滇中冷凉山区不同播期反季花椰菜产量效益分析

为摸索滇中高海拔冷凉山区反季节栽培花椰菜的最佳播期以集成高效栽培技术推广应用,于2017—2018年选择海拔2250 m的云南省峨山县塔甸镇大西村地块进行9个播期的2年随机区组试验。结果表明,花椰菜生育期随播期推迟而延长,而花球采收期除播期7月10日外随播期推迟而逐渐增长;花椰菜株高、外叶数、开展度、球高、球径和单球重等农艺性状有随播期延迟呈现先逐渐减小而后又逐渐增大的趋势;莲座期黑腐病和霜霉病的病情指数随着播期的延迟呈现先逐渐升高而后又逐渐下降的趋势;花椰菜小区产量随着播期的延迟呈现先逐渐下降而后又逐渐提高的趋势,播期4月20日和4月30日与其余7个播期产量之间的差异达极显著水平。综合花椰菜在冷凉山区反季节栽培的生产实际和各播期产量产值及商品性表现,推荐滇中高海拔冷凉山区反季节栽培花椰菜的最佳播期为4月20—30日。     

完善农村居民最低生活保障制度的几点建议

当前，我国农村普遍建立了居民最低生活保障制度，这是保障农村社会稳定的“最后一道安全网”，是中国农村社会保障体系的基础工程。但是，我国农村居民最低生活保障制度也还存在一些问题，例如保障对象、保障方式、保障资金、管理体制等，充分认识并采取 有效措施解决好这些问题，对于完善农村社会保障体系，维护农村社会稳定和经济发展有着重要现实意义。     

南方山区草地资源的类型及开发利用途径

根据生态学的基本原理，对我国南方山区草地资源的特点进行了分析，从生态学类型上对该地区草地进行了划分，进而提出了南方山区草地开发利用的途径。     

牦牛放牧率对小嵩草高寒草甸不同植物类群地上生物量生产率的影响

2年的牦牛放牧试验表明:除不同植物本身的生理特性外,降水和地温是影响小嵩草高寒草甸两季草场不同植物类群地上生物量绝对生长率的关键因素。小嵩草高寒草甸两季草场地上总生物量的绝对生长率1999年在7月份最大;1998年,冷季草场各放牧处理的绝对生长率在8月份达到最大,暖季草场的对照组和轻牧组在7月份最大,中牧组和重牧组在8月份最大。不同植物类群地上生物量生长率的变化不尽相同。1998年,冷季草场禾草和莎草地上生物量的绝对生长率8月份达到最大,暖季草场禾草和莎草地上生物量的绝对生长率7月份达到最大,且9月份出现了营养的再次积累;1999年,冷季草场禾草地上生物量的绝对生长率在6月份和8月份出现了两个峰值,暖季草场禾草地生物量的绝对生长率在7月份达到最大。对杂草类而言,1998年冷季草场的绝对生长率6月份最大,暖季草场重牧组的绝对生长率8月份达到最大,其他各处理7月份达到最大;1999年重牧组杂草的绝对生长率在6月份达到最大,其他各处理杂草在8月份达到最大。     

中国结缕草属(Zoysia spp.)植物抗寒性评价

在广泛收集结缕草属(ZoysiaWild.)种质资源基础上,按照形态类型和地理分布,选取40份种质,采用电导法(EL)对其抗寒性进行初步评价。以半致死温度(LT50)为评价指标,在参试材料中除大穗结缕草和来自台湾岛海边沙地的沟叶结缕草外,其它种质都较天堂-419(对照)抗寒;在结缕草属内,抗寒性具有明显的种间差异,耐寒性依次为日本结缕草>中华结缕草>沟叶结缕草>细叶结缕草>长花中华结缕草>大穗结缕草,其中细叶类型的沟叶结缕草和细叶结缕草抗寒性变异较大;日本结缕草和中华结缕草抗寒性变异与地理分布之间没有显著关系,但分布在海边的种类和种质抗寒性明显较低;结缕草属及其中华结缕草的抗寒性与叶长、叶宽以及叶背面被毛之间均存在显著的负相关关系,但这种关系不体现在日本结缕草上。实验结果还表明,EL方法是评价结缕草属抗寒性较为可靠的方法之一。     

苹果酸处理水稻种子对秧苗根系及抗寒性影响的初探

水稻种子经苹果酸处理后,淀粉酶过氧化氢酶和脱氢酶活性均有提高。其幼苗根系发达,根/茎叶比重增加。幼苗经5C冷处理后,超氧化物歧化酶活性和叶绿素含量虽表现出下降,但明显高于对照。丙二醛含量和电解质渗漏率比对照为低。苹果酸处理在一定程度上提高了水稻秧苗素质及抗寒能力。     

春制越年家蚕卵乙胚子冷藏方法研究

研究结果表明，春制越年家蚕卵丝乙胚子冷藏处理后，其实用孵化率〉９２．３％蚁蚕绝食致半数时数≥１１０ｈ，不良卵发生率〈１０％，发病率〈８．６％，茧质优良，产量平稳，在有效冷藏期限内随时出库催青饲育均安全可靠。     

浅析农牧交错区特殊地位与生态环境建设难点

农牧交错区是国家实施西部大开发的重点区域,通过建国50多年的艰苦努力,已经成为一条经济产业带,生产了大量的煤炭、石油、天然气和农牧产品支持国家的经济建设,并对西部地区起着重要的吸引和辐射作用。通过野外调查和资料分析,按照典型剖析、专题研究、总结提高的基本思路,分析了农牧交错区在国家经济建设中的地位与作用,探讨了在西部大开发中生态环境建设面临的严峻挑战,进而提出了相应的发展对策。     

以电导法配合Log istic方程确定茶梅‘小玫瑰’的抗寒性

 摘　要: 以不同处理时间、不同低温处理下茶梅‘小玫瑰’叶片的电解质外渗率(REC) 变化作曲线,并结合Logistic方程分别计算茶梅的半致死温度(LT50 ) , 结果发现在低温处理6 h以上, 茶梅叶片的REC均随着处理温度的降低而呈“S”形上升, 由此计算出“S”形拐点对应的温度即为茶梅叶片的LT50 , 其温度值在- 1215℃至- 14℃之间, 这可认为是茶梅抗寒能力的重要指标。关键词:     

Effects of land ownership and landscape-level factors on rare-species richness in natural areas of southern Ontario,Canada

Surprisingly few studies have considered the extent to which the nature of the ownership of land is associated with differences in biodiversity. We analysed ownership and other landscape-level effects on rare-species richness for both globally- and regionally-rare biota (including birds, herpetofauna, butterflies, mammals, and plants) in 289 designated natural areas (NAs) in southern Ontario, Canada. Information about each NA −including area, number of plant communities, ownership status and details of species diversity were collected from published sources. Length of perimeter of NA, relative isolation, and an estimate of fragmentation were measured using image analysis and GIS techniques. NAs were in general relatively small, with mean area of 158 ha (median 85 ha, range from 0.9 to 1278 ha) for private NAs; public NAs had mean area of 132 ha (median 16 ha, range from 0.1 to 1481 ha). Mean number of plant communities was 4.6 (median 4, range 1- 13) at private NAs and 3.8 (median 3, range 1-16) at public NAs. Our results show that, of several landscape-level factors, area had the greatest effects on rare-species richness and other biotic indices. Effects of area were followed by effects of plant community diversity, however this was itself significantly affected by area and the extent of perimeter of the NA. Both these factors were followed by effects of ownership of the NA and by effects of isolation of the NA (represented by minimum distance to nearest NA and by number of NAs in 10 km radius). Other landscape- level factors did not appear to have overall significant effects. Variation in area accounted for 0.1% to 29% of variation in number of rare species, with lower values for globally-rare, than for regionally-rare taxa. For all biotic groups, public ownership of NAs was associated with significantly greater rare-species richness compared to private ownership, even after other factors such as area were controlled. For all globally-rare biota except butterflies, area of NA had greater effects on rare-species richness than did ownership. Richness of regionally- rare birds was more affected by plant community diversity than by area of NA. Number of recorded plant communities accounted from 2.1% of variation in number of globally-rare plant species to as high as 31% of variation in regionally-rare butterflies. The diversity of plant communities was itself influenced by total site area (accounting for 45% of variation), extent of elongation of the NA, and both external- and interior- edge perimeters. Public NAs had greatest numbers of rare biota and so should be a significant focus for conservation programs. Smaller, privately-owned patches of natural area dominate (by number and area) in this densely populated region and their significance should not be overlooked. This revised version was published online in July 2006 with corrections to the Cover Date.