运用Jayaweera-Mikkelsen模型对太湖地区水稻田稻季氨挥发的模拟

运用密闭气室通气法测定了太湖地区典型水稻田lysimeter实验中肥料施用后的稻季氨挥发动态变化和总损失量,并使用Jayaweera-Mikkelsen氨挥发模型验证了测定结果.田间测定结果表明,施用普通尿素和控释尿素后的氨挥发显著不同,在水稻生育期普通尿素的氨挥发损失达施入N量的29%～35%,不同施N水平间差异显著;而不同用量的控释尿素的氨挥发损失则相对一致,仅为施入N量的5%.模型高估了生育期的氨挥发总量,特别是在普通尿素高挥发时期造成了较大偏差.对尿素处理,模型预测值与实测值的比率为2.95～4.19;对控释尿素处理,预测值对实测值有正负偏差,比率为1.19～1.40.运用预测值与实测值的级数商评价了模型的实用性.通过灵敏度分析,对模型中的参数NH 4-N的浓度进行了修正,引入了限制条件.修正后的模型能够很好地满足对高挥发量的预测,模拟结果比率为1.12～1.28.实测田面水中的NH 4-N浓度不能代表模型中参与计算的实际浓度,可能原因是藻类活动对NH 4-N浓度和氨挥发过程产生的影响.     

对HANNA C200离子分析仪测定氨氮精密度和准确度

HANNA C200离子分析仪测定水中的氨氮操作简便、快速、试剂用量小;经统计学处理,标准样品在中间浓度精密度、准确度较高;测定值更准确。     

Gaseous emissions from weaned pigs raised on different floor systems

Gaseous emissions from agriculture contribute to a number of environmental effects. Carbon dioxide (CO₂), methane (CH₄) and nitrous oxide (N₂O) are greenhouse gases taking part to the global problem of climate change. Ammonia (NH₃) emissions are responsible of soil acidification and eutrophication and contribute also to indirect emissions of N₂O. This work evaluated the influence of the type of floor on the emissions of these gases in the raising of weaned pigs. Two trials were carried out. In the first trial, the animals were kept either on fully slatted floor or on straw-based deep litter and, in the second one, either on fully slatted floor or on sawdust-based deep litter. For each trial and on each type of floor, 2 successive batches of weaned pigs were raised without changing the litter or emptying the slurry pit between the 2 batches. The rooms were automatically ventilated to maintain a constant ambient temperature.The performance of the animals was not significantly different according to the floor type. In trial 1, the nitrogen contents of the straw deep litter (including the substrate) and slurry were respectively 276 and 389 g pig⁻¹. In trial 2, the sawdust deep litter and slurry nitrogen contents were respectively 122 and 318 g pig⁻¹.Raising pigs on straw deep litter produced proportionately around 100% more NH₃ than raising pigs on slatted floor (0.61 g NH₃-N d⁻¹ pig⁻¹ vs. 0.31 g NH₃-N d⁻¹ pig⁻¹; P < 0.05). Differences in CO₂, H₂O and CH₄ emissions were not significant between systems. Raising pigs on sawdust deep litter produced also proportionately more NH₃ (+52%; 0.55 g NH₃-N d⁻¹ pig⁻¹ vs. 0.36 g NH₃-N d⁻¹ pig⁻¹; P < 0.01) but also more CO₂ (+25%; 427 g d⁻¹ pig⁻¹ vs. 341 g d⁻¹ pig⁻¹; P < 0.001) and H₂O (+65%; 981 g d⁻¹ pig⁻¹ vs. 593 g d⁻¹ pig⁻¹; P < 0.001) and less CH₄ (−40%; 0.52 g d⁻¹ pig⁻¹ vs. 0.86 g d⁻¹ pig⁻¹; P < 0.001) than raising pigs on slatted floor. Practically no N₂O emission was observed from rooms with slatted floor while the N₂O emissions were 0.03 and 0.32 g N₂O-N d⁻¹ pig⁻¹ for the straw and sawdust deep litter respectively. The warming potential of the greenhouse gases (N₂O + CH₄), were about 22, 34 and 168 g CO₂ equivalents per day and per pig on fully slatted floor, straw or sawdust deep litter respectively.In conclusion, pollutant gas emissions from rearing of weaned pig seem lower with fully slatted plastic floor system than with deep litter systems.     

温度、氨对鲢、鳙、草、鲤鱼的影响

为制定热排放标准的需要,用动态实验和静态实验方法研究了热冲击与氨对鲢、鳙、草、鲤鱼的急性和亚急性效应。结果表明：选择温度与起始致死温度（TL₅₀）值随着驯化温度的升高而增大,鳙鱼对热冲击的反应较敏感。氨对鲢、鳙、鲤鱼的急性毒性（96h）LC₅₀值分别为0.38、0.30、0.66mgNH₃/L（非离解氨）。水温升高5℃,鲤鱼的（96h）LC₅₀。值从0.66mgNH₃/L下降到0.44mgNH₃/L,热冲击明显提高了氨对鲤鱼的毒性。氨对鲤鱼的亚急性毒性结果表明,鳃、肝组织出现了病理改变。以上室内实验结果可作为评价监测热污染水质的科学依据。     

Influence of H2S and NH3 on biogas dry reforming using Ni catalyst: a study on single and synergetic effect

● NH₃ in biogas had a slight inhibitory effect on dry reforming. ● Coexistence of H₂S and NH₃ led to faster decline of biogas conversion. ● Regeneration was effective for catalysts deactivated under synergetic effect. Biogas is a renewable biomass energy source mainly composed of CH₄ and CO₂. Dry reforming is a promising technology for the high-value utilization of biogas. Some impurity gases in biogas can not be completely removed after pretreatment, which may affect the performance of dry reforming. In this study, the influence of typical impurities H₂S and NH₃ on dry reforming was studied using Ni/MgO catalyst. The results showed that low concentration of H₂S in biogas could cause serious deactivation of catalyst. Characterization results including EDS, XPS and TOF-SIMS confirmed the adsorption of sulfur on the catalyst surface, which was the cause of catalyst poisoning. We used air calcination method to regenerate the sulfur-poisoned catalysts and found that the regeneration temperature higher than 500 °C could help catalyst recover the original activity. NH₃ in the concentration range of 50–10000 ppm showed a slight inhibitory effect on biogas dry reforming. The decline rate of biogas conversion efficiency increased with the increase of NH₃ concentration. This was related to the reduction of oxygen activity on catalyst surface caused by NH₃. The synergetic effect of H₂S and NH₃ in biogas was investigated. The results showed that biogas conversion decreased faster under the coexistence of H₂S and NH₃ than under the effect of H₂S alone, so as the surface oxygen activity of catalyst. Air calcination regeneration could also recover the activity of the deactivated catalyst under the synergetic effect of H₂S and NH₃.     

Effluent stream treatment in a nitrogenous fertilizer factory: An exergy analysis for process integration

The industrial processes used for the production of nitrogenous fertilizers are the main generators of reactive nitrogen compounds, chemicals and effluents that ultimately impact the biosphere. Exergy analysis has been performed to a nitrogen fertilizer factory in the State of Bahia, Brazil, where the Anaerobic Ammonium Oxidation (Anammox) and other physical–chemical processes are used to partially or totally handle the feed streams normally sent to a stripping tower.The results showed that the combined use of physical–chemical and biological process can improve the overall exergetic efficiency and avoid the emission of reactive compounds to the atmosphere allowing the recovery of the condensate lost as effluent, so that it can be reincorporated in the production of steam network, increasing energy efficiency and environmental performance of the process.     

甲胺磷在水-气界面挥发动力学研究

研究了挥发时间、温度和气流量对农药甲胺磷在水-气界面挥发行为的影响.挥发量采用气相色谱法检测,利用保留值定性,以外标法定量.研究结果表明,温度升高、气流量增大,使甲胺磷挥发量增大较快,二者是影响甲胺磷挥发的主要因素;挥发时间在4 h之内对甲胺磷挥发量影响较大,4 h之后基本无影响.通过试验还研究了甲胺磷在水-气界面的挥发动力学.根据实验结果,建立了甲胺磷在水-气界面挥发的动力学模型,比较实验值与动力学模型计算值,二者基本吻合,相对误差≤5%,这表明该动力学模型可以用于预测甲胺磷在水-气界面的挥发行为.     

Ammonia as confounding factor in toxicity tests with the sea urchin Paracentrotus lividus (Lmk)

The aim of this study was to investigate the toxicity of total ammonia towards sea urchin bioassays, in order to elucidate the role of ammonia as confounding factor in sediment quality assessment studies. New toxicity data, expressed as EC50, NOEC and LOEC are reported for Paracentrotus lividus based on experiments at differing pH values. Results confirmed that sperm cell toxicity test is not very sensitive to ammonia, while total ammonia embryotoxicity is strictly pH dependent. Accurate observations of embryotoxic effects at increasing total ammonia concentrations evidenced progressive shifts from malformed plutei to gastrula and blastula blockages. Toxicity data obtained for P. lividus are comparable with previous results with other echinoid species.     

生物炭对盐碱土壤氨挥发的影响

为探明生物炭对黄河三角洲盐碱土壤氨(NH_3)挥发的影响,通过室内连续培养的方式,先测定改良的通气法对土壤NH_3挥发的回收率,再对比施加肥料颗粒与肥料水溶液对土壤NH_3挥发的影响,最后探究生物炭的种类、添加量及施肥种类对NH_3挥发速率和总量的影响.结果表明,以硫酸铵为氮源进行的NH_3挥发捕集实验,NH_3回收率平均值高达100. 30%.在相同施氮量下,施加尿素水溶液的处理比施加尿素颗粒的处理NH_3挥发减少了60. 29%,施加硫酸铵水溶液的处理比施加硫酸铵颗粒的处理NH_3挥发减少了61. 40%.相较于不添加生物炭只施用硫酸铵水溶液的空白处理,添加0. 5%生物炭且施加生物炭种类为水稻300℃(RB-300)、水稻600℃(RB-600)、棉花300℃(CB-300)和棉花600℃(CB-600)的处理,NH_3挥发总量分别减少了18. 68%、16. 16%、9. 35%和8. 26%,且施肥后2d内NH_3挥发速率最大,占总挥发量的53. 80%～64. 02%.添加生物炭后,NH_3挥发量随生物炭添加量的增加呈现出先降低后增加的趋势.因此,田间施肥前添加少量生物炭并结合水肥一体化管理技术,可以有效地减少NH_3挥发并提高氮肥利用率.     

Estimating the volatilization of ammonia from synthetic nitrogenous fertilizers used in China

Although it has long been recognized that significant amounts of nitrogen, typically in the form of ammonia (NH(3)) applied as fertilizer, are lost to the atmosphere, accurate estimates are lacking for many locations. In this study, a detailed, bottom-up method for estimating NH(3) emissions from synthetic fertilizers in China was used. The total amount emitted in 2005 in China was estimated to be 3.55 Tg NH(3)-N, with an uncertainty of ± 50%. This estimate was considerably lower than previously published values. Emissions from urea and ammonium bicarbonate accounted for 64.3% and 26.5%, respectively, of the 2005 total. The NH(3) emission inventory incorporated 2448 county-level data points, categorized on a monthly basis, and was developed with more accurate activity levels and emission factors than had been used in previous assessments. There was considerable variability in the emissions within a province. The NH(3) emissions generally peaked in the spring and summer, accounting for 30.1% and 48.8%, respectively, of total emissions in 2005. The peaks correlated with crop planting and fertilization schedules. The NH(3) regional distribution pattern showed strong correspondence with planting techniques and local arable land areas. The regions with the highest atmospheric losses are located in eastern China, especially the North China Plain and the Taihu region.