The relative movement and persistence in soil of chlorsulfuron, metsulfuron-methyl and triasulfuron

Summary. Adsorption and degradation rates of triasulfuron in 8 different soils were negatively correlated with soil pH and were generally lower in subsoils than in soils from the plough layer. The half-life at 20°C varied from 33 days in a top soil at pH 5·8 to 120 days in a subsoil at pH 7·4. Adsorption distribution coefficients in these two soils were 0·55 and 0·19, respectively. Movement and persistence of residues of chlorsulfuron, triasulfuron and metsulfuron-methyl were compared in a field experiment prepared in spring 1987. Triasulfuron was less mobile in the soil than the other two compounds. Residues of all three herbicides were largely confined to the upper 40–50 cm soil 148 days after application. With an initial dose of 32 g ha⁻¹, residues in the surface soil layers were sufficient to affect growth of lettuce and sugar-beet sown approximately one year after application. Laboratory adsorption and degradation data were used with appropriate weather data in a computer model of herbicide transport in soil. The model gave good predictions of total soil residues during the first five months following application, and also predicted successfully the maximum depth of penetration of the herbicides into the soil during this period. However, more herbicide was retained close to the soil surface than was predicted by the model. The model predicted extensive movement of the herbicides in the soil during winter but did not predict that residues sufficient to affect crop growth could be present in the upper 15–20 cm soil after one year.     

The degradation of simazine, linuron and propyzamide in different soils

Simazine, linuron and propyzamide were incubated in 18 different soils at 25°C and field capacity soil moisture content. The degradation of each herbicide followed first-order kinetics. The half-life of simazine varied from 20 to 44 days, that of linuron from 22 to 86 days and that of propyzamide from 10 to 32 days. The rate of linuron degradation was highly significantly correlated with soil organic matter content, clay content, soil respiration and the extent of herbicide adsorption by the soil. The rate of simazine degradation was significantly and negatively correlated with soil pH, but the rate of propyzamide degradation was not related with any of the soil factors examined.     

黄土区不同退耕年限草地土壤分离速率及其理化性质

以子午岭连家砭林场不同退耕年限草地为研究对象,以撂荒地为对照,通过野外调查和室内测试分析,研究了退耕12 a、18 a、24 a、36 a草地土壤分离速率及其理化性质。结果表明:草地土壤分离速率与同一土层的撂荒地相比明显降低,并随着退耕年限增加而降低。不同退耕年限草地土壤容重、有机质含量、水稳性团聚体含量、根系生物量密度均有不同程度的改变,且表层土壤(0~20 cm)理化性质改善最为显著(P0.05);不同退耕年限草地土壤分离速率与其理化性质均呈显著相关关系(P0.05),但对于不同退耕年限草地,影响土壤分离速率的主导因子不同。     

博尔塔拉河下游河岸带土壤养分特征及其相关性分析

对博尔塔拉河下游河岸带土壤有机质、全氮、速效磷、速效钾、pH进行了分析。结果表明：① 土壤有机质在表层和80 cm土层属于强变异;20 cm、40 cm和60 cm土层属于中等变异。② 有机质含量为0.03%～4.19%,差值较大;不同深度土壤有机质含量从表层到深层逐渐减少,递减规律显著;5层（0~10 cm、20 cm、40 cm、60 cm和80 cm）土壤之间有机质含量垂直方向的相关性特征显示,60 cm深度与其他层次土壤有机质含量呈弱正和弱负相关,0 cm与80 cm、20 cm与40 cm之间的相关性极显著。③ 土壤有机质含量与pH、速效钾含量呈负相关,与速效磷含量呈正相关,与全氮呈极显著正相关（[WTBX]R[WTBZ]=0.934）。④ 通过对土壤样品养分含量分级显示,土壤有机质含量和速效磷含量平均值分别为0.44%和1.99 mg•kg^-1,均属于极缺乏型;全氮含量和速效钾含量平均为0.07%和39.78 mg•kg^-1,属于很缺乏型;pH平均为7.47,属于中性。     

The fate of imazapyr in a Swedish railway embankment

The long-term fate of the herbicide imazapyr [2-(4-isopropyl-4-methyl-5-oxo-2-imidazolin-2-yl)nicotinic acid] applied to a Swedish railway embankment was studied. Imazapyr was applied at 750 and 1500 g ha(-1) by a spraying train used for full-scale herbicide treatment operations. Soil and groundwater were sampled twice a year for 8 years after application of the herbicide, and the dissipation of imazapyr was studied by HPLC analysis of the residues in soil and groundwater. A clean-up procedure including solid-phase extraction was performed prior to detection by HPLC. Recoveries of imazapyr from soil and water samples were 76-98% and 61-90%, respectively, and detection levels were 0.003 mg kg(-1) and 0.05 microg litre(-1), respectively. Sorption, desorption and microbial amount and activity were also measured at the two locations. The organic matter content correlated positively and the pH negatively to the adsorption of imazapyr on soil, and increasing organic matter contents decreased desorption. Apart from the 0-10-cm top layers of both sites, the microbial amount and activity were small. The main proportion of imazapyr was found in the upper 30 cm of the soil, and degraded with a half-life in the range 67-144 days. Small amounts were transported to lower soil layers and to the groundwater in proportion to the amounts applied. Traces of imazapyr were detected in the groundwater even 8years after application. It was concluded that environmental risks from the use of herbicides on railway embankments could be reduced by including adsorption layers in the embankment during their construction and by reducing the dose of the herbicide used.     

巴音布鲁克主要草地类型表层土壤有机碳特征及其影响因素的研究

以新疆天山中段巴音布鲁克主要草地类型为研究对象,分析了不同草地类型土壤有机碳(SOC)的分布特征及其与气候因子、植被特征和土壤特性的关系。结果表明:分布在盆地海拔最低处的高山沼泽化草甸的土壤有机碳含量最高,而分布在盆地中间海拔的高山草原最低,分布在较高海拔的高寒草甸和高山草原化草甸处于高山沼泽化草甸和高山草原之间。0-30cm土壤有机碳含量与空气相对湿度、草地生产力、植被盖度、土壤含水量呈显著正相关(P<0.05),与土壤容重、土壤紧实度、土壤pH呈显著负相关(P<0.05),土壤有机碳与温度存在一定负相关,但未达到显著水平。偏相关分析显示,影响表层土壤有机碳含量最主要的因素是土壤含水量、土壤紧实度、草地生产力、空气相对湿度。     

Adsorption and degradation of four acidic herbicides in soils from southern Spain

BACKGROUND: Pesticide degradation and adsorption in soils are key processes determining whether pesticide use will have any impact on environmental quality. Pesticide degradation in soil generally results in a reduction in toxicity, but some pesticides have breakdown products that are more toxic than the parent compound. Adsorption to soil particles ensures that herbicide is retained in the place where its biological activity is expressed and also determines potential for transportation away from the site of action. Degradation and adsorption are complex processes, and shortcomings in understanding them still restrict the ability to predict the fate and behaviour of ionisable pesticides. This paper reports the sorption and degradation behaviour of four acidic pesticides in five soils from southern Spain. Results are used to investigate the influence of soil and pesticide properties on adsorption and degradation as well as the potential link between the two processes. RESULTS: Adsorption and degradation of four acidic pesticides were measured in four soils from Spain characterised by small organic matter (OM) contents (0.3-1.0%) and varying clay contents (3-66%). In general, sorption increased in the order dicamba < metsulfuron-methyl < 2,4-D < flupyrsulfuron-methyl-sodium. Both OM and clay content were found to be important in determining adsorption, but relative differences in clay content between soils were much larger than those in OM content, and therefore clay content was the main property determining the extent of herbicide adsorption for these soils. pH was negatively correlated with adsorption for all compounds apart from metsulfuron-methyl. A clear positive correlation was observed for degradation rate with clay and OM content (P < 0.01), and a negative correlation was observed with pH (P < 0.01). The exception was metsulfuron-methyl, for which degradation was found to be significantly correlated only with soil bioactivity (P < 0.05). CONCLUSIONS: Both OM and clay content were found to be important in determining adsorption, but relative differences in clay content between soils were much larger than those in OM content, and therefore clay content was the main property determining the extent of herbicide adsorption for soils of this type. pH was negatively correlated with adsorption for all compounds apart from metsulfuron-methyl. The contrasting behaviour shown for these four acidic pesticides indicates that chemical degradation in soil is more difficult to predict than adsorption. Most of the variables measured were interrelated, and different behaviours were observed even for compounds from the same chemical class and with similar structures.     

Identifying the influence of urbanization on soil organic matter content and p H from soil magnetic characteristics

Soil magnetic characteristics are correlated with soil p H and organic matter content. Analyzing soil magnetic characteristics, organic matter content and p H can indirectly evaluate soil pollution caused by human activities. This study analyzed the soil magnetic characteristics, organic matter content and p H in surface soil samples from different land use types in Shihezi city, a newly and rapidly developing oasis city in Xinjiang of China. The aims of this study were to explore the possible relationships among the soil magnetic parameters and thereby improve the understanding of influence of urbanization on soil properties. Eighty surface soil samples at the depth of 0–10 cm were collected from 29 July to 4 August 2013. The results showed that the magnetic minerals in surface soil were dominated by ferromagnetic minerals. Spatially, the magnetic susceptibility(χLF), anhysteretic remanent magnetization susceptibility(χARM), saturation isothermal remanent magnetization(SIRM) and "soft" isothermal remanent magnetization(SOFT) were found to be most dominant in the new northern urban area B(N-B), followed by built-up areas(U), suburban agricultural land(F), and then the new northern urban area A(N-A). The values of χLF, χARM, SIRM and SOFT were higher in the areas with high intensities of human activities and around the main roads. Meanwhile, the property "hard" isothermal remanent magnetization(HIRM) followed the order of UN-BFN-A. Built-up areas had an average p H value of 7.93, which was much higher than that in the new northern urban areas as well as in suburban agricultural land, due to the increased urban pollutant emissions. The average value of soil organic matter content in the whole study area was 34.69 g/kg, and the values in the new northern urban areas were much higher than those in the suburban agricultural land and built-up areas. For suburban agricultural land, soil organic matter content was significantly negatively correlated with χLF, and had no correlation with other magnetic parameters, since the soil was frequently ploughed. In the new northern urban areas(N-A and N-B), there were significant positive correlations of soil organic matter contents with χARM, SIRM, SOFT and HIRM, because natural grasslands were not frequently turned over. For the built-up areas, soil organic matter contents were significantly positively correlated with χLF, χARM, SIRM and SOFT, but not significantly correlated with frequency-dependent susceptibility(χFD, expressed as a percentage) and HIRM, because the soil was not frequently turned over or influenced by human activities. The results showed that soil magnetic characteristics are related to the soil turnover time.     

Adsorption,desorption and dissipation of metolachlor in surface and subsurface soils

BACKGROUND: Variations in soil properties with depth influence retention and degradation of pesticides. Understanding how soil properties within a profile affect pesticide retention and degradation will result in more accurate prediction by simulation models of pesticide fate and potential groundwater contamination. Metolachlor is more persistent than other acetanilide herbicides in the soil environment and has the potential to leach into groundwater. Reasonably, information is needed about the dissipation and eventual fate of metolachlor in subsoils. The objectives were to evaluate the adsorption and desorption characteristics and to determine the dissipation rates of metolachlor in both surface and subsurface soil samples. RESULTS: Adsorption of metolachlor was greater in the high‐organic‐matter surface soil than in subsoils. Lower adsorption distribution coefficient (K_ads) values with increasing depth indicated less adsorption at lower depths and greater leaching potential of metolachlor after passage through the surface horizon. Desorption of metolachlor showed hysteresis, indicated by the higher adsorption slope (1/n_ads) compared with the desorption slope (1/n_des). Soils that adsorbed more metolachlor also desorbed less metolachlor. Metolachlor dissipation rates generally decreased with increasing soil depth. The first‐order dissipation rate was highest at the 0–50 cm depth (0.140 week^?1) and lowest at the 350–425 cm depth (0.005 week^?1). Degradation of the herbicide was significantly correlated with microbial activity in soils. CONCLUSION: Metolachlor that has escaped degradation or binding to organic matter at the soil surface might leach into the subsurface soil where it will dissipate slowly and be subject to transport to groundwater. Copyright © 2009 Society of Chemical Industry     

Degradation of the sulfonylurea herbicides chlorsulfuron and triasulfuron in a high-organic-matter volcanic soil

The degradation rates of two sulfonylurea herbicides, chlorsulfuron and triasulfuron, were determined at two application rates, 15 and 30 g a.i. ha^–1, in a sandy loam soil of volcanic origin under controlled environment and field conditions. Residues were measured using a modified gas chromatographic (gc) determination method. Both herbicides degraded rapidly in the acidic soil (pH 5.7) with high organic matter levels (7.3% o.m.), generally according to first-order rate kinetics. The respective half-lives ranged from 22 to 38 d for chlorsulfuron and from 31 to 44 d for triasulfuron under five controlled temperature/soil moisture regimens, ranging from 10 to 30 °C and between 40% and 80% maximum water-holding capacity. Half-lives in the field were considerably shorter (13 d for chlorsulfuron and 12–13 d for triasulfuron). The degradation rates of the herbicides were influenced more by soil temperature than by soil moisture content. Bioassays using white mustard ( Sinapis alba L.) and forage sorghum [ Sorghum bicolor (L.) Moench] were also used to determine the persistence of phytotoxic residues of both herbicides in the field, and the results showed that the effects of chlorsulfuron disappeared within 8 weeks. Triasulfuron residues disappeared within 9 and 14 weeks for the 15 and 30 g a.i. ha^–1 rates respectively.     

河北中部药用植物AM真菌生态学研究

2005年8月和10月,对河北省安国市境内种植的9种药用植物AM真菌侵染状况及与土壤因子的相关性进行了调查分析.结果表明,9种药用植物都能与AM真菌形成良好的共生关系,不同药用植物形成菌根的能力不同.形成的菌根包括重楼型(Paris-type)和疆南星型(Arum-type)2种类型.土壤碱解N与丹参和麻山药的孢子密度、北沙参菌丝定殖率和总定殖率呈显著正相关,与紫苑丛枝定殖率呈显著负相关.土壤速效P与丹参丛技定殖率、麻山药泡囊定殖率呈显著正相关,与桔梗孢子密度、白术泡囊定殖率呈显著负相关.土壤有机质与北柴胡孢子密度呈显著负相关.土壤pH与北沙参菌丝定殖率和总定殖率、北柴胡孢子密度呈显著负相关,与北沙参孢子密度呈显著正相关.     

Degradation of primisulfuron-methyl and metsulfuron-methyl in soil

A newly developed chemical assay was used to determine the degradation in soil of two sulfonylurea herbicides, primisulfuron-methyl and metsulfuron-methyl, under both controlled and field conditions. The results from the chemical assay were compared with those from traditional bio-assays for determination of persistence in the field. Phytotoxic effects of these herbicides were not observed after 6 weeks following application to an acidic (pH 5.7) soil with high organic matter content (7.3% o.c). Half-lives of 13 to 29 days were measured for primisulfuron-methyl at different soil-water contents and temperatures while those for metsulfuron-methyl ranged from 8 to 36 days. The rate of degradation of metsulfuron-methyl was more sensitive to temperature than that of primisulfuron-methyl. Persistence in the field was shorter than expected considering the results from the controlled environment studies. However, determination of the persistence by both chemical assay and bioassay methods produced very similar results.     

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。     

Variation in soil organic matter accumulation and metabolic activity along an elevation gradient in the Santa Rosa Mountains of Southern California,USA

Variations in soil organic matter accumulation across an elevation can be used to explain the control of substrate supply and variability on soil metabolic activity. We investigated geographic changes in soil organic matter and metabolic rates along an elevation gradient(289–2,489 m) in the Santa Rosa Mountains, California, USA from subalpine and montane pine forests through chaparral to desert. From base(289 m) to summit(2,489 m), 24 sites were established for collecting soil samples under canopies and inter-canopy spaces, at 0–5 and 5–15 cm soil depths increments. Soil organic matter(SOM) content was determined using weight loss on ignition at 550°C and soil CO2 efflux(R) was measured at day 5(R5) and day 20(R20) of incubation. Changes in SOM content along the elevation gradient showed a significant relationship(P0.05) but R5 and R20 were not related to either elevation or SOM content. However, the ratio of R and SOM(R5/SOM) showed a strong relationship across the mountains at both soil depths. R5/SOM, as an indicator of carbon use efficiency, may be applicable to other semi-arid transects at larger scale modeling of soil metabolic processes.     

祁连山排露沟流域青海云杉林土壤养分和pH变化特征

祁连山北坡中山带森林灰褐土是生长青海云杉的集中地带。选择排露沟流域海拔2 900～3 300 m的青海云杉林为研究对象,每隔100 m海拔梯度设置3个调查样地,研究青海结果表明：① 在海拔梯度上,0~40 cm土层土壤有机质、全氮及全磷平均含量高海拔处高于低海拔,而且高海拔与低海拔差异显著（P<0.05）;土壤全钾和速效钾含量则是高海拔低于低海拔,差异亦显著（P<0.05）;速效磷含量随海拔升高没有明显的变化规律,而且海拔间差异不显著（P<0.05）;土壤pH随海拔的升高不断减小,但是海拔间的差异不显著（P＞0.05）。 ② 在不同土层深度,0~10 cm土层土壤有机质、全氮、全磷、速效磷和速效钾平均含量均大于10~20 cm和20~40 cm土层,而且0~10 cm土层含量显著大于20~40 cm土层（P<0.05）;土壤pH和全钾含量则随土层深度增加,pH在0~10 cm土层与20~40 cm差异显著（P<0.05）,但全钾含量在不同土层差异均不显著（P＞0.05）。 ③ 在碳、氮、磷、钾营养元素循环中,土壤pH和土壤有机质是影响青海云杉群落养分供应的首要限制因子。     

Influence of soil moisture on short-term adsorption of diuron and isoproturon by soil

The adsorption of diuron and isoproturon by a clay loam soil at 35% (3-16 kPa) and 62% (1 kPa) soil moisture content was studied by means of glass microfibre filters capable of sampling soil solution for herbicide analysis. Adsorption was rapid, with 40–80% of the final (24 h) sorption being achieved within 2 min. These equilibria were achieved more rapidly for diuron, which was also the more highly adsorbed. Adsorption of both herbicides was favoured by low soil moisture initially, but was enhanced by higher soil moistures at sorption times greater than 30 min. However, increasing the soil moisture from 31% (10 kPa) to 62% (1 kPa) had little effect on the final soil sorption capacity. Regarding the water status in the soil, it is thought that adsorption took place in small pores (<3 μm). Herbicides diffused rapidly into small pores and adsorption by wet soil was delayed for a short period of time (about 30 min).     

Spatial variability in the mineralisation of the phenylurea herbicide linuron within a Danish agricultural field: multivariate correlation to simple soil parameters

The spatial variability in the mineralisation rate of linuron [N-(3,4-dichlorophenyl)-N'-methoxy-N'-methylurea] was studied within a previously treated Danish agricultural field by sampling soils from eleven different plots randomly distributed across an area of 20 x 20 m. The soils were characterised with respect to different abiotic and biotic properties including moisture content, organic matter content, pH, nutrient content, bacterial biomass, potential for mineralisation of MCPA [(4-chloro-2-methylphenoxy)acetic acid] and linuron. Five soils had a potential for mineralisation of linuron, with 5-15% of the added [ring-U-14C]linuron metabolised to 14CO2 within 60 days at 10 degrees C, while no extensive mineralisation of linuron was observed in the six remaining soils within this period. A TLC analysis of the methanol-extractable residues showed no development of 14C-labelled metabolites from linuron in any of the samples. Multivariate analysis was conducted to elucidate relationships between the intrinsic properties of single soil samples and initial rate of linuron mineralisation. The analysis indicated that important soil parameters in determining the spatial heterogeneity included the C(total)/N(total) ratio, pH and the water-extractable potassium contents, with the first of these highly negatively correlated and the last two highly positively correlated to the initial linuron mineralisation rate. This study shows that enhanced biodegradation of linuron may develop with successive field treatments, but that considerable in-field spatial heterogeneity in the degradation rate still exists. Combined with a parallel enrichment study focused on the underlying microbial processes, the present results suggest that intrinsic soil properties affect the linuron-metabolising bacterial population and thereby determine the spatial variability in the linuron mineralisation activity.     

Adsorption-desorption behaviour of flufenacet in five different soils of India

Adsorption-desorption of the herbicide flufenacet (FOE 5043) has been studied in five soils from different locations in India (Delhi, Ranchi, Nagpur, Kerala and Assam) varying in their physicochemical properties. The organic matter (OM) content varied from 0.072 to 0.864%, clay content from 2.5 to 43.7% and pH from 4.45 to 8.35. The adsorption studies were carried out using a batch equilibration technique. Ten grams of soil were equilibrated with 20 ml of aqueous 0.01 M CaCl2 solution containing different concentrations (0-30 mg litre-1) of flufenacet. After equilibration, an aliquot of supernatant was taken out for analysis. During desorption, the amount withdrawn for analysis was replenished with fresh 0.01 M CaCl2 solution and further equilibrated. Desorption studies were carried out with the 30 mg litre-1 concentration of flufenacet only. The adsorption studies revealed that there was moderate to high adsorption of flufenacet considering the comparatively low organic carbon content in the five test soils. Average Kd values ranged from 0.77 to 4.52 and Freundlich KF values from 0.76 to 4.39. The highest adsorption was observed in Kerala soil (OM 0.786%; clay 25%; pH 4.45) followed by Ranchi, Nagpur and Delhi soils, and the lowest in Assam soil (OM 0.553%; clay 2.5%; pH 6.87). The trend in adsorption could be attributed to the chemical nature of flufenacet and the physicochemical properties of the soil such as pH, OM and clay contents. OM and clay contents were positively correlated whereas pH was negatively correlated. Soils having low pH, high OM and high clay contents showed higher adsorption. Desorption studies revealed that there was a hysteresis effect in all the soils. Hysteresis coefficient values (ratio of n(ad) and n(des)) varied from 0.09 to 0.45. The study implies that, because of its moderate to high adsorption, flufenacet is likely to persist in soil for some time. However, the possibility of its movement by leaching or surface run off is less.     

渭河上游地区温室菜地土壤肥力演变特征研究

在陇东南渭河上游地区的天水市武山县,通过田间采样的方法,以不同种植年限的温室和露地的耕层土壤(0~20 cm)为研究对象,研究了长期连作温室蔬菜对土壤p H、全盐、有机质及氮磷钾养分的影响。结果表明:不同种植年限温室菜地的土壤p H都明显低于其露地大田,而且随种植年限的延长,p H逐渐降低,与种植年限显著负相关,年均降低0.05个单位。而土壤全盐含量与种植年限呈显著正相关,年均增加0.091个百分点。连续14年种植温室蔬菜土壤全盐含量达到0.34%,是露地土壤的6.35倍。土壤有机质、全氮、碱解氮、全磷、全钾、速效磷和速效钾含量也随种植年限逐渐增加,与种植年限显著正相关,连续14年种植温室蔬菜后,土壤的速效氮、速效磷和速效钾含量分别达到230.17、342.17 mg·kg-1和263.00 mg·kg-1,显著的高于大田。     

环境条件对除草剂莎稗磷降解的影响

环境条件影响莎稗磷在土壤中的降解速度 :随着土壤温度的升高和含水量的增加 ,莎稗磷降解速度加快 ,在温度为 2 0、30和 4 0℃下 ,经过 10 d,莎稗磷的降解率分别为10 .4 %、2 6 .7%和 37.6 % ;在相对含水量为 30 %～ 110 %的土壤中 ,15d后莎稗磷降解 4 5.0 %～ 6 8.4 %。土壤中有机质能促进莎稗磷的降解 ,在有机质含量为 3.35%和 0 .55%的两种土壤中 ,莎稗磷的半衰期分别为 11d和 15d。莎稗磷在碱性土壤中比在酸性土壤中降解快 ,在偏酸性 (p H值为 6 .0 1)土壤中的半衰期为 2 2 d,在偏碱性 (p H值为 7.98)土壤中半衰期为 15d.