和谐社会下失地农民社会保障体系的构建——以合肥经济技术开发区为例     

刘林军  李娜 《安徽农业科学》2009,37(25)

在分析我国失地农民社会保障问题现状及当前存在的主要问题的基础上,以合肥经济技术开发区为例,构建了失地农民社会保障体系。  相似文献   

农业土地规模经营的理论探讨     

张万双 《黑龙江八一农垦大学学报》1989,(1):75-80

实现农业土地规模经营,有利于生产力有效运转并取得最佳的规模效益。其适度性受各种因素的影响,具有区域性和动态性。规模经营与劳动生产率有着密切的关系,应该在确保提高土地生产率的基础上来提高劳动生产和土地规模经营的效益。土地适当集中、土地经营主体的总人数尽量精简和劳动组合的优化是优化土地经营规模的三个相互制约的因素。要采取积极的措施逐步实现土地的规模经营。对现有土地经营形式要做具体分析,其调整应从有利于生产力发展出发,在尊重群众意愿的基础上稳步进行。  相似文献   

禽白血病病毒J亚群(ALV-J)的攻毒试验   总被引：2，自引：1，他引：1  

成子强  赵振华  张利  高娃 《中国兽医学报》2004,24(3):219-222

将禽白血病病毒 J亚群 (AL V- J)内蒙株 NM876 1和 NM9996人工接种于 1日龄爱维茵肉种鸡 ,通过眼观、病理组织学检查观察了攻毒鸡的病理学特征 ;通过 PCR和 EL ISA技术检测了病毒感染率、抗体变化规律以及病毒和抗体的相关性。结果显示 ,攻毒鸡从第 3周开始即可检出病毒 ,NM876 1株和 NM9996株病毒感染率分别为 71.4 %和6 4 .3% ;从第 5周开始 ,出现较明显的病理学变化 ,病变特征以骨髓、肝脏、心脏、脾、卵巢等组织内髓细胞增生为主 ,而法氏囊、脑、坐骨神经无变化 ;攻毒鸡抗体消长变化有一定的规律 ,一般在 7～ 8周龄和 18～ 2 0周龄时分别出现 1次高峰 ,而在 4～ 6周龄、10周龄和 2 3周龄分别出现 1次低谷 ,提示鸡场进行 EL ISA检测时要避开这一时期 ;攻毒鸡产生耐受性病毒血症 ,即病毒阳性而抗体阴性 (V A- )的比例较高 (7/14 ,9/14 )。通过以上的研究证明 ,AL V- J内蒙株疾病模型复制成功 ,NM876 1、NM9996可作为原型株进行相关研究  相似文献   

贵州省退耕还林与农村经济发展研究     

赵华 《林业调查规划》2004,29(1):57-60

通过对贵州省贞丰、桐梓、锦屏等若干县市林业生态建设监理、检查、造林实绩核查等工作的实践和研究，认为退耕还林工程与农村经济发展相结合，目前应加强以下工作：选择林业主导产业；林产业时间、空间的合理布局；树种、林种的结构优化；林业体制创新；实施相关配套工程。  相似文献   

松嫩平原羊草草地水淹干扰恢复过程的群落动态   总被引：16，自引：6，他引：10  

张宝田  杨允菲 《草业学报》2003,12(2):30-35

根据随机取样的测定数据，经过幂函数和多元回归分析及相关检验，揭示了草地水淹干扰对羊草 寸草苔、羊草 杂类草群范数量性状的变化规律。水淹干扰对草地植被的物种组成及其比例有明显的影响。水淹后基本恢复到正常草地的种类数量和生产量配置大约需要6—7年。随着生境水分减少和土壤变干，羊草种群的数量和生物量均以幂函数形式增加，而寸草苔和杂类草的数量和生物量则呈先增后降的变化过程。  相似文献   

Change in spatial characteristics of forest openings in the Klamath Mountains of northwestern California,USA   总被引：4，自引：0，他引：4  

Carl N. Skinner 《Landscape Ecology》1995,10(4):219-228

Change in the spatial characteristics of forest openings was investigated in three forested watersheds in north-western Siskiyou County, California totalling approximately 24,600 hectares. Watersheds with minimal human disturbance were chosen for study. However, fire suppression has been pervasive throughout. Characteristics of forest openings (area, perimeter, distance between neighboring openings) were measured on aerial photographs taken 41 years apart. An index of regional form was determined for the landscape. Shape complexity for each opening was calculated using two indices based upon fractals. Significant differences were found using the Kolmogorov-Smirnov two-sample test between the perimeters, areas, distance from sample point to nearest opening, and distance between neighboring openings. The perimeters and areas became smaller, and the distances from the sample point to the nearest opening and between neighboring openings became greater over the 41 years between aerial photo sets. The estimated area occupied by openings decreased from 25.8 % to 15.6 % of the study area. No significant difference was found in the shape of the openings except as the shape indices were influenced by changes in size of the openings.This article was written and prepared by U.S. Government employees on official time, and it is therefore in the public domain and not subject to copyright.  相似文献   

A review of models of landscape change   总被引：23，自引：1，他引：22  

William L. Baker 《Landscape Ecology》1989,2(2):111-133

Models of landscape change may serve a variety of purposes, from exploring the interaction of natural processes to evaluating proposed management treatments. These models can be categorized as either whole landscape models, distributional landscape models, or spatial landscape models, depending on the amount of detail included in the models. Distributional models, while widely used, exclude spatial detail important for most landscape ecological research. Spatial models require substantial data, now more readily available, via remote sensing, and more easily manipulated, in geographical information systems. In spite of these technical advances, spatial modelling is poorly developed, largely because landscape change itself is poorly understood.To facilitate further development of landscape models I suggest (1) empirical multivariate studies of landscape change, (2) modelling of individual landscape processes, (3) explicit study of the effect of model scale on model behavior, and (4) scaling-up results of studies, on smaller land areas, that have landscape relevance.  相似文献   

陆地棉核雄性不育材料在山东不同地区的育性转变及应用研究     

张军  庞居勤 《山东农业科学》1996,(1):4-7

对在山东的济南、平度、莱西、烟台种植的几种陆地棉（Ｇｏｓｓｙｐｉｕｍ　ｈｉｒｓｕｔｕｍＬ．）核雄性不育材料的育性表现进行了研究,结果表明：洞Ａ不育系的衍生材料ＭＢ、ＭＡ在不同气候条件下有育性的变化。在济南高度不育,可作为不育系。在其他几个地区表现不同程度的可育。其中ＭＢ在平度有相当好的育性,能正常结铃。而双隐性核不育材料５９Ａ、６２Ａ未能观察到育性变化。本文就核不育材料在棉花杂交制种中的应用前景及需深入研究的问题作了探讨。  相似文献   

THE CLIMATE CHANGE AND FORESTRY OF HEILONGJI ANG PROVINCE IN 1990''''S     

姜乃准  段文标 《林业研究》1995,(4)

INTRODUCTIONIntheworldoftoday,theglobalclimatechangeanditsinfluenceonecologyhavebe-comeaveryimportantproblem,towhichmanyscientists,governnentleadersandordinarypcoplepaycloseattentionI1-'].Inl979,theWorldClimateResearchProgram(WCP)waslaiddowninthefirstworldclimatemeeting.lnl99(),thesecondworldclimatemeetingwasconvcl1edinGencva,andalltl1eexpertsagreedthattheglobalwarmlngwillbeextremelyseriousdisasterthananynatUralcalamityever.Attl1eMectingof"WorldEnvironmentandDevelopment,"holdinBrazil…  相似文献   

An investigation of uncertainty in field habitat mapping and the implications for detecting land cover change     

Andrew Cherrill  Colin McClean 《Landscape Ecology》1995,10(1):5-21

Land cover data for landscape ecological studies are frequently obtained by field survey. In the United Kingdom, temporally separated field surveys have been used to identify the locations and magnitudes of recent changes in land cover. However, such map data contain errors which may seriously hinder the identification of land cover change and the extent and locations of rare landscape features. This paper investigates the extent of the differences between two sets of maps derived from field surveys within the Northumberland National Park in 1991 and 1992. The method used in each survey was the Phase 1 approach of the Nature Conservancy Council of Great Britain. Differences between maps were greatest for the land cover types with the smallest areas. Overall spatial correspondence between maps was found to be only 44.4%. A maximum of 14.4% of the total area surveyed was found to have undergone genuine land cover change. The remaining discrepancies, equivalent to 41.2% of the total survey area, were attributed primarily to differences of land cover interpretation between surveyors (classification error). Differences in boundary locations (positional error) were also noted, but were found to be a relatively minor source of error. The implications for the detection of land cover change and habitat mapping are discussed.  相似文献