicide was displaced through the soil columns by non-equilibrium flow processes. Model calibration was limited to parameters related to evapotranspiration, water uptake by roots and degradation rates in the subsoil. With this minimum amount of calibration, the model successfully described the leaching pattern of chlorsulfuron, provided that the two-flow domain option in the model was used. Running the model in one-flow domain resulted in considerable underestimates of leaching of chlorsulfuron over the short-term (<1 year). The degradation rate in the subsoil was also found to be critical. It had to be increased about fivefold to match measured chlorsulfuron concentrations in leachate. At such concentrations, 0·012 g ha⁻¹ of chlorsulfuron (0·3% of that applied) was predicted to leach through the soil profile during the 11-month simulation period when the lower dose of the compound was applied.     

Pharmacokinetics of fenvalerate after intravenous administration to sheep

The pharmacokinetics of total radioactivity and of intact fenvalerate were determined in sheep treated intravenously with radiolabelled or non-radiolabelled fenvalerate. Mean residence times (MRT) of total radioactivity and intact fenvalerate in plasma were 910 (±75) and 39 (±3) min, while harmonic mean elimination-phase half-lives (TM_β) were 990 and 82 min, each respectively. Systemic clearance values (Cl_S) of total radioactivity and intact fenvalerate were 2·8 (±0·3) ml min⁻¹ kg⁻¹ and 51·3 (±5·9) ml min⁻¹ kg⁻¹, respectively. Volumes of distribution at steady state (V_SS) were each near 2500 ml kg⁻¹. Elimination of radioactivity occurred, in part (33·3 (±3·3)% of dose), by renal excretion, at a rate (0·9 (±0·1) ml min⁻¹ kg⁻¹), similar to that of glomerular filtration. These data are consistent with a disposition model according to which intact fenvalerate was rapidly distributed into a peripheral compartment, where metabolism occurred. In addition, since the elimination half-life of fenvalerate from plasma was less than 90 min after intravenous injection, ‘flip-flop’ kinetics should be considered when longer elimination half-lives are observed after oral or dermal exposures.     

Aerobic Metabolism of Flupropacil in Sandy Loam Soil

The aerobic soil metabolism of [¹⁴C]flupropacil (isopropyl 2-chloro-5-(1,2,3,6-tetrahydro-3-methyl-2,6-dioxo-4-trifluoromethylpyrimidin-1-yl)benzoate) was determined in microbially active, sieved (2-mm) sandy loam soil with a soil moisture content of 75% at 1/3 bar. The soil was treated with [¹⁴C]flupropacil at 0·5 mg kg⁻¹ (twice the field use rate) and placed in incubation flasks connected to a series of traps (50 g litre⁻¹ NaOH, 0·5M H₂SO₄, ethylene glycol) and incubated at 25(±1)°C. Soil was sampled at 0, 3, 9, 20, 30, 48, 76, 120, 181 and 238 days of aerobic incubation. Volatiles were collected once every two weeks and on the day of soil sampling. Flupropacil metabolized with a half-life of 79 days under aerobic conditions. The major metabolite was flupropacil acid which accounted for up to 69·1% of the initially applied radioactivity at Day 238. Each of the two minor metabolites detected at the end of the study accounted for less than 0·5%. One of the minor metabolites was identified as C4242 acid (2-chloro-5-(1,2,3,6-tetrahydro-2,6-dioxo-4-trifluoromethylpyrimidin-1-yl)benzoic acid). Only a negligible portion (less than 0·3%) of the applied flupropacil was mineralized to [¹⁴C]carbon dioxide. Extractable radioactivity ranged from 78·9% to 95·5%, with bound residues accounting for 3·2%–23·4%. The material balance ranged from 91·6% to 104·4%.     

滴灌施肥条件下土壤水氮运移数值模拟

为了研究滴灌施肥条件下土壤水、氮的运移分布规律,本文通过室内土柱滴灌水氮入渗试验,研究了滴灌结束时及再分布过程中土壤水、氮的运移变化规律;同时用HYDRUS软件建立了土柱滴灌水氮入渗的几何模型,用来模拟滴灌土壤水氮运移过程。对试验及模拟中12个观测点测得的土壤含水率、土壤铵态氮、硝态氮质量浓度进行对比分析,结果表明：土壤含水率模拟值与实测值的相对误差变化在10%以内;土壤铵态氮、硝态氮质量浓度的模拟值与实测值变化范围在20%以内。滴灌结束时土体剖面内土壤含水率随距滴头距离的增大而减小,再分布72 h土层25~30 cm土壤含水率增大到0.2 cm³·cm^-3,120 h后土体剖面内土壤含水率较滴灌结束时下降了18%。土壤铵态氮质量浓度主要分布于距滴头20 cm的范围;24 h土壤铵态氮质量浓度最大,且随着时间的推移逐渐减小,到120 h时减少了40%;各观测点24 h至120 h土壤硝态氮质量浓度随着时间的推移逐渐增大,且硝态氮质量浓度在滴头20 cm的范围内由0.442 mg·cm^-3增加到1.2 mg·cm^-3。各观测点24 h土壤硝态氮质量浓度在空间分布上差异不大,其中观测点1,3,6,8,5的土壤硝态氮质量浓度分别为0.437,0.467,0.451,0.482 mg·cm^-3和0.447 mg·cm^-3,差值均小于0.05 mg·cm^-3;48 h后土体剖面内土壤硝态氮质量浓度空间分布随离滴头距离的增加而减小,垂直方向上从距滴头5 cm的观测点1到距滴头25 cm的观测点8减少了53%。依据研究结果,可用数值模型模拟滴灌施肥条件下土壤水氮运移的变化规律。     

Leaching of Alachlor from Alginate-Encapsulated Controlled-Release Formulations

The mobility of alachlor from alginate-encapsulated controlled-release (CR) formulations was investigated in two contrasting soil profiles. Two CR formulations of alachlor were prepared with the following components (1) base—sodium alginate+kaolin+‘Tween’ 20 (1+10+0·5 by mass) and (2) base+40 g kg⁻¹ linseed oil. These were compared to technical grade alachlor and to a commercial alachlor EC formulation (‘Lasso’ 4EC). All herbicide treatments were labeled with [¹⁴C]alachlor and were applied to duplicate soil columns that were composed of a surface and a subsoil horizon. Each horizon was packed to a depth of 12·5 cm, giving a total column length of 25 cm. The columns were leached with 21 cm (420 ml) to 30 cm (600 ml) of 0·01M calcium chloride for a period of 7 to 10 days. Alachlor leaching from the EC formulations was the same as that from the technical material in both soils: 33% in the Evesboro and 10% in the Conover soil. The CR-Oil formulation leached 4 and 2% of the applied [¹⁴C]alachlor, compared to 12 and 3% for the CR-N formulation for the Evesboro and Conover soils, respectively. The CR-Oil formulation also increased the amount of [¹⁴C]alachlor retained in the soil surface horizon (105–114%), compared to CR-N (39–45%), technical material (14–23%) and EC (12–17%).     

黄土塬区土地利用方式对土壤主要理化性质的影响

通过对陕西长武4种典型土地利用方式下0~500 cm土层土壤主要理化性质分析,以明确土地利用方式对土壤理化性质的影响。结果表明：农田、果园土壤有机质、全氮含量显著高于荒地和刺槐林地,土壤粘粒含量与土壤容重呈显著负相关关系,与土壤饱和导水率呈显著正相关关系;农田0~100 cm土层土壤容重达1.44 g·cm^-3,显著高于同深度荒地（1.27 g·cm^-3）、果园（1.38 g·cm^-3）、刺槐林地（1.32 g·cm^-3）土层;400~500 cm土层土壤含水量为刺槐林地（86 g·kg^-1）<果园（113 g·kg^-1）<荒地（152 g·kg^-1）<农田（165 g·kg^-1）;果园和刺槐林地0~500 cm土层土壤平均饱和导水率分别为0.37、0.36 mm·min^-1,显著高于农田（0.25 mm·min^-1）和荒地（0.23 mm·min^-1）。退耕还林（草）导致土壤容重降低、饱和导水率增加,有助于降水入渗,但退耕后深层土壤有干燥化的倾向。     

Concentration-Dependent Mobility of Chlorfenvinphos in Isolated Plant Cuticles

The mobility of chlorfenvinphos in isolated pear (Pyrus communis cv. Bartlett) leaf cuticular membranes (CM) was studied as a function of concentration of chlorfenvinphos sorbed in the cuticle. Mobilities of chlorfenvinphos increased approximately 9-fold when the amount sorbed increased from 1 to 100 μg cm⁻² pear leaf cuticle. From the amounts per area, average volume fractions of chlorfenvinphos in the cuticle were calculated ranging from 2×10⁻³ to 5·1×10⁻². The increase in mobilities was steepest at the lower and levelled off at higher volume fractions. This correlation could be described for the whole range of volume fractions investigated by an equation which assumes homogeneously dispersed chlorfenvinphos. Temperature dependence of mobilities was studied at 17, 25 and 35°C and chlorfenvinphos volume fractions of 5·5×10⁻³ and 0·12, respectively. Arrhenius graphs were linear for both volume fractions, showing that cuticles did not undergo a phase transition due to the high amount of sorbed chlorfenvinphos. However, at a volume fraction of 0·12, the activation energy of diffusion, E_D, was significantly lower (83·6 kJ mol⁻¹) than at 5·5×10⁻³ (135 kJ mol⁻¹). We interpret these findings as evidence for a plasticising effect on cuticular waxes by chlorfenvinphos. So far, such an effect had been demonstrated only for certain adjuvants (ethoxylated alcohols) but not for active ingredients. Chlorfenvinphos not only increased its own mobility in pear leaf cuticles, but also that of 2,4-D in Citrus leaf cuticles. This would be expected if plasticising of waxes was the sole mechanism responsible for increased mobilities. From these data we predict that permeabilities of cuticles to chlorfenvinphos are not constant. Depending on temperature as well as types and amounts of adjuvants, rates of foliar penetration of chlorfenvinphos can be higher if its concentration in the spray liquid is increased.     

Bentazone Leaching in Spanish Soils

Adsorption, incubation and soil-column experiments with bentazone [3-isopropyl-1H-2,1,3-benzothiadiazin-4(3H)-one 2,2-dioxide] were carried out in ten different soils from the marches surrounding the Doñana National Park (Huelva, SW Spain). Adsorption isotherms for the different soils showed a good fit with the Freundlich equation. Bentazone was poorly adsorbed in all the soils studied, with no significant relationship between theK_f values and soil characteristics. A significant correlation was obtained between the soil organic matter content and the distribution constant values (K_d) calculated at an equilibrium concentration of 200 μg cm⁻³. The low adsorption and non-degradation of bentazone on these soils suggest that the herbicide readily percolates through soils to reach the surface and ground waters. The mobility of bentazone through three soil columns was also studied. The mass balances carried out showed that bentazone was totally eluted from the soil columns. The theoretical model applied to explain bentazone leaching under our experimental conditions seems to be suitable for soil columns with a uniform water-flow rate.     

东北春玉米不同发育期干旱胁迫对根系生长的影响

分别在玉米拔节期(BJ)和抽雄期(CX)进行水分胁迫试验,利用微根管技术观测不同发育期干旱过程中根分布动态,并利用根分布模型模拟相关参数(d_(50)和d_(95):累积根比例分别为50%和95%的土层深度),对不同干旱胁迫处理的土壤湿度、根系分布及相关参数时空动态特征进行分析。结果表明:水分控制后的土壤湿度在130cm以上基本达到预期干旱效果,即BJ和CX处理在控水时段0~100 cm土层土壤相对湿度都降至40%以下,但深层土壤湿度并未受到水分控制影响;拔节和抽雄期干旱胁迫条件下,根长密度(RLD)最大值分别为2.18±0.89cm·cm~(-3)和2.10±0.47 cm·cm~(-3),所在土壤深度为60 cm,对照(CK)RLD最大值为1.24±0.77 cm·cm~(-3),所在深度为40 cm,CK和BJ处理的RLD在最大值深度以下随土层深度增加而减小,CX处理的RLD在80 cm以下仍保持较大值;BJ和CX比CK的d50分别增大45%和59%,d95分别增大8%和41%,证明玉米根系因干旱胁迫而向深层土壤生长。     

Presence of Muscarinic Acetylcholine Receptors in the Cattle Tick Boophilus microplus and in Epithelial Tissue Culture Cells of Chironomus tentans

A muscarinic acetylcholine receptor (mAChR) has been demonstrated and partially characterized in larvae of the cattle tick Boophilus microplus. Its properties are compared with mAChR from an epithelial cell line from the dipteran insect Chironomus tentans. Competition studies with cholinergic ligands of different specificity revealed the muscarinic nature of the cholinergic receptors investigated in both species. In homogenates from tick larvae, specific binding sites for [³H]quinuclidinyl benzilate (QNB) with high affinity (1·2±(0·13) nM ; B_max 22·5 pmol mg protein⁻¹) were detected that do not bind nicotinic compounds specifically. The estimated IC₅₀ values for nicotine, imidacloprid and α-bungarotoxin were all in the mM range. Additionally, with tick larvae, high-affinity nicotinic binding sites were detected with [³H]nicotine which could be displaced by high concentrations of imidacloprid or QNB. The estimated IC₅₀ values for nicotine, α-bungarotoxin, imidacloprid and QNB were 43(±8) nM , 0·8(±0·2) μM , 2·8(±0·6) μM and 78(±1·9) μM , respectively. With homogenates of the non-neuronal insect cell line from C. tentans, only high-affinity binding sites for [³H]QNB were found. Muscarinic antagonists selectively displaced [³H]quinuclidinyl benzilate (QNB) binding to tick larvae homogenates. The mAChR of B. microplus preferred pirenzepine (IC₅₀ 2·13(±1·02) μM ) among different subtype-specific mAChR antagonists (4-DAMP had IC₅₀ 49·9(±9·13) μM and methoctramine had IC₅₀ 121(±14·2) μM ) indicating a type of binding site similar to the vertebrate M1 mAChR subtype. The tick muscarinic receptor seems to be a G-protein-coupled receptor, as concluded from the 4·8-fold reduction in receptor affinity for binding of the muscarinic agonist oxotremorine M upon treatment with the non-hydrolysable GTP-analogue γ-S-GTP. Binding data for the agonists oxotremorine M (IC₅₀ 71·3(±19·6) μM ) and carbachol (IC₅₀ 253(±87·1) μM ) parallel the biological efficacy of these compounds, in that, while oxotremorine M showed some activity against ticks, carbachol was ineffective.     

Movement of dieldrin through soils: II.—In sloping troughs and soil columns

A glass-lined trough was divided into six compartments by vertical transverse partitions and filled with soil to a height of 5 cm above the top of each partition. The base of the box and the surface of the soil sloped forwards one end with a gradient of 1 in 3·7. Dieldrin was applied (22 kg active ingredient/ha) to the soil surface in the uppermost compartment and the movement of dieldrin into leachate and down the slope was followed for 17 weeks. During this time 19·5 cm of rain fell. Less than 0·02% of the dieldrin appeared in the leachate and 99% of this was collected during the first 9 weeks, mainly from the uppermost compartment. Very little dieldrin moved down the slope and it was not detected in the leachate from compartments other than the treated one during 9–17 weeks after treatment. In other experiments, 3 cylinders were filled respectively with sandy loam, heavy clay loam and peat which were transferred from the field as intact cores. Three other cylinders were filled with soils of the same types but broken up. Approximately 2% of the dieldrin leached through one column but usually it was much less than 0·1%. The largest amounts of dieldrin were leached down columns of heavy clay loam, intermediate amounts down columns of peat, and least through sandy loam. Ten times as much dieldrin leached down the columns of intact soil as through those with broken soil. The results indicate that the movement of dieldrin from treated soil into water systems by leaching is limited and is unlikely to be a major pathway for the contamination of water.     

容重及含水率对土壤电导率的影响研究

土壤电导率能够间接反映田间养分或盐分含量,通过监测土壤电导率可以掌握土壤养分或盐分运移和利用情况。本文通过2种土壤容重、5种含水率条件下土柱入渗试验,利用5TE传感器对土壤体积含水率、体积电导率、温度等参数进行连续监测,分析容重及含水率对土壤电导率的影响。结果表明：在入渗过程中,含水率和电导率均先增大后逐渐减小,最后趋于平缓;电导率开始减小的时间较含水率开始减小的时间略有提前;当体积含水率一定时,孔隙水电导率随体积电导率的增加基本呈线性增加;随含水率的增大,孔隙水电导率随体积水电导率增大的速率变慢;当体积电导率一定时,随着含水率的增加,孔隙水电导率逐渐减小,容重为1.35 g·cm^-3时减幅为9.52%～55.51%,容重为1.3 g·cm^-3时减幅为9.72%～54.62%;孔隙水电导率一定时,体积电导率随含水率的增加而增大,容重为1.35 g·cm^-3时增幅为10.51%～124.75%,容重为1.3 g·cm^-3时增幅为10.76%～120.35%。对于2种容重情况,相同含水率下孔隙水电导率与...     

Fate of chlorsulfuron in the environment. 1. Laboratory evaluations

The behaviour and fate of chlorsulfuron in aqueous and soil systems were examined in laboratory studies. Aqueous hydrolysis was pH-dependent and followed pseudo-first-order degradation kinetics at 25°C, with faster hydrolysis occurring at pH 5 (half-life 24 days) than at either pH 7 or 9 (half-lives >365 days). Degradation occurred primarily by cleavage of the sulfonylurea bridge to form the major metabolites chlorobenzenesulfonamide (2-chlorobenzenesulfonamide) and triazine amine (4-methoxy-6-methyl-1,3,5-triazin-2-amine). This route is a major degradation pathway in water and soil systems. Aqueous photolysis (corrected for hydrolysis) proceeded much more slowly (half-life 198 days) than aqueous hydrolysis and is not expected to contribute significantly to overall degradation. Hydrolysis in soil thin-layer plates exposed to light (half-life 80 days), however, progressed at a much faster rate than in dark controls (half life 130 days), which suggests that a mechanism other than direct photolysis may have been operative. An aerobic soil metabolism study (25°C) in a Keyport silt loam soil (pH 6·4, 2·8% OM) showed that degradation was rapid (half-life 20 days). Dissipation in an anaerobic sediment/water system (initial pH of water phase 6·7, final pH 7·4) progressed much more slowly (half-life >365 days) than in aerobic soil systems. Major degradation products in aerobic soil included the chlorobenzenesulfonamide and triazine amine as in the aqueous hydrolysis study. Neither of these degradation products exhibited phytotoxicity to a variety of crop and weed species in a glasshouse experiment, and both exhibited an acute toxicological profile similar to that of chlorsulfuron in a battery of standard tests. Demethylation of the 4-methoxy group on the triazine moiety and subsequent cleavage of the triazine ring is another pathway found in both aqueous solution and soils, though different bonds on the triazine amine appear to be cleaved in the two systems. Hydroxylation of the benzenesulfonamide moiety is a minor degradation pathway found in soils. Two soils amended with 0·1 and 1·0 mg kg^-1 chlorsulfuron showed slight stimulation of nitrification. The 1·0 mg kg^-1 concentration of chlorsulfuron resulted in minor stimulation and inhibition of ¹⁴C-cellulose and ¹⁴C-protein degradation, respectively, in the same soils. Batch equilibrium adsorption studies conducted on four soils showed that adsorption was low in this system (K_oc 13–54). Soil thin-layer chromatography of chlorsulfuron (R_f=0·55–0·86) and its major degradation products demonstrated that the chlorobenzenesulfonamide (R_f=0·34–0·68) had slightly less mobility and that the triazine amine (R_f=0·035–0·40) was much less mobile than chlorsulfuron. In an aged column leaching study, subsamples of a Fallsington sandy loam (pH_water 5·6, OM 1·4%) or a Flanagan silt loam (pH_water 6·4, OM 4·0%) were treated with chlorsulfuron, aged moist for 30 days in a glasshouse and then placed upon a prewet column of the same soil type prior to initiation of leaching. This treatment resulted in the retention of much more total radioactivity (including degradation products) than by a prewet column, where initiation of leaching began immediately after chlorsulfuron application, without aging (primarily chlorsulfuron parent). © 1998 SCI     

基于HYDRUS模型的暗管排水水盐运移模拟

为了探索暗管排水条件下膜下滴灌农田的水盐运移规律,本文设计了埋深1 m,间距4 m的暗管排水模型试验,研究分析灌水淋洗过程中土壤水分和盐分的动态变化规律,并利用HYDRUS模型对暗管排水条件下的水盐运移规律进行数值模拟分析与验证。结果表明：经过3次灌水淋洗后,表层0~20 cm土层内盐分含量下降至2 g·kg^-1,达到了非盐化土水平,20~60 cm土体内上层土壤脱盐效果高于下层,总盐分含量下降至8 g·kg^-1以下;经过实测值与模拟值的验证,土壤盐分和水分的均方根误差RMSE最大分别为0.632和1.324,决定系数R²最小分别为0.992和0.906,说明模拟结果与实测结果吻合度较好,HYDRUS模型能够较好地模拟暗管排水过程中水盐运移规律。通过模型模拟6次灌水（共90 d）后暗管排水条件下不同土层深度的水盐动态变化特征,模拟结果表明,0~40 cm土层内盐分含量下降至2 g·kg^-1,40~80 cm土层内盐分含量下降至4 g·kg^-1左右,基本达到轻度盐化水平;距离暗管不同间距处的土壤剖面盐分含量呈波动变化,距离暗管越远,土壤剖面含盐量越大,盐分含量在0~8 g·kg^-1范围内变化。     

微咸水膜下滴灌对土壤水盐分布及加工番茄产量的影响

为探明微咸水膜下滴灌对土壤水盐分布及加工番茄生长和产量的影响,通过大田小区试验,设置灌水矿化度和灌水定额两个因素,其中3个灌溉水矿化度水平分别为S1:1 g·L~(-1)、S2:3 g·L~(-1)和S3:5 g·L~(-1),3个灌水定额分别为W1:305 m~3·hm~(-2)、W2:458 m~3·hm~(-2)和W3:611 m~3·hm~(-2),来进一步寻求适宜本地区加工番茄生长的微咸水膜下滴灌灌溉制度。结果表明:覆膜微咸水滴灌条件下土壤含水量垂直方向的变化趋势表现为0～20 cm土层随深度增加含水量逐渐降低、20～100 cm土层随深度增加含水量逐渐增大、60～100 cm范围内土层剖面含水量最大的分布规律;土壤含盐量随着灌水矿化度的增大而增加,且随着灌水量的增加土壤盐分逐渐向水平距滴灌带35 cm处聚集。灌水矿化度超过3 g·L~(-1)时加工番茄株高、茎粗均受到一定程度的抑制作用,但对产量影响不大。本文通过试验得出:灌水定额为611 m~3·hm~(-2)、矿化度为1 g·L~(-1)处理为本地区最佳微咸水膜下滴灌处理,加工番茄生长健壮且产量最高,达到127 613.2 kg·hm~(-2);同时认为,在我国淡水资源比较缺乏的新疆地区可以考虑采用灌水定额458 m~3·hm~(-2)和灌水矿化度3～5 g·L~(-1)的微咸水对盐分中等敏感的加工番茄进行灌溉。     

猕猴桃园和小麦—玉米轮作田两种土地利用方式对土壤养分状况的影响

为深入了解不同土地利用方式下土壤养分水平的差异及施肥和管理中存在的问题,选取陕西省周至县农耕区为研究区域,采用地统计分析和GIS相结合的方法,研究了猕猴桃园和小麦—玉米轮作田两种不同土地利用类型下土壤养分含量、养分相关性、空间变异特征及其分布格局。结果表明:猕猴桃园有机质、碱解氮、有效磷和速效钾4种养分含量分别为:(19.55±3.13)g·kg~(~(-1)),(80.58±14.69)mg·kg~(~(-1)),(23.37±6.09)mg·kg~(~(-1)),(102.79±12.74)mg·kg~(~(-1)),pH值为7.32±0.49;小麦—玉米农田有机质、碱解氮、有效磷和速效钾4种养分含量分别为:(19.43±2.63)g·kg~(~(-1)),(78.80±11.39)mg·kg~(~(-1)),(24.83±6.06)mg·kg~(~(-1)),(95.03±11.75)mg·kg~(~(-1)),pH值为7.41±0.58。猕猴桃园土壤有机质、碱解氮和速效钾含量均高于小麦—玉米农田,仅有效磷含量比小麦—玉米农田偏低。研究区主要养分要素的变异系数都处于10%~100%,属于中等空间变异性。在猕猴桃园中,有机质、碱解氮、有效磷、速效钾两两之间均呈极显著或显著正相关;在小麦—玉米农田,pH值与有机质表现出显著负相关。研究区土壤有效磷含量较为丰富,碱解氮含量处于中等偏高水平,有机质含量处于中等偏低水平,而速效钾含量总体缺乏。整体上猕猴桃园比小麦—玉米农田养分水平高,这主要与不同的田间管理和施肥状况有关。因此,今后应采取维持氮肥、控制磷肥、增加钾肥的措施,并十分重视有机肥的使用。此外,针对不同土地利用类型和土壤肥力状况进行分区培肥管理,普及科学施肥,提高肥料利用效率也是提升土壤肥力水平的重要措施。     

咸水灌溉对土壤水盐分布及设施番茄产量和品质的影响

为探明咸水灌溉对土壤水盐分布及设施番茄植株生长、产量和品质的影响,本试验以南疆地区设施番茄为研究对象,设置4个灌溉水矿化度,分别为2 g·L^-1（T1）、4 g·L^-1（T2）、6 g·L^-1（T3）和8 g·L^-1（T4）,并以淡水灌溉为对照（CK）,开展同一灌水定额条件下设施番茄适宜灌水矿化度的研究。结果表明：不同生育期阶段土壤含水率基本表现为20～60 cm土层较高,表层及深层土壤含水率相对较低,土壤含水率随着灌水矿化度的增大逐渐增加;0～80 cm土层平均土壤含水率在生育期内逐渐降低,且深层土壤降幅显著;生育期初始阶段土壤含盐量主要积聚在0～40 cm土层,随着生育期的推进土壤盐分呈累积趋势且向深层土壤运移,生育期末主要积聚在0～60 cm土层;灌水矿化度小于4 g·L^-1时0～20 cm土层整体呈脱盐状态,其中CK处理平均脱盐率达27.79%,T1处理平均脱盐率达17.07%;灌水矿化度2～4 g·L^-1促进了番茄植株生长,株高和茎粗相较CK分别...     

不同覆膜连作年限对玛纳斯县棉田土壤质量的影响

为研究不同覆膜连作年限对玛纳斯县棉田土壤质量的影响,以新疆玛纳斯县覆膜连作0、5、10、20、30 a的棉田为研究对象,分别采集0~10、10~20、20~30 cm土层土壤,测定其土壤理化性质、土壤酶活性、土壤微生物量碳、氮含量等指标,并对不同覆膜连作年限玛纳斯县棉田的土壤质量进行综合评价。结果表明：（1）随覆膜连作年限的增加,土壤含水率和有机质含量逐渐增加,以覆膜连作30 a时最高,分别为11.52%和21.60 g·kg^-1,土壤速效磷呈先升高后降低趋势,在覆膜连作10 a时含量最高（49.60 mg·kg^-1）,土壤电导率、总盐、速效钾和碱解氮总体呈降低趋势,在覆膜连作年限30 a时含量最低,分别为0.50 mS·cm^-1、0.69 g·kg^-1、148.28 mg·kg^-1和25.27 mg·kg^-1;同一覆膜连作年限下,随着土层深度的增加,土壤含水率、电导率和总盐逐渐增加,pH值、有机质、速效磷、速效钾和碱解氮含量逐渐降低。（2）在不同覆膜连作年限下,土壤蔗糖酶、脲酶、碱性磷酸酶活性随覆膜连作年限的增加呈先升高后降低趋势,在覆膜连作10 a时活性最高,分别为10.57 mg·g^-1·d^-1、0.86 mg·g^-1·d^-1、0.40 mg·g^-1·d^-1,土壤过氧化氢酶活性随不同覆膜连作年限并无显著变化,为1.80~2.20 mL·g^-1;在同一覆膜连作年限下,土壤脲酶、碱性磷酸酶活性均表现为表层>深层,且差异显著。随覆膜连作年限的增加,土壤微生物量碳含量呈现先增加后减少的趋势,最高为205.26 mg·kg^-1,微生物量氮含量逐渐降低,最低在覆膜连作30 a时为11.40 mg·kg^-1,且不同土层土壤微生物量碳、氮表现为表层>深层。（3）土壤速效磷与过氧化氢酶、脲酶、碱性磷酸酶活性和微生物量碳呈极显著正相关关系,与蔗糖酶活性呈显著正相关关系,表明土壤速效磷是影响土壤酶活性和微生物量碳、氮的主要因素。土壤质量综合评价表明,以覆膜连作10 a的土壤质量最佳,0 a和30 a的土壤质量相对较低。     

石羊河流域制种玉米咸淡水轮灌模式 的SWAP模型模拟

为了探究石羊河流域制种玉米的咸淡水轮灌模式,利用2014年田间试验观测资料对SWAP模型进行了参数率定和验证,模拟了不同咸淡水轮灌模式下的土壤水盐平衡,并筛选出了较优的咸淡水轮灌模式,预测了较长时期土壤盐分动态变化及制种玉米产量。结果表明：SWAP模型率定与验证过程中,土壤含水量的均方误差(RMSE)值在0.05 cm³·cm^-3以下,平均相对误差（MRE)值在15%以下;土壤含盐量的RMSE值在4.2 mg·cm^-3以下,MRE值在25%以下;制种玉米产量的RMSE值在380 kg·hm^-2以内,MRE值在10%以下,率定和验证后的SWAP模型可用于研究区咸水与淡水灌溉的模拟与预测。3.0 g·L^-1微咸水条件下采用2次淡水、1次咸水和1次淡水、2次咸水的轮灌方式以及6.0 g·L^-1咸水条件下采用2次淡水、1次咸水的轮灌方式为研究区制种玉米的较优轮灌模式,这3种较优咸淡水轮灌模式下的土壤盐分累积量较少,并且能够提高制种玉米的产量。3种较优轮灌模式模拟预测结果显示,在模拟期内土壤含盐量增幅不大,能够达到平稳,不会造成土壤盐渍化,制种玉米减产幅度较小,制种玉米产量能够保持平稳。