Performance and environmental effects of forage production on sandy soils. V. Impact of grass understorey, slurry application and mineral N fertilizer on nitrate leaching under maize for silage

A field experiment with maize for silage was conducted to assess the effects of mineral nitrogen (N) fertilizer application rates (0, 50, 100, 150 kg ha^?1), slurry application rates (0, 20, 40 m³ ha^?1) and the use of an understorey with perennial ryegrass on nitrate (NO₃)‐leaching losses. Leachate was collected using ceramic suction cups. Soil mineral N (SMN) was determined to a depth of 90 cm at the end of the growing season. Higher levels of N supply with mineral fertilizer or slurry resulted in higher leaching losses. The grass understorey significantly reduced the losses. The amount of N lost to the groundwater was positively related to SMN at the end of the growing season, with leaching losses representing less than 0·45 of SMN on average. Leaching losses were positively related to the N surplus, which was calculated from the difference between N input (N from fertilizer, slurry and atmospheric deposition) and N output (N removed with maize herbage mass and bound in the understorey biomass in spring). In view of the large variation in weather conditions between the experimental years, it is suggested that for the sandy soils in this experiment N‐leaching losses under maize can be estimated satisfactorily from SMN and the calculated N surplus.     

高温蒸煮除油对餐厨垃圾厌氧消化的影响

[目的]探讨高温蒸煮除油对餐厨垃圾性状及厌氧发酵的影响。[方法]在37℃条件下,通过批式试验分析不同温度蒸煮去油后的餐厨垃圾厌氧消化产气潜力。[结果]蒸煮除油处理提高了餐厨垃圾的sCOD、溶解性糖、溶解性蛋白的水解;未加热处理餐厨垃圾、110℃、120℃及130℃蒸煮除油后餐厨垃圾的单位挥发性固体(VS)产气潜力分别为766、578、624和646 ml/g;随着蒸煮除油温度提高,餐厨垃圾厌氧发酵的总固体(TS)和VS降解率增大。[结论]蒸煮除油可提高餐厨垃圾的水解效果,有利于提高产气潜力。     

猪粪沼液培养微藻系统中试试验

为实现猪粪沼液资源化的大规模应用,该研究以小球藻(Chlorella E2E)为试验藻种,开展了中试规模的“室内纯培养+室外纯培养+室外沼液培养”耦合模式多级放大沼液培养微藻试验：考察了各级培养试验中Chlorella E2E的生长状况、沼液中污染物的去除率及微生物多样性,最大培养体积达12.31 m³,系统运行时长达274 d。结果表明,Chlorella E2E经过多批次纯培养驯化,在二级柱式反应器内能快速达到最适生长状态,培养至第70天平均生物量可达227.72 mg/L;Chlorella E2E在室外纯培养平板反应器内的产量明显高于室内柱式反应器,培养至第14天生物量可达266.48mg/L。在采用沼液培养时,户外跑道池中生物量最高达250.02 mg/L,化学需氧量(chemical oxygen demand,COD)、氨氮(ammonia nitrogen,NH₄⁺-N)、总磷(total phosphorus,TP)去除率分别高达40.05%、95.06%、97.52%;跑道池内微生物多样性较高,更易形...     

畜禽养殖粪水酸化贮存及氮素减损增效研究进展

畜禽粪水酸化贮存能够有效调控粪水贮存中微生物、环境与氮素间的作用关系,实现粪水氮素的减损增效,是一种具有广泛应用前景的关键技术。该研究系统综述了粪水酸化贮存中氮素的迁移转化机理,比较评价了常见酸化剂和不同酸化贮存工艺的应用效果,分析了酸化贮存技术对粪水氮素减损增效的影响。梳理总结得到,粪水酸化存储中氮素的迁移转化机制主要包括有机氮矿化、铵态氮固持、无机氮转化的抑制及硝化3个关键环节,可以依靠改变微生物作用和化学平衡状态实现氮素的减损;与其他酸化工艺相比,长期酸化工艺具有酸化效果更加稳定、应用范围较为广泛等优势;粪水酸化技术能够大幅降低NH3排放,以及部分N2O的排放,进而提高粪肥还田后土壤肥效,但不合理的酸化贮存技术及施用方式也会降低粪水肥效,甚至引起二次污染;未来应重点从氮素迁移转化路径的定量分析、复合酸化剂的开发、粪肥施用效果及风险的评估应对等方面进行深入研究。     

牛粪发酵沼液对立枯丝核菌的抑制作用

为探讨牛粪发酵沼液的抑菌机理,以立枯丝核菌为研究对象,进行了试验研究。采用平皿培养方法:培养基表面分别均匀涂布1mL5种不同处理的沼液,即不作处理沼液、沼液灭菌、离心上清液、无菌膜滤液和菌体溶液,中心接种立枯丝核菌并于生化培养箱中28℃培养96h,每12h测量立枯菌落的生长直径以计算抑制率,同时借助分子生物学手段鉴定了沼液中起抑制作用的微生物。试验结果表明菌体溶液和不作处理沼液对立枯的抑制效果较好,抑制率最高可达74%和53%,离心上清液的抑制效果次之,无菌膜滤液和沼液灭菌处理的抑制作用较弱,一般在20%以下;对沼液中的微生物菌群进行了分离、纯化与筛选,获16株菌种,并与立枯丝核菌进行对峙培养试验,其中nfd-9和nfd-16具有较强抑制作用,其他菌株几乎没有抑制作用。将nfd-9、nfd-16与立枯对峙交界面处进行了扫描电镜观察,结果显示:这2株微生物通过竞争、拮抗和重寄生等作用来抑制立枯丝核菌的生长,从而到达防止病害的目的。经分子生物学技术鉴定,确定了nfd-9和nfd-16分别为米根霉菌(Rhizopus oryzae)和哈茨木霉(Trichoderma harzianum)。研究结果为进一步了解沼液抑制真菌的机理提供一定的理论参考。     

沼液配施化肥对太湖地区水蜜桃品质及土壤氮素累积的影响

将沼液农田回用是有机废弃物资源化与循环利用的重要途径。以7年生蜜露桃树为供试材料,通过连续2年牛粪沼液和水葫芦沼液的果园田间施用试验,研究等氮量条件下不同比例沼液与化肥配施对水蜜桃果实大小、 单重、 产量和果实品质及土壤矿质氮积累状况的影响。结果表明, 1）水葫芦沼液、 牛粪沼液和化肥配施可提高水蜜桃的产量与品质,在水葫芦沼液25% 配施比例、 牛粪沼液50% 配施比例下产量及果实的可溶性固形物、 糖分含量分别为最高,水葫芦及牛粪沼液中的水分含量是影响桃树产量和品质的关键因子,其适宜用量为200 kg/(planta); 2）各施肥处理土壤NH+4含量随土壤深度增加呈递减趋势; 沼液比例过高（75%和100%）会导致土壤硝酸盐在表层和近地下水层的累积,比例低下则硝酸盐累积不明显; 习惯施肥（过量施肥）和低比例沼液（相应的高化肥比例）处理硝酸盐主要累积于犁底层之上; 3） 连续2年在沼液灌溉条件下,25%的水葫芦沼液、 50%的牛粪沼液配施比例处理其近地下水层土壤硝酸盐含量均低于15 mg/kg,处于安全可控范围,但在该地区（高地下水水位）进行长期沼液灌溉尚需进一步观测和评价。     

Application of chromatographic method and high-frequency apparatus for determination of K and Na in soil extract

The amount of K and Na in HCI-extract of soils has been determined by various methods, using the flame photometer, and specific reagents, but none of these methods are fully satisfactory from a view point of cost or accuracy; Poul Porter et al.¹⁾ have pointed out the large errors that have frequently occured in tlamephotometry.     

钻孔灌注桩施工质量控制

本文作者通过本人多年的工程实践、施工中所掌握的关键环节 ,对如何控制钻孔灌注桩施工质量做了比较详细的论述     

Effects of method, rate and timing of slurry application to grassland on the preference by cattle for treated and untreated areas of pasture

Two experiments were conducted in the UK to investigate preference by cattle for areas of pasture treated or untreated with dairy cow slurry. Experiment 1 examined the effects of method and rate of slurry applied to a grass pasture in March (Spring); Experiment 2 examined the effects of method and timing of slurry application after cutting for silage in June (Summer). In both experiments, beef steers grazed grassland plots that had been treated with slurry on one half only of the plots for 4 weeks. Slurry was applied by shallow injection (I), trailing shoe (T) or conventional surface broadcasting (S) techniques. In Experiment 1, slurry was applied at 40 m³ ha^?1 (HI) or 20 m³ ha^?1 (LO) 21 d before grazing commenced; in Experiment 2, slurry was applied at 20 m³ ha^?1 either 32 d (E) or 10 d (L) before grazing commenced. Sward height was measured and animal behaviour was recorded during 8 × 24 h measurement periods in each experiment. Preference for slurry‐treated or untreated swards was indicated by a comparison of post‐grazing sward height on each sward and the proportion of total grazing time spent on the slurry‐treated swards. In Experiment 1, a smaller proportion of grazing time was spent on slurry‐treated areas of swards compared with untreated areas of swards on all treatments, but the proportion of time spent grazing the slurry‐treated sward was greater on method T than on methods I or S (0·28, 0·31 and 0·39 for methods S, I and T, respectively, s.e.d. = 0·035, P < 0·05). Steers showed no preference between slurry‐treated and untreated swards by 49, 45 and 44 d after slurry application for methods S, I and T respectively. Differences between HI and LO were not significant (P > 0·05). In Experiment 2, aversion to slurry‐treated swards compared with untreated swards was less for treatment E than for L, with a greater proportion of both residence and grazing time spent on the slurry‐treated sward of treatment E than L (0·43 and 0·28, respectively, for residence time, s.e.d. = 0·025, P < 0·001, and 0·47 and 0·30, respectively, for grazing time, s.e.d. = 0·021, P < 0·001). Significant differences were shown between the methods of slurry application for treatment E, with a greater proportion of grazing time spent on the slurry‐treated swards of methods I and T than method S (0·40, 0·52 and 0·49 for S, I and T, respectively, s.e.d. = 0·032, P < 0·001), and a greater difference between post‐grazing heights on slurry‐treated and untreated swards for method S than for I or T (30, 12 and 15 mm, respectively, s.e.d. = 4·8, P < 0·001). For treatment L, differences in the proportion of time spent grazing on slurry‐treated swards compared with untreated swards were not significant between treatments (0·26, 0·34 and 0·31 for methods S, I and T, respectively, s.e.d. = 0·040, P > 0·05) and indifference between slurry‐treated and untreated swards was achieved 77, 60 and 58 d after slurry spreading for methods S, I and T respectively. These results show that, when slurry is applied to pasture in a grazing rotation, the adverse effects on grazing behaviour associated with conventional surface broadcasting may be overcome by the use of novel slurry application techniques.     

Mitigation of N2O emissions from grassland by nitrification inhibitor and Actilith F2 applied with fertilizer and cattle slurry

Abstract. Nitrous oxide (N₂O) is involved in both ozone destruction and global warming. In agricultural soils it is produced by nitrification and denitrification mainly after fertilization. Nitrification inhibitors have been proposed as one of the management tools for the reduction of the potential hazards of fertilizer-derived N₂O. Addition of nitrification inhibitors to fertilizers maintains soil N in ammonium form, thereby gaseous N losses by nitrification and denitrification are less likely to occur and there is increased N utilization by the sward. We present a study aimed to evaluate the effectiveness of the nitrification inhibitor dicyandiamide (DCD) and of the slurry additive Actilith F2 on N₂O emissions following application of calcium ammonium nitrate or cattle slurry to a mixed clover/ryegrass sward in the Basque Country. The results indicate that large differences in N₂O emission occur depending on fertilizer type and the presence or absence of a nitrification inhibitor. There is considerable scope for immediate reduction of emissions by applying DCD with calcium ammonium nitrate or cattle slurry. DCD, applied at 25 kg ha^–1, reduced the amount of N lost as N₂O by 60% and 42% when applied with cattle slurry and calcium ammonium nitrate, respectively. Actilith F2 did not reduce N₂O emissions and it produced a long lasting mineralization of previously immobilized added N.