京津冀地区自然植被保护与自然保护区布局研究

京津冀一体化, 协同发展已上升为国家战略, 着力扩大环境容量生态空间, 加强生态环境保护合作是京津冀协同发展的具体要求, 而促进该区域自然植被的保护和自然保护区布局的优化是生态环境保护的重要组成。文章以京津冀地区的自然保护区基础信息、植被类型信息以及地形地貌信息为基础数据, 分析了京津冀地区自然保护区的基本特征, 利用GIS 的叠加分析功能, 研究了京津冀地区的植被保护现状与保护空缺, 分析了自然保护区分布与海拔梯度的关系, 植被分布与海拔梯度的关系。结果表明: 京津冀地区的自然保护区以森林类型为主, 其次是内陆湿地类型; 京津冀地区的主要森林植被类型得到了较好的保护, 草原草甸植被的保护需要加强; 自然保护区的分布和植被类型的分布在海拔梯度上具有较高的一致性, 在海拔800-1200 m 内分布的自然保护区数量最多, 也是森林植被类型数量与分布面积最多的海拔段。因此, 加强河北省西北部的草原草甸生态系统自然保护区的建设, 有助于弥补京津冀地区自然植被保护的不足; 加强河北省涞源县-阜平县, 井陉县-赞皇县等西部太行山海拔800-1200 m 范围内自然保护区的建设, 有助于保护暖温带落叶阔叶林生态系统, 构建由太行山和燕山森林类型自然保护区组成的生态屏障。     

我国国家级自然保护区数量特征研究

研究我国国家级自然保护区数量特征对加强保护区建设和管理具有重要意义。本文通过资料收集,采用方差分析、多元比较、相关分析等数理统计方法,分析了我国国家级自然保护区数量和面积的分布格局、各类型保护区各功能区划面积比例及功能区面积与物种的关系等数量特征。结果表明,我国国家级自然保护区数量上以森林生态系统类型最多;面积上为荒漠生态系统类型最大;面积分布格局呈现从西向东及从北向南逐渐减少的趋势。方差分析表明不同类型国家级自然保护区3个功能区面积所占其总面积的比例之间差异不显著;相关分析表明在以物种为保护对象的保护区中,其总面积、各功能区面积与物种数量、动植物种类的相关性显著。该研究相关结果为我国自然保护区的建设与管理提供一定的参考依据。     

广东林业生态省建设与红树林保护

广东是我国红树林分布最多的省份之一,有红树植物17科31种,红树林湿地面积21 438.3hm²,主要分布在粤西,其次是珠江三角洲地区。红树林具有防灾减灾、净化环境、调节区域小气候、保护生物多样性等重要生态功能。在广东林业生态省建设中,保护和发展红树林被列为八大林业生态工程之一。本文对红树林的生态功能进行了具体分析;阐述了广东红树林资源分布现状、红树林在广东林业生态省建设中的作用以及保护、发展状况;指出目前红树林还面临围海造田、围海养殖、沿海城市化、废水污染等威胁,红树林保护任务艰巨;并就加强红树林保护提出建议。     

我国西南地区物种多样性保护效果

通过选取比较重要的40处自然保护区,对我国西南地区自然保护区的物种保护效果进行了研究,以期对自然保护区的规划与管理提供一些依据.研究结果如下:通过回归分析发现,随着自然保护区的增加,受保护的野生动物(植物)物种总数呈现对数增长的趋势,由此得到西南地区受保护的野生脊椎动物物种总数为2426种,为我国野生脊椎动物物种总数6347种的38.2%;西南地区受保护的野生高等植物物种总数为20965种,是我国野生高等植物物种总数30000多种的近70%.我国西南地区在自然保护区的总面积为150万hm2以下时,受保护的动物(植物)物种总数与自然保护区的总面积呈现显著直线正相关关系,当总面积大于150万hm2时,受保护的动物(植物)物种总数增加不明显,因此要增建扩建自然保护区,应从保护珍稀濒危野生物种的角度考虑.在我国西南地区自然保护区中,得到保护的国家重点保护动物共119种,是国家重点保护动物总数的46.3%,其中保护的1级保护动物42种,保护比例为43.8%,保护的2级保护动物77种,保护比例为47.8%;得到保护的国家重点保护植物共138种,为国家重点保护植物总数的54.3%,其中保护的1级保护植物29种,保护比例为56.9%,保护的2级保护植物109种,保护比例为53.7%.     

国家生态保护重要区域植被长势遥感监测评估

国家生态保护重要区域植被长势对于维持区域生态系统结构和功能的稳定性至关重要.以国家重点生态功能区、国家重要生态功能区、国家生物多样性保护优先区和国家级自然保护区等四类生态保护重要区域为研究区,选取年累积NDVI作为指示因子,监测评估了1998-2007年间国家生态保护重要区域的植被长势特征.结果表明:(1)国家生态保护重要区域总面积为536.59万km2,占全国陆地国土面积的55.89％.国家生物多样性保护优先区与国家重点生态功能区、国家重要生态功能区的重叠面积较大,分别占到相应生态功能区总面积的53.36％和50.20％.国家级自然保护区与其他三种类型区域的空间叠加关系较好,尤其与国家重点生态功能区,重叠面积占国家级自然保护区总面积的75.10％.国家重点生态功能区和国家重要生态功能区的重叠面积分别占各自面积的63.73％和39.15％.(2)对于植被长势总体状况,国家生态保护重要区域中东部的植被状况好于西部.植被状况较差的区域面积为10.59％,植被状况一般的区域面积为29.59％,植被状况好的区域面积为23.44％,植被状况较好的区域面积为36.39％.国家级自然保护区和生物多样性保护优优先区的植被状况好于国家重要生态功能区和国家重点生态功能区.国家级自然保护区的空间分布差异最大.(3)对于植被长势变化趋势,国家生态保护重要区域的植被状况整体呈现出变好趋势.62.39％区域面积的植被状况较为稳定,22.69％区域面积的植被状况呈现出变好趋势,14.93％区域面积的植被状况呈现出变差趋势.国家重要生态功能区的植被变好趋势最为明显,其次为国家生物多样性保护优先区.国家生物多样性保护优先区的植被变化趋势空间差异最大,国家级自然保护区的植被变化趋势空间差异最小.     

基于MaxEnt模型的广东省红树林潜在适生区和保护空缺分析

红树林是分布在热带、亚热带海岸潮间带的木本群落,具有重要的生态功能。广东省是中国红树林分布面积最大的省份,在红树林保护方面具有重要地位。最大熵(MaxEnt)模型是以生态位理论为基础的物种分布模型,目前被广泛应用于物种潜在适生区预测。本研究应用MaxEnt模型,根据广东省红树林分布数据和环境变量数据,预测了该省红树林的潜在适生区分布,分析了影响红树林分布的关键环境变量及其适生区间,识别了广东省红树林保护与修复空缺区域。结果表明,在气候、地形、底质类型、海表盐度、海表温度5组变量中,影响广东省红树林分布的最主要环境变量为气温、海表温度和降水。关键环境变量的最佳适生区间为年平均温度22.37～23.58℃、最冷季平均海表温度23.15～23.34℃、年平均降水量1647.14～1809.61 mm、最干月降水量23.6～27.2 mm。广东省红树林的高适生区域主要集中于珠江口-大亚湾沿岸和雷州半岛-阳江沿岸,保护空缺主要出现在阳江港、镇海湾、珠江口、红海湾等地。本研究结果可为今后广东省红树林保护和修复行动与规划的空间布局提供科学依据。     

全球红树林时空变化及演变趋势

红树林是全球重要的生态系统,了解红树林的时空变化特征及演变趋势对开展红树林的保护、恢复及可持续管理具有重要意义。基于谷歌地球工程(Google Earth Engine,GEE)云平台,利用全球红树林分布数据和陆地卫星(Landsat)系列光学影像特征指数数据,结合Theil-Sen中值趋势分析、Mann-Kendall检验、Hurst指数等方法,分析了全球红树林的时空分布特征、时空演变趋势及其可持续特征。结果表明:1990-2020年全球红树林面积呈先下降后上升趋势,总面积减少52174.18km²,年平均流失率达1.2%,红树林面积减少最多的地区为东南亚,其次为澳大利亚和新西兰、南美洲和东南非洲;红树林呈退化趋势变化的面积(81.44%)明显多于改善区域的面积(17.43%),其中澳大利亚和新西兰的退化趋势最为明显;2015-2020年全球红树林变化趋势有所改善,有73.85%的区域在未来是可持续的,持续改善区域面积(38.58%)大于持续退化区域面积(33.06%),且改善区域的可持续性明显高于不可持续性,表明2020年之后全球红树林整体上呈改善趋势变化。全球红树林时空变化特征和演变模式,可为生物多样性保护、沿海经济发展、生态环境的可持续改善提供重要支撑,对评估联合国2030可持续发展目标实现的状况具有重要影响。     

生态系统保护现状及保护等级评估——以江西省为例

基于生态系统的保护是防止生物多样性丧失的重要手段,已成为保护生物学研究的热点。对生态系统保护等级进行划分,确定局域、区域和全球尺度上生态系统保护的优先性,可为制定生态系统保护方案提供重要依据。目前,生态系统保护等级划分的常用指标包括面积流失率、幅度和代表性。以江西省生态系统为例,基于20世纪80年代的江西省植被图、生态系统图、2010年土地利用图和自然保护区图,在GIS环境下进行图层叠加运算和重分类,再进行定量评估和归一化,将江西省生态系统划分为极重要、重要和一般3个级别。结果表明:过去的30年间江西省自然生态系统面积共减少了82613.83km2,减少率超过了60%。全省的37个自然生态系统类型中有19个类型建有国家级自然保护区,但得到保护的面积比例较低。森林生态系统中极重要、重要和一般生态系统类型分别占省国土面积的16.7374%、5.5310%和3.8242%,受国家级自然保护区保护的比例分别为0.51%、3.73%和5.76%;灌丛生态系统中极重要、重要和一般生态系统类型分别占0.0975%、0.9335%和0.0100%,保护比例分别为1.72%、0.17%和0.70%;草地生态系统中极重要、重要和一般生态系统类型分别占0.2647%、0.0005%和0.1064%,保护比例分别为0.21%、0.00%和3.49%;湿地生态系统中极重要、重要和一般生态系统类型分别占0.3532%、0.0345%和1.5650%,保护比例分别为1.87%、0.00%和18.01%。从各级生态系统空间分布来看,极重要生态系统分布范围最广,主要分布在江西省的东南部和西北部;重要生态系统主要分布在西北部和东北部;一般生态系统分布范围最小,主要分布在北部。中部地区的自然生态系统多数由于经济发展而退变为农田、城市等人工生态系统。结合江西省生态系统现状,将极重要的生态系统作为重点保护范围,因而占江西省国土面积17.46%的生态系统应该得到优先保护。这一结果为有效地开展生态系统管理,制定有针对性的生态系统的保护规划具有重要参考价值。     

我国哺乳动物就地保护状况评估

自然保护区被公认为是生物多样性就地保护最有效的方式之一。基于全国自然保护区基础调查,通过分析我国自然保护区内野生哺乳动物种群数量的分布情况,在全国尺度上对自然保护区内591种哺乳动物的就地保护状况进行了评估。根据评价指标体系,将我国哺乳动物就地保护水平划分为"有效保护""较好保护""一般保护""较少保护""未受保护""保护状况不明""未予评价"等7个等级。结果表明,除未予评价的35种外,其余参评的556种物种中,共有534种在自然保护区内得到一定程度的保护,占总数的90.36%。其中有效保护、较好保护、一般保护、较少保护的物种分别有145、60、100种和229种,分别占总数的24.53%、10.15%、16.92%和38.75%。此外,有22种物种保护状况不明。针对不同保护体系中的哺乳动物的就地保护状况进行评价,研究共涉及国家重点保护野生动物140种和列入中国物种红色名录的427种,其中分别有109种和409种在保护区内得到不同程度的保护。总体来说,虽然有90.36%的哺乳动物在保护区内得到不同程度的保护,但保护状况良好(包括有效保护和较好保护)的比例明显较低,保护状况仍然不容乐观,保护力度有待加强;对于保护状况不明的物种,有必要对保护区开展更加全面、细致的科学考察以进一步确定其保护现状;对于确未受到自然保护区就地保护的物种,需要通过完善保护区网络,将其纳入自然保护体系之中。     

华北地区国家级自然保护区对药用维管植物的保护状况

开展已有就地保护体系对生物多样性的保护现状评估有利于科学指导下一步保护规划工作.本研究收集华北地区46个国家级自然保护区的科学考察报告、多样性研究报告及其他相关文献资料,整理构建了华北地区药用维管植物保护名录数据库,并利用此数据库分析了该地区药用维管植物的就地保护状况.结果发现:华北地区国家级自然保护区不同程度保护了2 364种药用维管植物,隶属于165科800属;其中,1710个物种(占总数的72.34％)受保护程度一般,分布的保护区数量少于10个,仅62个物种(占总数的2.62％)受到有效保护,分布的保护区数量大于30个;不同保护类型的保护区对药用维管植物所发挥的保护作用不同,森林生态类型保护区发挥的保护作用最大,保护了华北地区89.04％(2 105/2 364种)的药用维管植物.研究认为华北地区国家级自然保护区对该地区药用维管植物的就地保护发挥了重要作用,但现有保护状况可进一步完善,尤其应该重视森林生态类型保护区的建设工作以及珍稀濒危药用植物的保护规划.     

Local Mangrove Planting in the Philippines: Are Fisherfolk and Fishpond Owners Effective Restorationists?

Local fisherfolk and fishpond owners have been practicing “restoration” of mangrove forests in some parts of the Philippines for decades, well before governments and non‐government organizations began to promote the activity as a conservation tool. This paper examines ecological characteristics of these mangrove plantations and compares them to natural mangroves in the same areas. Mangrove planters were interviewed and plantation and natural mangrove forests were surveyed to measure forest structure, composition and regeneration. Compared with natural forests, mangrove plantations were characterized by high densities of small stems, shorter and narrower canopies, and fewer species. For both economic and ecological reasons, the vast majority of people dispersed and planted only Rhizophora mucronata/stylosa and, furthermore, they often thinned other species out of planted areas. There was remarkably little subsequent recruitment of other, nonplanted mangrove species into plantations up to 50 and 60 years of age. This pattern held across a diversity of sites, including plantations that had not been selectively cut or weeded. Important ecological and economic benefits result from local mangrove planting, but catalyzing diverse forest regeneration—at least in the short to medium term—is not one of them. The lesson: if you want to restore diverse mangrove forests, you have to plant diverse mangrove forests.     

The distribution and state of mangroves along the coast of Transkei,Eastern Cape Province,South Africa

The mangrove communities along the coastline of the former Transkei, now part of the Eastern Cape Province, have not been looked at in detail since Ward and Steinkes survey in 1982. Mangroves previously occurred in 17 estuaries but were now found in only 14 of the 76 estuaries visited, with a complete loss of mangroves evident in the Mnyameni, Mzimvubu and Bulungula estuaries amounting to 7.5 ha. Total mangrove loss amounted to 17.6 ha which represents a 6.5% loss over 17 years or 1.04 ha per annum. Tree cover had increased by 16.15 ha in eight other estuaries. This increase could be attributed to the inaccessibility of mangrove stands or to protection afforded by provincial nature reserves and hotel resorts. No new mangrove stands were recorded, although Steinke (pers. comm.) has recently recorded mangroves along the north bank of the Kei River. There has been little change in mangrove species composition in the different estuaries over the past 17 years. Total mangrove loss amounted to 17.6 ha which represents a 6.5% loss over 17 years or 1.04 ha per annum and the species recorded included Avicennia marina, Bruguiera gymnorhiza and Rhizophora mucronata. The mangrove fern Acrostichum aureum L. was recorded for the first time in the Mkozi estuary. Tree density for all estuaries was between 10 and 2594 trees ha^–1. The Mngazana and Mntafufu estuaries had the highest tree densities of 2594 and 1402 trees ha^–1 respectively, typical of riverine mangrove forests. Fringe mangroves were evident in most other systems. Removal of trees for wood has the greatest impact on mangrove cover. Fringe mangrove stands are particularly accessible to harvesters. Only 6% of the current area of trees is afforded some protection in conservation areas. The Mdumbi, Mzamba and Kobonqaba estuaries receive no conservation protection and harvesting has resulted in more than 50% of the trees being removed. The density of dead tree stumps was greater than the number of living trees and no seedlings or juvenile trees were found. Further removal of mangroves within the estuaries south of the Mzimvubu River is expected in the fringe mangroves, as most are unprotected and easily accessible.     

Small Gap Creation in Belizean Mangrove Forests by a Wood–Boring Insect1

We investigated the role of wood-boring insects in the creation of light gaps within mangrove forests. We compared the frequency of gaps caused by wood borers to other gap-forming processes and characterized the physical attributes of light gaps in mangrove forests on small islands in Belize. Methods of quantifying light gaps included aerial photography, ground surveys, and experimental plots. Small light gaps (≤12 m²) were very common in Rhizophom mangle fringe, comprising almost 22 percent of these forests. Rhizophora mangle gaps were smaller than gaps in Avicennia germinans forests. In R. mangle forests, gaps were caused by branch death, and in A. germinans forests, gaps were caused primarily by downed trees. More than 91 percent of the gap-forming branches and boles in the R. mangle fringe were killed by a wood-boring cerambycid beetle, Elaphidion mimeticum, indicating that it is the major cause of small-scale disturbances in these forests. No trees or branches in the A. germinans forest were attacked by this beetle. In R. mangle forests, small gaps had significantly higher light levels and soil temperatures than areas under the closed canopy; however, soil conditions for sulfide concentrations, porewater salinity, and redox potentials were similar in small gaps and under the closed canopy. Survival of R. mangle, A. germinans, and Laguncularia racemosa seedlings was also higher inside these small gaps, indicating their importance in regeneration of mangrove forests. Feeding by wood borers is thus an important type of indirect herbivory in mangrove forests, with a critical role in ecological processes such as gap dynamics.     

Simulating harvesting scenarios towards the sustainable use of mangrove forest plantations

Mangrove forests appear among the most productive ecosystems on earth and provide important goods and services to tropical coastal populations. Thirty-five percent of mangrove forest areas have been lost worldwide in the last two decades. Management measures could be an option to combine human use and conservation of mangroves. These measures can be improved if their impacts are assessed before they are performed. By doing so, the best management option out of a set of all potential options can be selected in advance. The mangrove model—KiWi—has been proven to be suitable for analyzing mangrove forest dynamics in the neotropics. Here, the model was applied to mangrove management scenarios. For this, the model was parameterized to Rhizophora apiculata, one of the most common mangrove species planted in Asia for timber production. It is thus the first simulation model describing Asian mangrove plantations. The recently developed Pattern Oriented Modelling approach was used to find those parameters fitting best density patterns and dbh (diameter at breast height) size classes reported in literature. The results demonstrated that the KiWi model was able to: (1) reproduce the growth patterns of a mono-specific plantation of R. apiculata in terms of forest density and size class distribution and (2) can provide criteria for the selection of a thinning strategy within a harvesting cycle.     

Effects of experimental sedimentation on the phenological dynamics and leaf traits of replanted mangroves at Gazi bay,Kenya

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Low Primate Diversity and Abundance in Northern Amazonia and its Implications for Conservation

Large areas of the Rio Negro basin in Amazonia are covered by continuous tracts of tropical forest, but have few primate species. This is anomalous considering the general relationship between area and number of species. One possibility is that much of the forest is unsuitable habitat for most primates and the area of suitable habitat is much less than the forested area. This has important consequences for the design of reserves and predictions of the consequences of climate change, which tend to be based on broad categories based on satellite images, and not on information of species distributions within those broad categories. The study was conducted through diurnal and nocturnal line‐transect surveys in the Biodiversity Research Program 25‐km² permanent grid in Viruá National Park, which has vegetation associations typical of much of northern Amazonia. The highest primate diversity and abundances occurred in tall terra firme forests (58%), whereas inundated forests and scrublands, which cover 42 percent of the survey grid and 90.8 percent of the Viruá National Park, have virtually no primates. This suggests that parks and reserves in northwestern Amazonia will have to be very large to maintain viable populations of most primates and their ecological interactions, and that very broad habitat categories are not sufficient to make predictions about actual and future suitability of areas for primate conservation.     

京津冀地区物种多样性保护优先区识别研究

着力扩大环境容量和生态空间,加强跨区环境保护合作,是落实京津冀一体化协同发展国家战略的重要内容。摸清京津冀地区的生物多样性分布格局,可为国家公园布局、生态环境保护工程的实施提供依据。根据"自然保护区生物多样性保护价值评估技术规程（LY/T 2649-2016）",基于京津冀地区自然保护区的综合科学考察报告,评估了京津冀地区典型自然保护区的物种多样性保护价值,并以其为因变量,以自然保护区的综合地形地貌为自变量,构建多元回归模型,同时以自然保护区的平均面积为基准,利用ArcGIS的创建"渔网"功能,将京津冀地区划分为1638个网格单元,利用构建的多元回归模型评估了这些网格单元的保护价值。结果表明：京津冀地区国家级自然保护区的保护价值平均得分为204分,比参评的全部35个自然保护区的平均分高40分;在省级自然保护区中也存在一些得分较高的自然保护区,如,唐海湿地自然保护区和河北南大港自然保护区,且超过了参评国家级自然保护区保护价值得分的平均值。京津冀地区的物种多样性保护优先区总面积为36791.35 km²,占京津冀地区总面积的16.94%,其中一级保护优先区面积4611.57 km²,二级保护优先区面积16045.79 km²,三级保护优先区面积16133.98 km²。这些区域主要分布在河北省和北京市的北部地区,区域内绝大部分以森林植被和灌丛植被为主。建议在未来的国家公园布局、生态环境保护工程布局中重点考虑这些地区。     

Ecological role of mountain ridges in and around gwangneung royal tomb forest in central Korea

We assessed the ecological structure and function of mountain ridges connected to a reserve area, Gwangneung Royal Tomb Forest (GRTF), in central Korea. This site has been strictly preserved since the 15th century. Our objectives were to 1 ) investigate the interactions between and the influence of a protected old-growth forest on its surrounding forests, and 2) suggest management strategies for forests outside that reserve area. Three ridges were surveyed and divided into two categories — A and B ridges covered with secondary forests connected to GRTF, and the C ridge, covered with primary forests and plantations within GRTF (from core zone to managed zone). The ridge forests had a characteristic lobe shape. We found no significant decline in species richness (peninsular effect) with distance from GRTF for any tree-layer or herbaceous-layer species on Ridges A or B. However, when only the species that appeared in primary forests on the C ridge were considered, the richness of tree- and herbaceous-layer species was significantly decreased there. This meant that the neighboring forests of GRTF could serve as a buffer zone. Differences were obvious between the two categorized forests in their species composition, species richness, basal area, and regeneration patterns. DCA ordination of quadrats on Ridges A and B showed that Axis 1 was significantly correlated with distance from GRTF, indicating that this protected area affects regeneration within neighboring forests. Thus, reserves are important not only to the conservation of biodiversity, but also to the ecological management of surrounding forests.     

Structure of a unique inland mangrove forest assemblage in fossil lagoons on the Caribbean Coast of Mexico

Scrub mangrove wetlands colonize the intertidal zone of fossil lagoons located in carbonate continental margins along the Yucatan Peninsula of Mexico. These unique ecological types were investigated in October, 1994, by locating transects in several mangrove forests along the Caribbean coast of the peninsula. Four species of mangrove occurred at these sites including Rhizophora mangle, Avicennia germinans, Laguncularia racemosa, Conocarpus erecta. This is one of the first examples of a species rich scrub forest. The mangroves fell into three height categories: short scrub less than 1.5 m, tall scrub to 3.0 m, and basin forests between 4.5 and 6 m. Average height, diameter (dbh), basal area, and complexity index generally increased from short scrub to basin forests. Basal area, ranged from 0.16 m² ha^–1 in a short scrub forest intermixed with Cladium jamaicense to 12.9 m² ha^–1 in a basin forest. Density ranged from 1520 trees ha^–1 to over 25,000 trees ha^–1 in a short scrub forest dominated by R. mangle. The complexity index ranged from 0.01 to 8.3. Height, dbh, basal area, and complexity index were positively related. A number of trees were growing as sprouts from larger downed trunks, suggesting that hurricanes, such as Gilbert that occurred in 1988, are important in controlling the structure of these forests. These forests appear isolated from the sea, but are influenced by groundwater exchange occurring at the land-margin zone.