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51.
土壤生物量-碳和-氮与土壤有机碳、氮及施肥的关系 总被引:12,自引:0,他引:12
应用氯仿熏蒸培养法测定不同肥力水平的土壤生物量-C 和-N。结果表明:士壤生物量-C 与土壤有机碳的相关性达到极显著水准;用6mol/L HCl 水解的总氮量与土壤全氮也有很好的相关性,但与生物量-N 则不然;生物量-N 与酸解的氨基酸态氮及未知态氮都有显著相关性。施肥显著提高土壤生物量-C 和-N,有机无机肥料配合施用的大于单施化肥的。 相似文献
52.
农七师车排子垦区柳沟灌区,原有柳沟一、二、三场,面积59万余亩。由于盐碱危害,生产状况和经济状况日益恶化,难以自立。在60年代初,与原25团合并,成为现今的125团的三个营,近年来进行大规模的盐碱土改良工作,取得了显著的效果。基本情况改良效果的观测主要在二营(原柳沟三场)进行,二营面积10.67万亩,可耕地8.85万亩,位于灌区南部、天山北麓,奎屯河与四棵树之间。区内由南向北倾斜,地势低平,坡降1-3‰,土壤多为粉粒中壤和重壤,1-2米以下,广泛分布着红棕色粘土层,因而地下水迳流呈封闭状态,极其不畅,主要靠地面蒸发和植物蒸腾维持平衡。地下水埋深1-1.5米;低洼区接近地面。矿化度20-30克/升,最高达88.45克/升。高矿化与高水位成为土壤盐渍化迅速发展的根本原因。 相似文献
53.
54.
Abstract. Current tillage erosion models account for the influence of tillage direction in the magnitude of the soil (tillage) transport coefficient. It is argued here that this is counter-intuitive and causes significant problems in modelling tillage erosion in areas of complex terrain. This article examines whether a re-modelling of tillage erosion is possible that separates tillage direction (an interaction with the landform) from the soil transport coefficient (a measure of tillage intensity representing the combination of implement erosivity and soil erodibility). Experimental data for mouldboard ploughing upslope, downslope and cross-slope at Coombe Barton Farm, Devon are examined. Integration of data for all directions into a single relationship, which relates translocation in the direction of tillage to slope in the direction of tillage and translocation perpendicular to tillage to slope perpendicular to tillage, is not possible using previously published methods of analysis. However, when total translocation distance is regressed against the tangent of the slope at 45° to the tillage direction (bisecting the tillage direction and the direction of overturning) it is found that a single relationship can be used to describe tillage in all three directions. Therefore, this relationship is used to determine a single value of the soil transport coefficient ( k fTa ) for constant soil and implement conditions but different tillage directions. This redefinition of tillage is important both for true estimation of tillage erosion severity, the adirectional coefficient being 40% larger than the directional coefficient, and for modelling of tillage erosion in complex terrain. These improvements are vital when tillage erosion simulation is used to direct soil conservation strategies. 相似文献
55.
J.A. Díez P. Hernaiz M.J. Muñoz A. de la Torre A. Vallejo 《Soil Use and Management》2004,20(4):444-450
Abstract. The repeated application of pig slurry to agricultural soils may result in an accumulation of salts and a risk of aquifer pollution due to nitrate leaching and salinization. Under Mediterranean conditions, a field experiment on a sandy loam soil (Typic Xerofluvent) was performed with maize (Zea mays) in 1998, 1999 and 2001 to study the effects of applying optimal (P1) and excessive rates (P3) of pig slurry on soil salinization, nitrate leaching and groundwater pollution. The rate of pig slurry was established considering the optimal N rate for maize in this soil (170, 162 and 176 kg N ha?1 for 1998, 1999 and 2001, respectively). Pig slurry treatments were compared to an optimal N rate supplied as urea (U) and a control treatment without N fertilizer (P0). The composition of the slurries showed great variability between years. Mean NO3? leaching losses from 1998 to 2001 were 329, 215, 173 and 78 kg N ha?1 for P3, P1, U and P0 treatments, respectively. The amount of total dissolved salts (TDS) added to the soil in slurry application between 1998 and 2001 was 2019 kg TDS ha?1 for the P1 treatment and 6058 kg TDS ha?1 for the P3 treatment. As a consequence, the electrical conductivity (EC) of the slurry‐treated soils was greater than that of the control soil. The EC correlated significantly with the sodium concentration of the soil solution. Over the entire experimental period, 2653, 2202 and 2110 kg Na ha?1 entered the aquifer from the P3, P1 and P0 treatments, respectively. The P3 treatment did not significantly increase grain production in 1999 and 2001 compared with that achieved with the optimal N rate treatment (P1). This behaviour shows the importance of establishing application guidelines for pig slurry that will reduce the risk of soil and groundwater pollution. 相似文献
56.
绵阳官司河流域水土流失综合报告 总被引:1,自引:0,他引:1
报告简述域地质地貌水文气象土壤,植被等地理因素的概况及其与土壤侵蚀的关系,指出本流域由于长防林的建立,发挥了保持水土作用,水土流失不严重,属轻度-中度侵蚀,最大侵蚀模数小于7400[t/(km^2.年],全区平均侵蚀模数1754.42[t/km^2.年];确定了水土流失类型,即片蚀,沟蚀,母质侵蚀三大类;分析了水土流失的原因:以泥岩和灰白砂岩,第四纪冰碛物堆积土侵蚀最高测定不同精植被类型的土壤质地 相似文献
57.
鸡舍环境耐药细菌气溶胶及其向环境传播的研究 总被引:23,自引:0,他引:23
通过对舍内粪便、空气和舍外环境(10、50、100m)中的空气分离到的细菌鉴定,包括细菌DNA分子生物学检测及药物敏感实验以及细菌含量统计学分析,证明三者之间存在着内在联系;舍内环境微生物气溶胶包括耐药细菌通过舍内外气体交换排往鸡舍周围环境,舍周边环境在一定范围内受到生物污染。研究显示,在粪便、舍内空气、舍外环境10、50、100m空气中分离的金黄色葡萄球菌和链球菌80%以上对氯霉素(CMP)和对苯唑青霉素(OXA)耐药;粪便和舍内外环境空气中的80%以上的大肠杆菌和沙门氏菌对氨苄青霉素(AMP)、氯霉素(CMP)、头孢唑啉(CFZ)均为抑制。证明该鸡舍曾经使用过这些药物治疗或作为添加剂在饲料中添加,鸡群产生了耐药细菌菌株,并向环境传播。测量数据统计结果指出,十里河鸡场鸡舍内环境空气中的大肠杆菌、沙门氏菌、金黄色葡萄球菌和链球菌与舍外环境中相应菌群含量比较差异显著或极显著(P<0.05或P<0.01),但舍外10、50、100m之间的相应菌群比较差异不显著(P>0.05),这说明鸡舍内环境细菌气溶胶含量产生多,含量高,菌源强度大;另一方面,反应了鸡舍内环境微生物气溶胶包括耐药细菌能向舍外环境扩散,位舍外环境在一定的范围内受到动物源性生物污染,影响范围大于100m。通过对鸡舍环境微生物气溶胶来源的探讨发现,粪便中的大肠杆菌、沙门氏菌、金黄色葡萄球菌和链球菌与舍内空气相应菌群数量关系比较,呈现正相关(r=0.99)。这从一个侧面揭示了粪便可能是微生物气溶胶的主要来源。 相似文献
58.
对梅州市五华县几个石灰岩矿区周边土壤中铅含量进行了测定,结果表明,污染土壤的铅含量远远超出了国家土壤环境质量三级标准(对土壤生态环境产生影响的最低浓度值),对生态产生影响。根据内梅罗污染指数评定得出,矿区土壤铅污染达到重污染的程度。提出了减轻铅污染对生态环境危害的控制污染源措施和改良对策。 相似文献
59.
根据在北京郊区的试验,认为土壤水冻融过程可分为三阶段,其中第二阶段有聚墒现象,平均聚墒8.6mm,所聚的墒在融化过程中又逐渐消失。气温回升至-2℃左右是冻层下部由冻到融的转折温度。冬灌水保存到来年春季的数量有限,本试验中1m 土层内平均不足20mm。 相似文献
60.
Abstract. In Australia, stubble burning and tillage are two of the major processes responsible for the decline of soil organic carbon concentration in cropped soils, and the resulting soil degradation. However, the relative importance of these two practices in influencing the soil organic carbon concentration and the long-term impact on soil quality and productivity are not clear. The effects of stubble burning as practised by farmers in southeastern Australia were evaluated in two field trials, one of 19 years duration, the other of 5 years. Conventional tillage (three tillage passes) led to greater loss of soil organic carbon than stubble burning. Loss of total soil organic carbon attributed to stubble burning in the 0–10 cm layer was estimated to be 1.75 t C ha−1 over the period of the 19-year trial, equivalent to 29% of that lost due to tillage. In the 5-year trial, no change in soil organic carbon due to stubble burning was detectable. Changes in soil quality associated with stubble burning detected in the longer trial included a reduction in macro-aggregate stability, and increases in pH and exchangeable K+ . Only the latter two were detected in the shorter trial. A higher mean wheat yield (average 0.15 t ha−1 ) following stubble burning was observed in the 19-year trial but not in the 5-year trial. Research to monitor the longer term effects of stubble burning is needed, and to identify conditions where loss of soil organic carbon is minimized. 相似文献