食用向日葵产量性状的遗传研究

以食葵不育系17-A26为母本、恢复系17-C19为父本,构建P₁、P₂、F₁、F₂、B₁和B₂ 6个世代群体,研究了产量相关性状盘径、单株总粒数、结实率、百粒重、粒长和粒宽的后代变异及遗传率。结果表明,6个性状均为数量性状,变异幅度排序为单株总粒数>粒长>盘径>结实率>百粒重>粒宽,狭义遗传率排序为百粒重>粒长>单株总粒数>粒宽>盘径>结实率。根据遗传进度结果,百粒重、粒长、单株总粒数和粒宽宜早代根据表型选择,盘径宜晚代选择,结实率宜晚代结合多环境联合选择。     

合理调整山西人民食物结构的策略与途径

合理调整我国人民的食物结构是提高全民族身体素质,推进社会文明进步,具有深远的战略意义的一项国策。调整国民食物结构是一个科学性,政策性很强,社会涉及面广,地区人群民食习惯差别大的极为复杂的动态系统工程。作者针对山西省情实际,从追朔我国饮食传统,膳食民习,食物资源及演变趋向探求,提出合理调整山西人民食物结构的策略与途径。     

以固氮树种发展食用菌专用林的建议

许多固氮树种速生丰产，萌生能力强，叶片，木屑含氮率较高，可为食用菌栽培提供理想原料，而且固氮树种在绿花荒山，保持水土，提高地力方面作用显著，以固氮树种发展短轮伐期食用菌专用林，具有较高的经济效益和生态效益，本文介绍了银合欢，黑荆，大叶相思，银荆，桤木，南洋楹和马占相思等在食用菌栽培上的应用概况，各地可因地制宜栽培合适的固氮树种作为食用菌专用林。     

食用菌复合保水颗粒菌种生产工艺及其应用研究

运用微生物发酵技术，配合新型合成材料，研制出食用菌复合保水颗粒菌种。这类菌种可保持活力60d。这一工艺可用于糙皮侧耳、金针菇、灵芝、白灵菇、杏鲍菇、鸡腿蘑和鲍鱼菇等多种食用菌苗种的制作。栽培试验证明，此类菌种的菌丝生长速度、现蕾时间、生物学效率与常用的棉籽壳菌种相似。     

我国食用菌出口遭遇贸易壁垒的原因、类型及对策

贸易壁垒正在成为我国农产品出口的瓶颈。本文分析了我国食用菌产品出口遭遇的贸易壁垒类型及其原因，并提出了相关建议。     

酯酶同工酶在食用菌菌种选育中的应用研究

采用聚丙烯酰胺凝胶电泳 ,分析了不同培养时间和不同培养基种类对平菇、杏鲍菇、白灵菇酯酶同工酶的影响 ,结果表明在不同培养时间和不同培养基条件下 ,酯酶同工酶酶谱的酶带呈现不同的多态性 ,由此提示同工酶在食用菌菌种选育的应用上应固定最佳培养时间及最适培养基种类 ,并在所有操作条件一致的情况下 ,才能得到稳定准确的分析结果     

云南省食用菌产业技术标准体系建设研究

分析了食用菌标准化现状，归纳目前食用菌标准体系存在的主要问题，提出云南省食用菌标准体系建设的原则与依据，按照产前、产中、产后划分标准类别，构建云南省食用菌产业技术标准体系。     

食用型紫心甘薯新品种湘紫薯174 的选育

湘紫薯174 是以浙紫薯1 号为母本、浙紫薯3 号为父本杂交选育而成的食用型紫心甘薯新品种，薯块纺锤形，薯皮 紫红色，薯肉紫色，结薯较集中整齐，单株结薯4～5 个，大中薯率82.7% 以上，熟食味好，抗黑斑病，中抗根腐病、茎线 虫病和薯瘟病；每667 m² 鲜薯产量1 913～2 359 kg，薯干产量549～736 kg；花青素含量为714.5 mg · kg^-1（FW）。适宜在湖 南、湖北、江西、江苏、浙江等地春夏薯区种植。     

Environmental stress response limits microbial necromass contributions to soil organic carbon

The majority of dead organic material enters the soil carbon pool following initial incorporation into microbial biomass. The decomposition of microbial necromass carbon (C) is, therefore, an important process governing the balance between terrestrial and atmospheric C pools. We tested how abiotic stress (drought), biotic interactions (invertebrate grazing) and physical disturbance influence the biochemistry (C:N ratio and calcium oxalate production) of living fungal cells, and the subsequent stabilization of fungal-derived C after senescence. We traced the fate of ¹³C-labeled necromass from ‘stressed’ and ‘unstressed’ fungi into living soil microbes, dissolved organic carbon (DOC), total soil carbon and respired CO₂. All stressors stimulated the production of calcium oxalate crystals and enhanced the C:N ratios of living fungal mycelia, leading to the formation of ‘recalcitrant’ necromass. Although we were unable to detect consistent effects of stress on the mineralization rates of fungal necromass, a greater proportion of the non-stressed (labile) fungal necromass C was stabilised in soil. Our finding is consistent with the emerging understanding that recalcitrant material is entirely decomposed within soil, but incorporated less efficiently into living microbial biomass and, ultimately, into stable SOC.     

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.