582 resultados para upland steppes


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Wales is important for fish conservation in Britain. In much of Wales, atchments are small (median catchment size = 121 km2 ) and frequently eparated by areas of upland (> 600 m altitude), creating a highly agmented habitat for freshwater fish. Consequently, fish communities onsist mainly of diadromous species such as trout, eel and sticklebacks hat were able to recolonise freshwaters via the sea following the retreat of he ice sheets ca. 10 000 years BP. This review aims to (i) update the former work of Lyle and Maitland, taking into account new National Nature Reserves (NNRs)and additional data collected since 1991; (ii) assess the different fish communities represented on Welsh NNRs with respect to their naturalness; (iii) examine the use of NNRs for angling; (iv) evaluate opportunities for expanding the NNR series to conserve fish populations of conservation importance. The paper provides a table of freshwater fish occurrence by water body in Wales.

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Pisidium obtusale in the neighbourhood of Borka occurs in deep pools on upland bogs. The majority of water-bodies where this mollusc lives are temporary. Their bottoms are covered with sedges, and sometimes mosses occur. Evidently there is a marked attraction of P. obtusale to places overgrown by willow. In pools remote from scrub or woody vegetation it does not appear. Temporary water-bodies fill up with melt water in the middle or the end of April and finally dry up at the end of July or the beginning of August. Observations on the life cycle of P. obtusale started on 21 April 1966, following on the filling-up of the water-body by melt water. The findings of the study are presented in this paper.

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Scour and deposition have been measured in two small cobble-bedded upland streams, for two years. Grids of scour chains were inserted in the bed and relocated after the passage of individual hydrographs. Scour, fill and the area of the bed affected by these processes were recorded. The relationship between mean scour or fill and maximum scour or fill is assessed. In addition, the relationship between the depth of scour and the sediment transport rate as bedload is discussed briefly.

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There is no evidence of an increase in the acidity (lower pH or alkalinity) of water-bodies in the Lake District over the last 50 years. Brown trout occur in acid streams and upland tarns where pH is 4.5-5.2 throughout the year. Their occurrence in such waters in Britain and Ireland has been known for most of this century and there is no previous evidence of harmful effects on salmonid fisheries, though numbers of fish are naturally low. However, many benthic invertebrates that are common in hill-streams where pH is above 5.7 do not occur in more acid streams. This phenomenon occurs in the headwaters of several western rivers in Cumbria. It is not a recent response to "acid rain". Harmful effects of pH are undoubtedly more pronounced in waters that are poor in other dissolved ions. Low concentrations of sodium, potassium, calcium and chloride are especially important and may limit the distributions of some aquatic animals even where pH is above 5.7. The concentration of sulphate ions is usually relatively high but this is not important to the fauna; concentrations are at least two times higher in productive alkaline water-bodies than they are in unproductive acid waters.

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The main British salmonid species spawn in clean gravel in streams and rivers, many of them in the upland areas of Britain. The earliest stages of the life cycle (eggs and alevins) spend some months within the gravel of the river bed. During this period their survival rate can be strongly influenced by flow regime and by related phenomena such as movement of coarse river bed material, changes in water level and the deposition of silt. In recent years human influence upon the flow regimes of upland water courses and upon the sediment inputs to them has increased. In order to conserve and, if possible, enhance the populations of salmonid fishes a deeper understanding of the interrelationships between survival of young salmonids and flow-related phenomena is needed. The acquisition of appropriate information is the main aim of the present project, which included: Studies on silt movement and the infilling of gravel voids by fine sediments, together with initial studies on the relationship between intragravel oxygen supply rate and the survival of intragravel stages of salmonids; studies in the general field of egg washout. The latter investigated the physical background to gravel bed disruption, the examination of the physical characteristics of sites chosen for redds, dimensions of redds and burial depth of eggs relative to the size of the fish constructing the redd and a series of smaller studies on other aspects of egg washout.

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Rainbow trout is one of the important exotic species that is well established in the upland waters of India. This paper presents the historical background of its introduction and the present status of the fish in the streams of he Nilgiri peninsula of India. The rainbow trout inhabits natural reservoirs and streams of the region as a self-recruiting population. The growth rate is reported to be relatively low and conflicting views about its taxonomic status have been reported. Successful crossbreeding of the Nilgiri rainbow trout with trout stocks from the Indian State of Himachal Pradesh has indicated the scope for utilizing cryopreserved milt as a mode of introducing new genetic material into the Nilgiri rainbow trout population. This paper outlines the requirement of ecological and genetic data to develop a strategy for management and reintroduction fresh stocks.

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No presente estudo foi avaliada (i) a estrutura das assembleias de peixes de igarapés de terra-firme ao longo do contínuo fluvial do rio Machado, na bacia do rio Amazonas, (ii) os efeitos de alterações ambientais sobre as assembleias de peixes de igarapés através de comparações entre áreas íntegras (em uma Unidade de conservação) e alteradas por ação antrópica na bacia hidrográfica do rio Machado, e (iii) a organização espacial das assembleias de peixes de tributários de baixa ordem na bacia do rio Machado através da avaliação dos padrões de co-ocorrência das espécies, identificando os possíveis fatores estruturadores dessas assembleias e através de uma Análise de Parcimônia de Endemismo (PAE). As amostragens foram realizadas entre os meses de agosto e setembro de 2011, junho e agosto de 2012 e julho de 2013, totalizando 81 igarapés. Os peixes foram coletados durante uma hora em um trecho de 80 metros, com o auxilio de uma rede de mão (picaré) e um puçá. Para o capítulo 1, um maior número de indivíduos e espécies foram encontradas no trecho baixo quando comparado o trecho alto da bacia. Todavia, somente foram encontradas diferenças significativas entre o trecho alto e os trechos médio e baixo. Assim, rejeitamos nossa hipótese de diferenças entre os trechos analisados, onde esperávamos que a riqueza e abundância de espécies de igarapés aumentaria no gradiente longitudinal cabeceira-foz do rio Machado. Contudo, apesar da não confirmação da hipótese, um padrão de adição e substituição de espécies foi observado do trecho alto para o médio, e um padrão de substituição de espécies foi observado do trecho médio para o baixo. Referente ao capítulo 2, apontamos que apesar da área desflorestada não apresentar diferenças marcantes na riqueza de espécies e abundância, quando comparada com a área com igarapés conservados, esta (área desflorestada) apresentou elevada similaridade a nível composicional entre os igarapés amostrados (menor diversidade beta), diferentemente dos igarapés localizados na Rebio, que apresentaram maior número de espécies com hábitos mais especializados. Igarapés desflorestados apresentaram homogeneização da sua ictiofauna em comparação com igarapés providos de mata ripária, refletindo a maior homogeneização estrutural encontrada em igarapés com baixo percentual de cobertura vegetal. Dessa forma, a retirada da cobertura vegetal em igarapés com comunidades mais diversificads e especializadas, como os da Rebio Jaru, promoveria a homogeneização das espécies acarretando a perda destas, assim como a substituição destas por espécies tolerantes a condições ambientais comuns a ambientes alterados. Para o capítulo 3, embora não tenhamos encontrado áreas de endemismo na bacia analisada, apontamos que a influência da estrutura física dos igarapés sobre a composição de espécies é o principal fator modulador da estruturação da assembleia de peixes. Todavia, tal fator não se aplica a estruturação da assembleia baseada na coocorrência de espécies, haja vista que, a análise de toda a bacia com diferentes níveis de uso de solo, apresentou um padrão organizacional não aleatório

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This is the episodic variations in stream water chemistry associated with acid rainfall and run-off and the effect on aquatic ecosystems, with particular reference to fish populations in North West England produced by the North West Water Authority in 1985. This report looks at the biological, physical and chemical information collected over a five year period from over 100 sites on upland streams in the North West Region of which drained rocks of low buffering capacity. In both Lake District and South Pennine sites striking differences were found between the composition of invertebrate communities inhabiting acid-stressed and less acid-stressed streams. Electric fishing surveys showed that acidic streams (geometric mean pH <5.5) generally had abnormally low densities of salmonids ( < 0 .2m2) and that 0+ fish were very few or absent. The latter indicates recruitment failure. Salmon were more sensitive than trout to low pH.

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Estuaries provide critical nursery habitat for many commercially and recreationally important fish and shellfish species. These productive, diverse ecosystems are particularly vulnerable to pollution because they serve as repositories for non–point-source contaminants from upland sources, such as pesticide runoff. Atrazine, among the most widely used pesticides in the United States, has also been one of the most extensively studied. There has not, however, been a specific assessment of atrazine in marine and estuarine ecosystems. This document characterizes the presence and transformation of atrazine in coastal waters, and the effects of atrazine on marine organisms. Review of marine and estuarine monitoring data indicate that atrazine is chronically present in U.S. coastal waters at relatively low concentrations. The concentrations detected have typically been below acute biological effects levels, and below the U.S. EPA proposed water quality criteria for atrazine. While direct risk of atrazine impacts are low, uncertainty remains regarding the effects of long-term low levels of atrazine in mixture with other contaminants. It is recommended that best management practices, such as the use of vegetative buffers and public education about pesticide use, be encouraged in the coastal zone to minimize runoff of atrazine into marine and estuarine waters.

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This report describes the creation and assessment of benthic habitat maps for shallow-water (<30m) marine environments of the Guánica/Parguera and Finca Belvedere Natural Reserve in southwest Puerto Rico. The objective was to provide spatially-explicit information on the habitat types, biological cover and live coral cover of the region’s coral reef ecosystem. These fine-scale habitat maps, generated by interpretation of 2010 satellite imagery, provide an update to NOAA’s previous digital maps of the U.S. Caribbean (Kendall et al., 2001) for these areas. Updated shallow-water benthic habitat maps for the Guánica/Parguera region are timely in light of ongoing restoration efforts in the Guánica Bay watershed. The bay is served directly by one river, the Rio Loco, which flows intermittently and more frequently during the rainy season. The watershed has gone through a series of manipulations and alterations in past decades, mainly associated with agricultural practices, including irrigation systems, in the upper watershed. The Guánica Lagoon, previously situated to the north of the bay, was historically the largest freshwater lagoon in Puerto Rico and served as a natural filter and sediment sink prior to the discharge of the Rio Loco into the Bay. Following alterations by the Southwest Water Project in the 1950s, the Lagoon’s adjacent wetland system was ditched and drained; no longer filtering and trapping sediment from the Rio Loco. Land use in the Guánica Bay/Rio Loco watershed has also gone through several changes (CWP, 2008). Similar to much of Puerto Rico, the area was largely deforested for sugar cane cultivation in the 1800s, although reforestation of some areas occurred following the cessation of sugar cane production (Warne et al., 2005). The northern area of the watershed is generally mountainous and is characterized by a mix of forested and agricultural lands, particularly coffee plantations. Closer to the coast, the Lajas Valley Agricultural Reserve extends north of Guánica Bay to the southwest corner of the island. The land use practices and watershed changes outlined above have resulted in large amounts of sediment being distributed in the Rio Loco river valley (CWP, 2008). Storm events and seasonal flooding also transport large amounts of sediment to the coastal waters. The threats of upstream watershed practices to coral reefs and the nearshore marine environment have been gaining recognition. Guánica Bay, and the adjacent marine waters, has been identified as a “management priority area” by NOAA’s Coral Reef Conservation Program (CRCP, 2012). In a recent Guánica Bay watershed management plan, several critical issues were outlined in regards to land-based sources of pollution (LBSP; CWP, 2008). These include: upland erosion from coffee agriculture, filling of reservoirs with sediment, in-stream channel erosion, loss of historical Guánica lagoon, legacy contaminants and sewage treatment (CWP, 2008). The plan recommended several management actions that could be taken to reduce impacts of LBSP, which form the basis of Guánica watershed restoration efforts.

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A study was conducted, in association with the Alabama and Mississippi National Estuarine Research Reserves (NERRs) in the Gulf of Mexico (GoM) as well as the Georgia, South Carolina, and North Carolina NERRs in the Southeast (SE), to evaluate the impacts of coastal development on tidal creek sentinel habitats, including potential impacts to human health and well-being. Uplands associated with Southeast and Gulf of Mexico tidal creeks, and the salt marshes they drain, are popular locations for building homes, resorts, and recreational facilities because of the high quality of life and mild climate associated with these environments. Tidal creeks form part of the estuarine ecosystem characterized by high biological productivity, great ecological value, complex environmental gradients, and numerous interconnected processes. This research combined a watershed-level study integrating ecological, public health and human dimension attributes with watershed-level land cover data. The approach used for this research was based upon a comparative watershed and ecosystem approach that sampled tidal creek networks draining developed watersheds (e.g., suburban, urban, and industrial) as well as undeveloped sites (Holland et al. 2004, Sanger et al. 2008). The primary objective of this work was to define the relationships between coastal development with its concomitant land cover changes, and non-point source pollution loading and the ecological and human health and wellbeing status of tidal creek ecosystems. Nineteen tidal creek systems, located along the Southeastern United States coast from southern North Carolina to southern Georgia, and five Gulf of Mexico systems from Alabama and Mississippi were sampled during summer (June-August) 2005, 2006 (SE) and 2008 (GoM). Within each system, creeks were divided into two primary segments based upon tidal zoning: intertidal (i.e., shallow, narrow headwater sections) and subtidal (i.e., deeper and wider sections), and watersheds were delineated for each segment. In total, we report findings on 29 intertidal and 24 subtidal creeks. Indicators sampled throughout each creek included water quality (e.g., dissolved oxygen, salinity, nutrients, chlorophyll-a levels), sediment quality (e.g., characteristics, contaminant levels including emerging contaminants), pathogen and viral indicators (e.g., fecal coliform, enterococci, F+ coliphages, F- coliphages), and abundance and tissue contamination of biological resources (e.g., macrobenthic and nektonic communities, shellfish tissue contaminants). Tidal creeks have been identified as a sentinel habitat to assess the impacts of coastal development on estuarine areas in the southeastern US. A conceptual model for tidal creeks in the southeastern US identifies that human alterations (stressors) of upland in a watershed such as increased impervious cover will lead to changes in the physical and chemical environment such as microbial and nutrient pollution (exposures), of a receiving water body which then lead to changes in the living resources (responses). The overall objective of this study is to evaluate the applicability of the current tidal creek classification framework and conceptual model linking tidal creek ecological condition to potential impacts of development and urban growth on ecosystem value and function in the Gulf of Mexico US in collaboration with Gulf of Mexico NERR sites. The conceptual model was validated for the Gulf of Mexico US tidal creeks. The tidal creek classification system developed for the southeastern US could be applied to the Gulf of Mexico tidal creeks; however, some differences were found that warrant further examination. In particular, pollutants appeared to translate further downstream in the Gulf of Mexico US compared to the southeastern US. These differences are likely the result of the morphological and oceanographic differences between the two regions. Tidal creeks appear to serve as sentinel habitats to provide an early warning of the ensuing harm to the larger ecosystem in both the Southeastern and Gulf of Mexico US tidal creeks.

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1.以MS无机盐+B 5有机成分为基本培养基,附加2,4-D,KT,ZT等激素,以农艺性状良好,抗枯萎病的棉花品种“冀492”为材料,建立了愈伤组织诱导,体细胞胚胎发生和植株再生体系. 2.实验结果表明,2,4-D是诱导愈伤组织产生的促进因子,效果明显好于其它生长素类物质,但是随着培养基中2,4-D浓度的升高,愈伤组织状态也会变差,褐化严重,而且,附加O.lppm 2,4-D,O.lppm K T的培养基是较为合适的培养基.IAA,NAA对愈伤组织的诱导不十分理想,此外,愈伤组织的产生还同外植体,基因型和一些物理条件有关, 胚性愈伤组织的产生,需不断调节培养基中激素浓度,逐步降低2,4 -D浓度,并添加低浓度ZT,胚状体要在去除2,4-D的培养基上才能产生.虽然,2,4-D对于胚性愈伤组织的诱导是必须的,但是却抑制胚状体的发育. 3.培养基中硝态氮和氨态氮比例,激素浓度和种类,活性炭的添加,对于胚状体的萌发和成熟有重要影响,硝酸钾加倍,硝酸铵减半,并附加低浓度ABA和活性炭是胚状体诱导和成苗(去除ABA)的适宜培养基,而附加0.2ppm N A A,0.2ppm ZT和活性炭的M S2培养基是胚状体成熟的适宜培养基.通过对胚性愈伤组织的干燥处理,培养基中低浓度ABA和活性炭的添加,比较有效地抑制了畸形胚的产生,大大地提高了正常胚的比例. 4.对陆地棉“冀4 9 2”的下胚轴和子叶利用含Bt抗虫基因的根农杆菌(AgrobacterIIm tumefrens)进行了遗传转化研究,在筛选培养基上获得了大量生长旺盛的阳性愈伤组织,葡糖酸苷检测结果表明,大部分愈伤组织均有G us基因的表达. 5.通过花粉管通道法,进行了将含有Bt抗虫基因DNA的大肠杆菌质粒导入陆地棉“冀492”的实验,并收获了近1 0,000粒种子,为从大量种子中筛选出抗性种质材料,建立了卡那霉素田间初步筛选法. 6.利用活体压片和石蜡切片技术对体细胞胚胎发生过程和胚状体起源进行了观察,发现胚状体发生主要是通过类合子途径进行的,胚状体可能起源于单细胞. 7.通过对相同培养基上的非胚性愈伤组织,胚性愈伤组织和不同时期胚状体的可溶性蛋白SDS - PAGE电泳分析,发现16KD和50K D蛋白特异性地存在于胚性愈伤和各期胚状体中,该蛋白可作为胚性愈伤组织的筛选标记.对不同发育时期的愈伤组织进行了同工酶和可溶性蛋白的IE F/SD S-PA G E双向电泳分析,结果表明,不同发育时期的愈伤组织同工酶酶谱和可溶性蛋白电泳图谱之间具有较大的差别,分化前期的胚性愈伤组织酶的活性强,种类多,并且有新的蛋白斑点的出现,这些都可能与体细胞胚胎发生相关.

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本文通过根农杆菌(Agrobacterium tumfaciens)介导法分别将Signal和KDEL修饰的豇豆胰蛋白酶抑制剂(Cowpea trypsin inhibitor, CpTI)基因、豌豆外源凝集素(Pea lectin, P-Lec)和大豆Kunitz型胰蛋白酶抑制剂(Soybean Kunitz typsin inhibitor, SKTI)双价抗虫基因、雪花莲外源凝集素(Galanthus nivals agglutinin, GNA)基因以及高效复合启动子OM控制的苏云金杆菌(Bacillus thuringiensis, B.t.)杀虫毒蛋白基因导入了陆地棉(Gossypium hirsutum L.)栽培品种新陆早1号、新陆中2号、晋棉7号、冀合321、辽9和晋棉12号,并获得了大批转基因再生植株。 实验中对影响棉花转化和再生的一些条件进行了研究,从根农杆菌培养、棉花无菌苗的制备、转化操作和共培养等方面对转化条件进行了探讨;从激素配化、植物表达载体、外植体类型、基因型等方面对抗性愈伤组织的诱导进行了摸索;从激素、从碳源、培养容器、pH值、抗褐化剂及固化剂的选择等方面对影响植株再生的条件进行了优化。 本文开创性地采用嫁接代替移栽,从而极大地提高了转化植株定植成活率,缩短了缓苗时间并增加了转化植株当代的繁殖系数。 在建立了一套较为高效的陆地棉转化及再生系统基础上,本文还进行了其它转化方式和转化体系的初步探讨。利用棉花幼嫩种子无菌苗下胚轴作为外植体,通过改变愈伤组织诱导培养基配方面提高胚性愈伤组织的诱导频率,进而得到更多的体细胞胚状和再生植株,缩短再生周期;尝试用胚性愈伤组织作为外植体的根农杆菌介导法转化,确定了一些与转化有关的条件;建立了一套棉花茎尖培养程序,为运用基因枪法轰击棉花茎尖分生组织或用根农杆菌直接转化茎尖分生组织,以克服根农杆菌转化棉花时体胚发生的基因型局限开辟了一条新途径。 本文还建立了一种快速鉴定转化植株后代的方法。这一简便方法还有助于进行转基因棉纯合系的筛选以及外源基因的遗传稳定性研究。 转基因植株经Npt-II ELISA、PCR、PCR Southern 检测证明外源抗虫基因CpTI、SKTI、P-lec、GNA以及B.t.基因已存在于转化植株基因组内。修饰的CpTI转基因植株抗棉铃虫(Heliothis armigera Hubner)试验结果表明,其杀虫效果显著优于前期未修饰的CpTI转化植株。P-lec和SKTI双价转基因植株抗棉铃虫试验结果表明,转基因植株对棉铃虫幼虫具有较强的杀虫活力。 目前,已获得转以上抗虫基因棉花T1代植株。为今后进一步将植物基因工程技术应用于棉花遗传改良打下了基础。

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本文采用野外观测和室内测定相结合的方法,研究了内蒙古草原两种主要的土地利用方式(开垦和放牧)对土壤碳库和温室气体通量的影响,结果如下: 1.内蒙古草甸草原开垦后30年后,与天然草原相比,在休闲年份0~20 cm土壤有机碳和土壤微生物量碳含量均没有显著下降,但开垦导致土壤易分解碳下降了24%。土壤易氧化碳受季节性水热因子的驱动,表现出明显的季节变化动态。因此,土壤易分解碳的较土壤碳库的其他组分对开垦更敏感,是表征土壤管理措施引起有机质变化的一个重要指标。 草原开垦后,土壤-植物系统氧化大气甲烷的能力明显提高,农田和天然草原CH4平均吸收通量分别是48.9 和 29.0 μg C m-2 h-1,开垦后增加了1.7倍。开垦没有改变CH4吸收通量 “夏季高秋季低” 的季节变化规律(由降水决定);开垦使N2O的平均释放通量增加了47%,农田和天然草原N2O平均吸收通量分别是56.6 和 38.6 ugN m-2 h-1;开垦同时也增大了通量的变异幅度;但没有改变N2O季节变化规律,只是出现高峰的时间较天然草原推后约10天左右。 2.开垦后的农田土壤在模拟添加厩肥后,刺激了土壤微生物的呼吸代谢,使CO2的释放量增加了5-7倍。试验期间总体排放的CO2中,约60%来源于羊粪,40% 来源于土壤。两种土壤即羊草顶级草原土壤(高碳高氮)和冷蒿-小禾草退化草原土壤(低碳低氮),在CO2的释放总量和释放比例上都没有显著性差异。添加厩肥均造成两种土壤碳库的净碳损失,并且退化草原土壤(7.0%)的土壤净碳损失要大于羊草草原(2.6%)。说明与开垦后的高C土壤相比,在已经退化草原的低C土壤上施厩肥将趋向于土壤更大的净碳损失。 3.自由放牧22年后,羊草草原0~10 cm土壤有机碳、微生物量碳和易分解碳分别下降了14.1%、27.9%和22.0%;大针茅草原0~5 cm土壤有机碳和微生物量碳分别下降了27.6%和38.2%。两类草原土壤碳组分的季节变化受水热因子的驱动,大针茅草原季节波动出现高峰的时间较羊草草原迟。土壤微生物量碳在表征羊草草原和大针茅草原土壤碳素的动态变化时,要敏感于土壤总有机碳。放牧对冷蒿-小禾草草原土壤各碳素组分影响不明显。在表征放牧对冷蒿-小禾草草原土壤的影响指示上,MB-C/ Org-C和Lab-C/ Org-C要比MB-C和Lab-C更加敏感。这说明在研究放牧对草原土壤碳库影响时,不同的草原类型应使用不同的指标来表征其变化。 内蒙古羊草草原是大气CH4的汇,自由放牧增加土壤对CH4的吸收。CH4平均吸收通量增加了27%,但CH4吸收的季节变化形式没有改变;放牧使。自由放牧还增大了N2O的排放通量,将原来N2O源、汇的双重功能改变为单一的源功能;放牧使N2O平均释放通量增加了1倍;放牧显著增加了羊草草原向大气排放CO2的量(p<0.05),并且年度排放量范围也有所增大。 4.草原羊尿斑土壤的pH和NH4+浓度在施后显著升高,但土壤微生物C和N没有明显变化,尿斑N素会发生大量的流失。粪斑和厩肥斑中各有46%和27%的N素分解后转移到植物中。羊草种群斑块上粪尿斑引起CO2和N2O通量的变化,要大于星毛委陵菜种群斑块。与植被类型的影响相比,羊粪尿斑尤其是尿斑对温室气体通量的影响更大。尿斑既降低了土壤对CH4的吸收,又增加了CO2和N2O的释放,使粪尿斑上相当于CO2的净排放量比对照土壤增加了15%。 在内蒙古草原中等放牧条件下,家畜粪尿斑在放牧草地上的覆盖面积约只有2%,与未被家畜排泄物覆盖的草原土壤 相比,粪尿斑对内蒙古草原温室气体总体收支产生的影响可以忽略不计。因此内蒙古草原地区温室气体减排措施的重点,应放在家畜的食性食量对温室气体的影响以及厩肥的科学利用上。但随放牧强度的加大,家畜排泄物覆盖草地的面积将大大增加,加之放牧生态系统中家畜瘤胃代谢产生的的大量温室气体,其对草原温室气体的核算将会产生的影响也是不容忽视的。

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地上净初级生产力(ANPP)是陆地生态系统碳循环的重要组成部分,但由于估测ANPP的方法不同使得对ANPP的估测值存在很大的不确定性。本文采用3种方法(群落中所有种群当年最大地上生物量之和(ANPPC1)、当年群落最大地上生物量(ANPPC2)以及每年固定日期(8月30日)的地上生物量(ANPPC3))在种群、功能群和群落水平上分别对连续19年(1980~1998)的内蒙古羊草和大针茅草原生态系统功能(如ANPP、植物多样性和水分利用效率(WUE))的动态变化进行了比较分析,同时探讨了不同估测方法下气候和放牧对ANPP的影响,在此基础上利用DNDC模型进行了ANPP的模拟和敏感性分析研究,主要结果包括: 在羊草和大针茅草原群落中,不同主要植物种群或功能群多年平均地上最大生物量出现的时间不同,而同一植物种群或功能群的年地上最大生物量出现的时间存在年际间的变化。采用当年最大地上生物量和8月30日固定日期的地上生物量作为群落ANPP的这两种方法高估了建群种或禾草功能群在群落中的作用。 羊草草原群落多年平均ANPPC1、ANPPC2和 ANPPC3分别是257.5、190.1和166.0 g.m-2;相应的大针茅草原多年平均ANPPC1、ANPPC2和 ANPPC3分别是180.4、132.8和122.5 g.m-2。就群落生产力而言,后两种常用的方法二和方法三分别低估了草原群落ANPP 14.2%~40.0%和15.5~59.0%。本文研究表明尽管ANPPC1与ANPPC2和ANPPC3之间存在显著的差异,但二者之间存在极显著的相关性:羊草草原的ANPPC1= 59.587+1.061×ANPPC2(r2=0.865, p<0.001),ANPPC1= 92.329+1.017×ANPPC3(r2=0.569, p<0.001);大针茅草原的ANPPC1= 32.918+1.114×ANPPC2(r2=0.814, p<0.001),ANPPC1= 76.120+0.875×ANPPC3(r2=0.499, p=0.001)。 种群、功能群和群落地上净初级生产力与气候因子间的关系因不同的估测方法而异。羊草草原的建群种羊草种群仅ANPPS3与8月和11月份的平均温度间存在显著相关性,而大针茅草原群落的建群种大针茅种群的ANPPS1和ANPPS2与3月份平均最高气温间呈负相关关系。在羊草草原群落,杂类草功能群ANPPF1和ANPPF2与3月份气温呈负相关关系;而灌木半灌木功能群ANPPF1和ANPPF2与3月份降水呈负相关关系。在大针茅草原群落,禾草功能群ANPPF1与5月份最高平均气温呈显著负相关关系。羊草草原群落ANPPC1和ANPPC3分别与11月份最低温度和平均温度存在显著负相关关系;大针茅草原群落ANPPC1与2和6月份月降水量间相关性显著,ANPP2与5月和11月份月平均最低温度呈显著负相关关系,而4~9月份,1和4月份平均最低温度对群落ANPPC3起决定作用。 在羊草和大针茅草原群落,由方法一得到的群落水分利用效率、Shannon植物多样性指数和均匀度指数与方法二或方法三得到的相应的指数间存在显著的差异,方法二和方法三得到的值间差异不显著。群落地上净初级生产力与相应估测方法的植物Shannon多样性指数和均匀度指数之间相关性不显著。 放牧条件下羊草或大针茅草原群落中的建群种羊草和大针茅在群落中的相对地上生物量较围栏内的相应植物种群的降低,而糙隐子草种群在群落中的比例上升。不同的放牧管理条件下,群落中植物种群地上现存量的季节动态发生变化。群落的植物组成及植物种群地上生物量在群落中总生物量的比例发生了明显的变化。利用遥感来估测地上净初级生产力时,分别低估了羊草和大针茅草原ANPP 52%和27%。 DNDC模型可以很好地模拟内蒙古典型草原生态系统的地上生物量,通过敏感性分析表明降水是草原植物生长的主要限制因子,在降水量增加或降低至日降水的30%时,模拟的地上生物量显著地高于或低于实测地上生物量值。在多年平均降水量为347mm的情况下,随着土壤粘粒含量的增加,地上生物量逐渐降低,与北美草原一致。