湿地生态系统对污水中重金属的修复作用

湿地污水处理技术的研究是国内外众多学者关注的热点之一。综合国内外在污水湿地处理技术方面的研究成果,对湿地生态系统及其各组成要素对重金属污染的修复作用及其作用机理进行了讨论,针对目前利用湿地生态系统进行重金属污染废水修复过程中应注意的几个问题进行了探讨,并对今后研究发展方向进行了评述。     

空心多茎株型短季棉施氮效应研究初报

试验研究高光效空心多茎株型短季棉施N效应结果表明 ,强源是空心多茎株型短季棉施N增产的主要原因 ,扩库对产量的作用有限。低N量即显著提高空心多茎株型短季棉皮棉产量 ,继续增施N肥则空心多茎株型短季棉仅对N素表现出较强适应性 ,而未能充分发挥其产量潜力 ,表明产量潜力的发挥需要配套栽培技术的支撑     

不同N水平的富营养化水体中经济植物净化能力比较研究

为建立净化富营养化水体的生态工程，本试验选择水芹、水蕹菜、韭菜、葱、黄花菜、芹菜等6种经济植物，研究了各种植物的净化能力及其生物学特性。结果表明：每种经济植物对水体总氮、总磷均有一定的去除作用，特别是水芹和水蕹菜，其在试验的20d内，对总氮、总磷的去除百分率分别为89．5％，98．2％；同时还对6种经济植物引起水体总氮浓度下降与时间关系作回归分析，结果表明随着处理时间的延长，水体中总氮浓度呈负指数形式衰减。本文还对在植物处理过程中，水中Chla、BODs和COD的变化进行了观测。研究表明，在高N水平的富营养化水中除水芹和水蕹菜外，Chla、BOD。和COD随处理时间的延长而下降，但在韭菜和葱处理过程中，水中腥味加重。各项指标综合分析表明，在不同N水平的富营养化水体中，水蕹菜处理效果最好，水芹次之，黄花菜和芹菜居中，韭菜最差。     

红壤不同含水量对尿素氨挥发的影响

根据第四纪红壤水分特征设计160、200、240、280、320、360g/kg6个土壤含水量处理,通过温室模拟,研究了红壤不同含水量对尿素氨挥发的影响。结果表明,等量尿素施入红壤后,氨挥发通量与土壤含水量之间无显著相关性,而高含水量(280、320、360g/kg)处理氨挥发通量峰值较低含水量(160、200g/kg)处理提前10天。氨挥发过程可分为快速-慢速2个阶段,氨累积挥发量(y)与对应时间(t)符合Elovish动力学方程(y=a blnt)。第1～10天,氨挥发累积量随红壤含水量的增加而递增;第11天后,以含水量为240g/kg处理的氨挥发累积N量最低。试验期间,氨挥发累积总N量,以含水量240g/kg时最低(0.90gN),含水量320g/kg时最高(1.16gN),分别占尿素施入N量的9.0%和11.6%。     

生物法处理养殖污水中氨氮的研究进展

综述近几年生物方法处理养殖污水中氨氮的研究进展及实际应用,并对大规模处理养殖污水方面提出了一些思考和展望,期望在今后的研究工作中能够探索出高效率、低成本、无二次污染的生物方法处理养殖污水中的氨氮.     

畜禽养殖废水脱氮除磷研究进展

笔者介绍了SBR、上流式活性污泥床、fiehl prototype工艺等几种目前国内外较典型的集约化养殖场废水处理方法,比较了它们在脱氮除磷方面的优缺点及其应用和研究情况,简述了畜禽养殖废水脱氮除磷现状.最后对畜禽养殖废水脱氮除磷存在的问题进行了探讨,同时对其发展趋势进行了展望.     

Controls on nitrification in a water-limited ecosystem: experimental inhibition of ammonia-oxidising bacteria in the Patagonian steppe

We studied controls on nitrification in an undisturbed water-limited ecosystem by inhibiting autotrophic nitrifying bacteria in soils with varying levels of vegetative cover. The activity of nitrifying bacteria was disrupted using nitrapyrin, 2-chloro-6-(trichloromethyl)-pyridine, under field conditions in three microenvironments (underneath shrubs, next to grasses and in bare soil). Ammonia-oxidising bacteria were detected by PCR analysis of DNA in soils. The inhibition of nitrification changed the concentrations of NO₃⁻ and NH₄⁺ in the soil, while the microenvironment was most important in determining the response of bacteria to the inhibitor. Nitrapyrin application resulted in a significant (p<0.05) reduction in soil NO₃⁻ concentration (39%) and a significant increase (p<0.001) in soil NH₄⁺ concentration (41%). Untreated bare-soil microenvironments had the lowest concentrations of NH₄⁺ (1.57 μg/g of dry soil) and NO₃⁻ (0.49 μg/g of dry soil) when compared to the other microenvironments, and showed the highest impacts of nitrification inhibition. For example, NH₄⁺ concentrations increased 288% and NO₃⁻ concentrations decreased 60% in inhibited bare-soil microenvironments. In contrast, untreated microenvironments underneath shrubs had the highest levels of NH₄⁺ (10.01 μg/g of dry soil) and NO₃⁻ (0.69 μg/g of dry soil), but showed no significant effects of inhibition of nitrification on soil nitrogen concentrations.     

Nitrous oxide, methane and ammonia emissions following slurry spreading on grassland

In Sweden, 90% of ammonia (NH₃) emissions to the atmosphere originate from agriculture, predominantly from animal manure handling. It is well known that incorporation of manure into soil can reduce NH₃ emissions after spreading. However, there is a risk of increased nitrous oxide (N₂O) and methane (CH₄) emissions caused by bacterial activity and limited oxygen availability under these conditions. A full‐scale injector was developed and evaluated in a field experiment on grassland. Cattle slurry was either injected in closed slots 5 cm below ground or band spread on the soil surface above the crop canopy at a rate of 25 t ha^?1. In a control treatment, no slurry was applied. During a 5‐day period after application, NH₃ emissions were measured using an equilibrium concentration method. Gas samples for estimating CH₄ and N₂O emissions were also collected during 7 weeks following slurry application. Injection in closed slots resulted in no detectable NH₃ emissions. After band spreading, however, NH₃ emissions corresponded to nearly 40% of the total ammoniacal nitrogen in the applied slurry. The injection of slurry gave rise to a broad peak of N₂O emissions during the first 3 weeks after application. In total, for the measuring period, N₂O emissions corresponded to 0.75 kg N ha^?1. Band spreading resulted in only a very small N₂O release of about 0.2 kg N ha^?1 during the same period. Except for the first sampling occasion, the soil was predominantly a sink for CH₄ in all the treatments. The use of the injector without slurry application reduced grass yield during unfavourable growing conditions. In conclusion, shallow injection in closed slots seems to be a promising technique to reduce negative environmental impacts from NH₃ emissions with a limited release of N₂O and CH₄.     

Ammonia volatilization from poultry manure-amended soil

Summary Poultry manure (PM) is commonly applied to cropland as a fertilizer, usually at rates determined by the nitrogen content of the manure. Limited information is available, however, on the volatilization of ammonia from poultry manure-amended soils, despite the effect these losses may have on the fertilizer value of the manure. This study was initiated to determine the influence of incorporation and residue cover on NH₃ losses from PM-amended soils. In the first experiment, a dynamic flow technique was used to measure NH₃ losses from 18 manures applied to a bare soil surface at a rate of 12 Mg ha^-1. In the second experiment, 3 of the 18 manures were incorporated either immediately, 24 h or 72 h after application. The third experiment compared the same three manures applied to a bare soil surface or to corn or soybean residues. Surface application of the manures resulted in the loss of from 4 to 31% of the total N applied in the manures. Incorporation of the PM with soil significantly reduced NH₃ loss with the greatest decrease following immediate incorporation. Crop residues either had no effect or slightly reduced NH₃ volatilization losses relative to PM application to a bare soil surface. Ammonia volatilization was not well correlated with individual manure properties, but a multiple regression approach using manure pH and total N content offered some promise as a means to segregate manures of the basis of volatilization potential.