新疆林业生态环境中的木垒胡杨林群落特征研究

对新疆林业生态环境中木垒胡杨林群落的多样性特征进行研究,分析胡杨林群落的相似度变 化趋势,通过个体数对数和失稳率研究胡杨林的结构与动态特征。结果表明:在多样性特征中,中、 下游区域临界点的胡杨林群落丰富度最高,中游区域的丰富度最小;生态输水前,下游区域的胡杨 林群落均匀度指数最小,中游区域的均匀度指数最大,生态输水后,中、下游区域临界点处的均匀度 指数最大,下游区域的均匀度指数最小;生态输水后的物种多样性高于生态输水前的物种多样性, 下游区域的物种多样性受生态输水的影响较小;在相似性特征中,Jaccard 指数和Sorenson 指数在 不同区域内的变化趋势相似;在胡杨林结构与动态特征中,胡杨林种群在上游区域中的数量较多, 种群的个体数与高度级呈反比。     

矿区生态监测的地理加权遥感生态指数构建及评价

矿区生态是陆地生态系统的重要组成部分,准确监测矿区生态对保护生态环境、维持生态平衡具有重要意义。遥感技术为矿区生态监测提供了有效手段,针对遥感生态指数（remote sensing ecological index,RSEI）在矿区生态监测中存在监测精度低、针对性弱和指标权重空间上均一化问题,该研究对RSEI进行了改进。首先,考虑矿区特殊的生态成因,在绿度、热度、湿度、干度的基础上加入煤尘污染因子构成矿区遥感生态指数;然后,利用地理加权主成分分析法确定各指标的空间权重,构建了地理加权遥感生态指数（geographically weighted-remote sensing ecological index,GW-RSEI）;最后,以山西省大同煤田为例,基于多期遥感影像对GW-RSEI在矿区生态监测中的有效性、适用性进行了验证。结果表明：GW-RSEI能准确捕捉矿区大气中的煤尘污染,从整体和局部尺度实现了矿区生态的精准监测,有效提高了矿区生态监测的精度;地理加权主成分分析法能够明确表征矿区生态的空间异质性和生态环境变化的空间连续性;2000—2020年大同煤田的GW-RSEI均值分别为0.51、0.48、0.46、0.59、0.56,整体生态环境经历了先恶化后改善的过程,其东南部生态环境变化趋势与整体一致,而西北部生态环境呈现先改善后恶化的变化趋势。研究成果为准确监测矿区生态提供了一种更加科学、有效的方法。     

极简主义对现代园林艺术的影响

通过对极简主义艺术的起源,特点以及理念的探讨;对极简主义园林东西方渊源的追溯及对现代园林中具有极简主义特征的实例的分析,总结出极简主义艺术在内在文化理念、外在创作形式两个方面对现代园林的影响,指出了学习西方极简主义园林对我国现代园林景观发展的实际意义。     

驻马店小麦条锈病发生气象指数预报方法探讨

小麦条锈病是河南省驻马店市小麦生产中的主要病害之一,历史上曾多次造成小麦严重减产。在分析小麦条锈病发病及流行特征的基础上,应用统计方法建立了条锈病病发气象指数预报气候模型和指数预测方程,并连续2a准确作出病发气象指数预报,为植保部门正确作出病害流行趋势预测预报提供了科学依据。     

茶产业集聚的实证研究

产业集聚是经济发展过程中所表现出的一种空间聚集和地方专业化的经济现象。利用区位商LQ系数和产业地理集中指数对安徽省茶产业2002~2006年的集聚情况进行效益分析。结果表明,安徽茶产业具有明显的产业集聚现象,且主要集中在皖南和皖西地区,并通过其回归分析模型验证了茶产业的集聚水平与产业的发展高度正相关。     

Progress in Research of Chinese Wetland Parks

There has been a rapid development in the construction of wetland parks in China in recent years.This paper discussed the progress in the research of Chinese wetland parks that covered the aspects of wetland resources,landscape and environment.The function of wetland parks,the evaluation of landscape and the exploiting of resources;the landscape concept and landscape planning and design;the plant environment,the water environment and the recreation environment were all reviewed.The research of Chinese wetland parks started later but developed rapidly,having remarkable achievements in practice and functional studies,and there are still some shortcomings in the researches to be improved.At last,the key points which should be researched urgently in the future were discussed.     

Path analysis of spatial predictors of front-yard landscape in an anthropogenic environment

Contagious spatial patterns were shown to exist in the landscape of front-yards in street sections of Hochelaga-Maisonneuve, Montréal. Neighbour mimicry was hypothesized as the mechanism behind this pattern (Zmyslony and Gagnon 1998). To assess the role of spatial environmental factors in structuring this pattern, we carried out a path analysis on the front-yard landscape with five spatial factors: relative distance, street side, width, depth and type of front-yard. We removed all non-significant factors from our model with simple Mantel tests and untangled the common spatial component from the relationship between spatial factors and front-yard landscape with partial Mantel tests. We then used path analysis to evaluate the relative importance of all significant spatial factors in structuring front-yard landscape and to determine the r ² (% of landscape variation explained by spatial factors). Results showed that (1) among all spatial environmental factors, distance (proximity) remained the best predictor of front-yard vegetation – distance alone explained an average of 20% of the landscape variation of a street section, (2) depth, width and type of front-yard also structured the front-yard landscape independently of distance, (3) front-yard landscape expresses greater similarity within the same side of a street section, and (4) in two street sections of Hochelaga-Maisonneuve, spatial factors predicted over 40% of the landscape variation. This suggests (1) that landscape contagion exists also in highly humanized environments and (2) that the mimicry phenomenon was induced not only by proximity, but also by similar environmental conditions in same side street sections and whole street sections. Finally, we suggest that street sections are a very useful and appropriate unit of analysis of urban ecosystems.     

An aggregation index (AI) to quantify spatial patterns of landscapes

There is often need to measure aggregation levels of spatial patterns within a single map class in landscape ecological studies. The contagion index (CI), shape index (SI), and probability of adjacency of the same class (Qi), all have certain limits when measuring aggregation of spatial patterns. We have developed an aggregation index (AI) that is class specific and independent of landscape composition. AI assumes that a class with the highest level of aggregation (AI =1) is comprised of pixels sharing the most possible edges. A class whose pixels share no edges (completely disaggregated) has the lowest level of aggregation (AI =0). AI is similar to SI and Qi, but it calculates aggregation more precisely than the latter two. We have evaluated the performance of AI under varied levels of (1) aggregation, (2) number of patches, (3) spatial resolutions, and (4) real species distribution maps at various spatial scales. AI was able to produce reasonable results under all these circumstances. Since it is class specific, it is more precise than CI, which measures overall landscape aggregation. Thus, AI provides a quantitative basis to correlate the spatial pattern of a class with a specific process. Since AI is a ratio variable, map units do not affect the calculation. It can be compared between classes from the same or different landscapes, or even the same classes from the same landscape under different resolutions.     

Scale-dependent habitat use in three species of prairie wetland birds

We evaluated the influence of scale on habitat use for three wetland-obligate bird species with divergent life history characteristics and possible scale-dependent criteria for nesting and foraging in South Dakota, USA. A stratified, two-stage cluster sample was used to randomly select survey wetlands within strata defined by region, wetland density, and wetland surface area. We used 18-m (0.1 ha) fixed radius circular-plots to survey birds in 412 semipermanent wetlands during the summers of 1995 and 1996. Variation in habitat use by pied-billed grebes (Podilymbus podiceps) and yellow-headed blackbirds (Xanthocephalus xanthocephalus), two sedentary species that rarely exploit resources outside the vicinity of nest wetlands, was explained solely by within-patch variation. Yellow-headed blackbirds were a cosmopolitan species that commonly nested in small wetlands, whereas pied-billed grebes were an area-sensitive species that used larger wetlands regardless of landscape pattern. Area requirements for black terns (Chlidonias niger), a vagile species that typically forages up to 4 km away from the nest wetland, fluctuated in response to landscape structure. Black tern area requirements were small (6.5 ha) in heterogeneous landscapes compared to those in homogeneous landscapes (15.4–32.6 ha). Low wetland density landscapes composed of small wetlands, where few nesting wetlands occurred and potential food sources were spread over large distances, were not widely used by black terns. Landscape-level measurements related to black tern occurrence extended past relationships between wetlands into the surrounding matrix. Black terns were more likely to occur in landscapes where grasslands had not been tilled for agricultural production. Our findings represent empirical evidence that characteristics of entire landscapes, rather than individual patches, must be quantified to assess habitat suitability for wide-ranging species that use resources over large areas.     

红壤干旱过程中剖面水分特征与土层干旱指标

农田水分管理以及产量评估都需要对土壤作物受旱状况定量化和指标化。干旱强度和干旱程度结合才能完整地描述土壤作物干旱状况,土壤干旱强度I是土壤剖面失水速率的函数,干旱影响逐渐累积并增强就构成干旱程度D,据此提出了包含I和D二个指数的土层干旱指标表达模式。通过红壤小区种植玉米并在抽穗期开始设置连续干旱12～36 d等6个不同的处理,研究了红壤干旱过程中剖面水分特征和干旱指标。结果表明：供试红壤干旱过程中剖面40 cm以下含水率下降幅度很小,玉米主要利用了0～40 cm土层的水分,监测30～40 cm土层含水率的变化情况可以指示玉米受到干旱胁迫的程度。连续干旱25 d后40 cm以下土层含水率明显降低,玉米产量也显著下降,此时0～60 cm土层和30～40 cm土层的干旱程度D均为0.55,可用此指标作为灌溉的依据。