不同乳酸菌组合对苜蓿青贮细菌群落结构的影响

为探讨不同乳酸菌互作对苜蓿（Medicago sativa）青贮细菌群落结构的影响，以2种植物乳杆菌、乳酸片球菌、戊糖片球菌及凝结芽孢杆菌形成的6种乳酸菌组合按1.5 mL·kg^-1的添加量制作苜蓿青贮，以等量蒸馏水替代添加剂作为对照，45 d后运用高通量测序分析细菌群落结构。结果表明，各苜蓿青贮的优势乳酸菌群均为厚壁菌门（Firmicates）的乳杆菌属（Lactobacillus）和片球菌属（Pediococcus），二者相对丰度之和为65.4%~79.0%，其中含植物乳杆菌处理高于对照和含凝结芽孢杆菌处理；与对照相比，乳酸菌组合处理提高了菌群Chao1和ACE指数但降低了Simpson和Shannon指数；6个乳酸菌组合处理中，含凝结芽孢杆菌处理组与对照相似性较高，对苜蓿青贮细菌群落影响较小；相关分析表明，苜蓿青贮菌群结构和多样性可较好地解释其营养品质的变化。综上，乳酸菌组合在一定程度上改善了苜蓿青贮的细菌群落结构，其中含植物乳杆菌的组合效果较好。     

不同药剂组合对马铃薯晚疫病的防治效果

马铃薯晚疫病是马铃薯生产中的重要病害,是影响马铃薯产量和品质的重要因素之一,在云南春作马铃薯上普遍发生,且危害较重,给当地马铃薯产业带来了巨大的经济损失。为减轻马铃薯晚疫病对马铃薯生产造成的损失,试验研究了11种药剂7种药剂组合(包衣剂+保护剂+治疗剂)通过播种期种薯包衣,现蕾期叶面喷施一次保护剂,发病初期和发病中期叶面各喷一次治疗剂的方法防治马铃薯晚疫病。结果表明,药剂组合种薯包衣+甲霜·锰锌+氟吡菌胺·霜霉威的防治效果最好,防治效果达到60.99%,增产率176.28%,增效率152.27%;其次是种薯包衣+霜脲·锰锌+氟吡菌胺·霜霉威组合,防治效果达到60.15%,增产率173.20%,增效率150.55%。这2个药剂组合对马铃薯晚疫病均有极显著的防治效果,增产增效明显。     

食源性病原及其毒素检测技术研究进展

食源性病原包括细菌、真菌、病毒、朊病毒和原虫,它们在生产加工及储运环节污染食物,同时不断分泌包含毒素在内的各种成分到细胞外直至自身死亡和裂解,其中一些病原菌及其毒素能耐受复杂的食物加工,直至进入人体干扰细胞生理过程并引发疾病。详细介绍了如何利用各种"组"学(包括蛋白质组、肽组、代谢组和食品组学)技术检测和寻找食源性病原微生物的生物标志物,深入了解其产毒机理、毒力和致病机理,及对胁迫的适应能力。这对于追踪食源性病原微生物内、外毒素的来源,保证食品安全并控制食源性疾病爆发具有重要意义。     

多花黑麦草特高和多年生黑麦草四季高频组培再生体系的优化与建立

对在贵州地区广泛种植的多花黑麦草特高(Lolium multiflorum‘Tetragold’)和多年生黑麦草四季(L.perenne‘Four seasons’)的成熟种子进行了愈伤组织诱导及植株再生的研究,建立了两个品种的胚性愈伤组织高频诱导与再生体系。结果表明,剥去成熟种子的颖壳,切除1/3胚乳端,将特高接种于CC+7mg·L~(-1) 2,4-D+0.5mg·L~(-1) 6-BA、四季接种于CC+5mg·L~(-1) 2,4-D+0.5 mg·L~(-1) 6-BA的培养基中,在明显降低组培污染率的同时,能分别得到65.52%和63.55%的最高愈伤组织诱导率;将两个品种诱导出的愈伤组织转移在MS+0.5 mg·L~(-1) 2,4-D+0.5mg·L~(-1) 6-BA+1.25mg·L~(-1) CuSO4+1.0g·L~(-1) CH的继代培养基上,能促进质量较好的Ⅱ型胚性愈伤组织的形成;根据后续转化试验所选用的植物表达载体pCAMBIA 1300的抗性特点,30~40mg·L~(-1)的潮霉素是两个品种愈伤组织最佳的筛选剂和临界浓度;特高的胚性愈伤组织接种在MS+2.0 mg·L~(-1) 6-BA+0.5 mg·L~(-1) NAA+0.1mg·L~(-1) TDZ的培养基上,可以产生86.37%的最高分化率,四季的胚性愈伤组织接种在MS+6.0 mg·L~(-1) 6-BA+0.3mg·L~(-1) NAA+5.0mg·L~(-1) KT的培养基上,能得到85.40%的最高分化率;生根培养基1/2MS+0.5 mg·L~(-1)NAA+0.5mg·L~(-1) IAA能让两个品种分化出的不定芽形成100%的生根率;以腐殖土∶蛭石∶砂壤土=1∶1∶1的混合材料作为营养土,能保证组培再生苗达到99%以上的成活率。优化建立的高频组培再生体系为下一步的遗传转化奠定了基础。     

不同菌剂处理对玉米芯发酵过程中纤维素降解及相关酶活性的影响

以玉米芯为发酵原料,EM酵素菌、有机物料腐熟剂、金宝贝菌剂3种市售菌剂为发酵菌剂,研究了3种菌剂处理对玉米芯发酵过程中纤维素降解及相关酶活性的影响。结果表明,不同发酵菌剂处理后,纤维素降解酶的活性均增强,玉米芯基质中的纤维素、半纤维素降解率高于对照,其中EM酵素菌处理效果最佳;3种菌剂处理使木质素过氧化物酶活性增强,可有效提高玉米芯基质中的木质素降解率,其中金宝贝菌剂处理效果最佳,与对照相比降解率提高21.1%~50.5%。     

Contributions of ammonia-oxidizing archaea and bacteria to nitrification in Oregon forest soils

Ammonia oxidation, the first step of nitrification, is mediated by both ammonia-oxidizing archaea (AOA) and bacteria (AOB); however, the relative contributions of AOA and AOB to soil nitrification are not well understood. In this study we used 1-octyne to discriminate between AOA- and AOB-supported nitrification determined both in soil-water slurries and in unsaturated whole soil at field moisture. Soils were collected from stands of red alder (Alnus rubra Bong.) and Douglas-fir (Pseudotsuga menziesii Mirb. Franco) at three sites (Cascade Head, the H.J. Andrews, and McDonald Forest) on acidic soils (pH 3.9–5.7) in Oregon, USA. The abundances of AOA and AOB were measured using quantitative PCR by targeting the amoA gene, which encodes subunit A of ammonia monooxygenase. Total and AOA-specific (octyne-resistant) nitrification activities in soil slurries were significantly higher at Cascade Head (the most acidic soils, pH < 5) than at either the H.J. Andrews or McDonald Forest, and greater in red alder compared with Douglas-fir soils. The fraction of octyne-resistant nitrification varied among sites (21–74%) and was highest at Cascade Head than at the other two locations. Net nitrification rates of whole soil without NH₄⁺ amendment ranged from 0.4 to 3.3 mg N kg⁻¹ soil d⁻¹. Overall, net nitrification rates of whole soil were stimulated 2- to 8-fold by addition of 140 mg NH₄⁺-N kg⁻¹ soil; this was significant for red alder at Cascade Head and the H.J. Andrews. Red alder at Cascade Head was unique in that the majority of NH₄⁺-stimulated nitrifying activity was octyne-resistant (73%). At all other sites, NH₄⁺-stimulated nitrification was octyne-sensitive (68–90%). The octyne-sensitive activity—presumably AOB—was affected more by soil pH whereas the octyne-resistant (AOA) activity was more strongly related to N availability.     

Fungal and bacterial N2O production regulated by soil amendments of simple and complex substrates

Fungal N₂O production results from a respiratory denitrification that reduces NO₃⁻/NO₂⁻ in response to the oxidation of an electron donor, often organic C. Despite similar heterotrophic nature, fungal denitrifiers may differ from bacterial ones in exploiting diverse resources. We hypothesized that complex C compounds and substances could favor the growth of fungi over bacteria, and thereby leading to fungal dominance for soil N₂O emissions. Effects of substrate quality on fungal and bacterial N₂O production were, therefore, examined in a 44-d incubation after soils were amended with four different substrates, i.e., glucose, cellulose, winter pea, and switchgrass at 2 mg C g⁻¹ soil. During periodic measurements of soil N₂O fluxes at 80% soil water-filled pore space and with the supply of KNO₃, substrate treatments were further subjected to four antibiotic treatments, i.e., no antibiotics or soil addition of streptomycin, cycloheximide or both so that fungal and bacterial N₂O production could be separated. Up to d 8 when antibiotic inhibition on substrate-induced microbial activity and/or growth was still detectable, bacterial N₂O production was generally greater in glucose- than in cellulose-amended soils and also in winter pea- than in switchgrass-amended soils. In contrast, fungal N₂O production was more enhanced in soils amended with cellulose than with glucose. Therefore, fungal-to-bacterial contribution ratios were greater in complex than in simple C substrates. These ratios were positively correlated with fungal-to-bacterial activity ratios, i.e., CO₂ production ratios, suggesting that substrate-associated fungal or bacterial preferential activity and/or growth might be the cause. Considering substrate depletion over time and thereby becoming limited for microbial N₂O production, measurements of soil N₂O fluxes were also carried out with additional supply of glucose, irrespective of different substrate treatments. This measurement condition might lead to potentially high rates of fungal and bacterial N₂O production. As expected, bacterial N₂O production was greater with added glucose than with added cellulose on d 4 and d 8. However, this pattern was broken on d 28, with bacterial N₂O production lower with added glucose than with added cellulose. In contrast, plant residue impacts on soil N₂O fluxes were consistent over 44-d, with greater bacterial contribution, lower fungal contribution, and thus lower fungal-to-bacterial contribution ratios in winter pea- than in switchgrass-amended soils. Real-time PCR analysis also demonstrated that the ratios of 16S rDNA to ITS and the copy numbers of bacterial denitrifying genes were greater in winter pea- than in switchgrass-amended soils. Despite some inconsistency found on the impacts of cellulose versus glucose on fungal and bacterial leading roles for N₂O production, the results generally supported the working hypothesis that complex substrates promoted fungal dominance for soil N₂O emissions.     

Study the Effects of Siderophore-Producing Bacteria on Zinc and Phosphorous Nutrition of Canola and Maize Plants

Plant growth-promoting rhizobacteria (PGPR) are soil bacteria that are able to colonize rhizosphere and to enhance plant growth by means of a wide variety of mechanisms. In the present study, Myristica yunnanensis and Stenotrophomonas chelatiphaga strains were recognized as new records in Iran flora. According to the results, these strains significantly affected plants’ zinc and phosphorous contents which could be due to the production of phytosiderophore. Siderophore-producing bacteria increased canola zinc (Zn) content as strategy-I plant, while in maize, it can be said that probably the effect of phytosiderophore produced by plant on increasing root and shoot Zn content was more than siderophore produced by bacteria. These isolates could be used as bio-input for improving the plant productivity as a substitute to chemical fertilizers and also to correct the nutrient deficiencies in canola and maize for sustainable agriculture.