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1.
互花米草盐沼土壤有机质分布特征   总被引:7,自引:1,他引:7  
互花米草是我国从美国引进的外来物利,目前在我国沿海已形成大面积的互花米草盐沼,对潮滩土壤等环境产生重大影响。为了分析互花米草盐沼土壤有机质的分布特征,本文通过对江苏东台沿海不同地点(生长年数)的互花米草盐沼土壤样品的-仃机质含量分析,发现互花米草盐沼在由海堤向外的水平方向上变化的平均梯度为每100m土壤有机质含最减少0.87g/kg,垂直方向上的平均梯度为每向下1cm土壤有机质含量减少0.05g/kg。互花米草盐沼土壤订机质的含量与互花米草生长年数相关程度较高,而与植株的生长状况相关较低。  相似文献   

2.
滨海盐沼作为重要的湿地生态系统,有极大的社会、经济和生态价值。文章采用多源国产高空间分辨率卫星数据,结合野外现场调查,对广东和广西滨海盐沼开展遥感调查与分析。2019年年底,广东和广西滨海盐沼分布面积分别为1 258.00 hm2和1 450.36 hm2。广东14个沿海市除茂名市外均有滨海盐沼分布,珠海市、江门市、湛江市的分布面积分别为438.89 hm2、331.83 hm2和162.36 hm2,占广东滨海盐沼总面积的34.89%、26.38%和12.91%。广西3个沿海市均有滨海盐沼分布,北海市、防城港市和钦州市的分布面积分别为1 354.87 hm2、49.73 hm2和45.76 hm2,占广西滨海盐沼总面积的93.41%、3.43%和3.16%。广东和广西互花米草分布面积分别为327.96 hm2和1 312.02 hm2。广东海岸带互花米草主要分布在江门市、阳江市、湛江市和潮州市,分布面积分别为179.07 hm2、73.64 hm2、69.72 hm2和5.52 hm2。广东近5年海岸带互花米草面积较为稳定,没有大范围暴发式扩散。广西海岸带互花米草主要分布在北海市和钦州市,分布面积分别为1 309.04 hm2和2.98 hm2。广西海岸带互花米草面积比最早引种时增加了1 311.08 hm2。互花米草在广西北海东海岸、铁山港、廉州湾和大风江口不断扩张,廉州湾的互花米草仍处于种群扩散的暴发期,需加强对互花米草的监测和防控工作。  相似文献   

3.
文章依据2021年9月黄河口盐沼湿地沉积物调查数据,分析了沉积物粒度、容重、有机碳分布特征,并对黄河口盐沼湿地沉积物碳密度及碳储量进行评估。结果显示,黄河口盐沼湿地沉积物类型以粉砂为主,部分层次为砂质粉砂和黏土质粉砂;4种植被类型中,不同深度的沉积物容重差异性不大,互花米草和盐地碱蓬分布区容重整体大于柽柳和芦苇分布区;互花米草、盐地碱蓬、芦苇和柽柳分布区沉积物中有机碳含量分别为0.199%、0.200%、0.184%和0.161%,互花米草和盐地碱蓬分布区底质中有机碳含量较芦苇和柽柳分布区偏高,这与互花米草和盐地碱蓬分布区含有更多的黏土组分有关;计算得出,黄河口盐沼湿地沉积物总碳储量为33.47万t,其中互花米草分布区为14.31万t,芦苇分布区为12.05万t,柽柳分布区为5.27万t,盐地碱蓬分布区为1.84万t。  相似文献   

4.
江苏沿海互花米草盐沼动态变化及影响因素研究   总被引:14,自引:0,他引:14  
收集了1988-2001年12个时相的江苏盐城幅卫星影像,提取了双洋河口至梁垛:河闸之间的互花米草盐沼;统计了不同时期的分布信息。分析表明:①互花米草盐沼在江苏扩张非常迅速,到2001年7月互花米草盐沼分布面积达129.28km^2,从射阳河口至梁垛河闸之间的潮问中上带泥滩大部分已被互花米草盐沼所覆盖;②由于生态位的影响,互花米草盐沼沿平行于海岸线方向的扩张速度快于垂直于海岸线方向的扩张速度;③依据野外调查和卫星影像分析,互花米草盐沼扩张可分为3个阶段:立地阶段、快速扩张期及成熟期。此外,还对互花米草盐的影响因素进行了探讨。  相似文献   

5.
互花米草对泉州湾盐沼表层沉积物输运的影响   总被引:1,自引:0,他引:1  
海岸盐沼是海岸湿地系统的重要组成部分,具有很强的环境调节功能.互花米草(Spartina alterniflora)的引种对海岸盐沼的沉积动力产生很大影响.粒度分析结果表明,互花米草盐沼边缘与沉积物平均粒径为6.7φ的等值线分布一致.现场观测表明,互花米草对流速具有明显的阻滞作用,使得光滩流速明显大于互花米草内的流速;在互花米草滩内,随着离盐沼边缘距离、植被高度、植株直径的不同,涨落潮流速也表现出不同的变化趋势.粒径趋势分析结果显示,互花米草盐沼边缘的表层沉积物由光滩向盐沼内输运,潮水沟的存在对沉积物的输运格局具有显著影响.对比分析表明落潮后期的水动力条件控制着研究区内表层沉积物的净输运方向.  相似文献   

6.
李屹  陈一宁  李炎 《海洋通报》2017,36(3):348-360
红树林和盐沼是世界上重要的滨海湿地类型。在我国东南部沿海,互花米草盐沼和红树林之间的竞争成为一个重要的问题。为了研究红树林和互花米草盐沼之间的空间竞争规律,选取福建漳江口红树林国家级自然保护区为研究区域,收集了1988年至2014年27年间共15期覆盖该区域的Landsat影像和Google Earth影像,采用最大似然分类法提取出红树林与互花米草盐沼的近30 a历史变化信息。历史遥感影像分析表明:1)红树林面积20世纪90年代增长速度最快,2004年以后增长速度变慢;2)互花米草最早出现在2002年,此后以缓慢的速度朝着地势高的区域扩散,2010年后互花米草的扩散速度加快;3)红树林与互花米草的交界区基本保持稳定,部分区域表现为红树林略微向外扩张;4)影响红树林与互花米草盐沼交界区空间格局的因素可能有潮沟的分布和红树林的林冠完整性等。  相似文献   

7.
互花米草对福建泉州湾海岸湿地沉积环境影响   总被引:3,自引:0,他引:3  
泉州湾淤泥质海岸湿地分布广泛,互花米草分布面积较大.利用小型电磁式流速仪进行流速观测,结果显示,水流由光滩湿地进入互花米草湿地后速度迅速减小,但随着互花米草带宽度地增加,减小程度逐渐变小且不显著.利用PVC管采集短柱状样并现场以一定间隔分样,进行粒度分析、TOC和TN分析及重金属分析结果显示,光滩湿地沉积物颗粒较粗,互花米草湿地边缘沉积物颗粒粗细均有且分选较差,密集互花米草湿地内沉积物粒径较细且分选较好,红树林湿地内沉积物颗粒最细且分选最好;稀疏互花米草湿地作为盐沼发育演化的青年阶段,对C、N具有很强的富集能力,红树林则对C、N的富集能力最弱,人类的排污活动增加了海岸湿地沉积物中的TOC含量;互花米草的存在拦截和吸附了陆源污染物,并使重金属富集在互花米草湿地沉积物中.  相似文献   

8.
滨海盐沼的碳库变化可为蓝碳碳汇核算提供依据。为量化短时间尺度(季节到年际尺度)内滨海盐沼碳库的固碳速率,基于高分辨率的地表高程监测系统,于2022年在杭州湾南岸典型滨海盐沼开展了季节性的观测和采样分析。研究结果表明,在观测期间,本地种海三棱藨草和外来种互花米草的生长呈现季节性变化特征,植物生长主要集中在3—9月。就植物碳库的地下部分而言,海三棱藨草固碳量达到11 g C·m-2,互花米草盐沼则较高,为56 g C·m-2。地表高程监测数据表明,海三棱藨草盐沼的沉积速率为12.30 cm·a-1,略低于互花米草盐沼的沉积速率(13.02 cm·a-1)。结合沉积速率与沉积物容重、有机碳含量等数据,可以算得观测期间,海三棱藨草盐沼沉积物碳埋藏速率为460 g C·m-2·a-1,互花米草盐沼沉积物碳埋藏速率为588 g C·m-2·a-1,这两种滨海湿地的碳埋藏速率也具有季节性,在夏、秋季达到高值。结合植物碳库和沉积...  相似文献   

9.
滨海盐沼作为重要的海岸带生态系统,在海岸保护、生物多样性维持、固碳减污等方面发挥了重要的生态服务功能。及时准确地监测滨海盐沼分布情况和动态变化,对于科学地管理和保护本地滨海盐沼生态系统意义重大。本研究基于2019年和2021年多源国产高空间分辨率卫星数据,结合无人机自主性强、灵活机动、不受云遮挡影响的优势,对广西壮族自治区滨海盐沼开展遥感跟踪监测。研究结果表明,广西2021年滨海盐沼总面积为1 341.40 hm2,其中,北海市、防城港市和钦州市3个海滨城市的滨海盐沼面积分别为1 247.82 hm2、49.73 hm2和43.85 hm2。与2019年相比,广西2021年滨海盐沼总面积减少108.96 hm2,其中,北海市互花米草(Spartina alterniflora)面积减少107.05 hm2,钦州市短叶茳芏(Cyperus malaccensis)和芦苇(Phragmites australis)面积减少1.91 hm2,防城港市滨海盐沼面积不变。广西当地对入侵种互花米草的治理卓有成效,互花米草大范围减少,但局部区域的互花米草分布仍呈不断增长的趋势,仍需重视对互花米草的监测与防控工作。  相似文献   

10.
杭州湾南岸互花米草潮滩底质粒度及其分布特征   总被引:1,自引:0,他引:1       下载免费PDF全文
李加林 《海洋科学》2008,32(8):53-57
以杭州湾南岸为例,探讨互花米草(Spartina alterniflora)潮滩底质的粒度及其分布特征。结果表明杭州湾南岸互花米草潮滩底质由黏土质粉砂、粉砂、粉砂质砂和砂质粉砂组成;从杭州湾口向湾内,互花米草潮滩底质中值粒径逐渐变粗,分选性变好;从低潮滩向高潮滩,互花米草潮滩底质的中值粒径逐渐变小,分选性变差。互花米草盐沼的形成使得潮滩底质粒度及其分布特征产生明显改变。  相似文献   

11.
为探讨互花米草(Spartinaalterniflora)入侵对三沙湾光滩、红树林湿地的生态影响,分别于2013年10月和2014年9月在三沙湾选择了2条互花米草断面、2条红树林断面和1条光滩进行底栖生物生态调查,分析了大型底栖动物群落分布的时空差异、底栖动物与环境因子之间的关系。经鉴定,该调查海域大型底栖动物共68种,隶属于7门40科,其中短拟沼螺(Assiminea brevicula)为互花米草区优势物种;宁波泥蟹(Ilyoplaxningpoensis)为光滩的优势物种;巴林虫(Barantollasp.)为红树林区优势物种。对各生境大型底栖动物物种数、生物量和栖息密度组成进行双因素无重复方差分析(two-way ANOVA),结果显示不同生境大型底栖动物物种数差异极显著(P0.01),互花米草入侵红树林后,大型底栖动物物种数稍有下降,但是互花米草入侵光滩后,大型底栖动物物种数有所增加;不同生境大型底栖动物生物量差异极显著(P0.01),栖息密度差异不显著(P0.05)。利用大型底栖动物的ABC曲线分析群落结构的稳定性,显示光滩群落结构稳定,互花米草入侵后,优势物种变化显著,双齿围沙蚕数量迅速增加,降低了原有大型底栖动物群落结构的稳定性。除生境影响外,互花米草入侵的潮位区域、生长密度差异、入侵阶段等也均会对大型底栖动物造成影响。  相似文献   

12.
Coastal salt marshes represent an important coastal wetland system.In order to understand the differences between boundary layer parameters of vegetated and unvegetated areas,as well as the mechanisms of sediment transport,several electromagnetic current meters (AEM HR,products of Alec Electronics Co.Ltd.) were deployed in coastal wetlands in Quanzhou Bay,China,to measure current velocity.During the low tide phase,the surficial sediment was collected at 10 m intervals.In situ measurements show that the current velocities on the bare flat were much higher than those in the Spartina alterniflora marsh.Current velocity also varied with distance from marsh edge and plant canopy height and diameter.Around 63% of the velocity profiles in the tidal creek can be described by a logarithmic equation.Over the bare flat and Spartina alterniflora marsh,a logarithmic profile almost occurs during the flood tide phase.Sediment analysis shows that mean grain size was 6.7 Φ along the marsh edge,and surface sediments were transported from bare flat to marsh;the tidal creeks may change this sediment transport pattern.The hydrodynamics at early flood tide and late ebb tide phases determined the net transport direction within the study area.  相似文献   

13.
We studied the population ecology of the snail Melampus bidentatus in relation to patch composition and landscape structure across several salt marsh systems in Connecticut, USA. These marshes have changed significantly over the past 40–50 years including loss of total area, increased areas of short Spartina alterniflora, and decreased areas and fragmentation of Spartina patens. These changes are consistent with tidal inundation patterns that indicate frequent flooding of high marsh areas. Melampus bidentatus densities were highly variable, both among different salt marsh systems and locations within specific marshes, but were generally similar among short Sp. alterniflora and Sp. patens patches within locations. Densities were lowest where the marsh was regularly inundated at high tide and only remnant Sp. patens patches remained. Almost no snails were found in bare patches. Areas that had large Sp. patens patches adjacent to short Sp. alterniflora supported the highest M. bidentatus densities. Population size‐structure varied significantly among patch types, with higher proportions of large individuals in short Sp. alterniflora and hummocked Sp. patens patches than in large and remnant Sp. patens patches. This was likely due to size‐selective predation and/or higher snail growth rates due to better food resource conditions in short Sp. alterniflora patches. Egg mass densities and the number of eggs per egg mass were highest in short Sp. alterniflora. Our results indicate that M. bidentatus is resilient to the level and patterns of salt marsh change evident at our study sites. Indeed, snail densities were significantly higher than reported in other field studies, suggesting that increased patch areas of short Sp. alterniflora and associated environmental conditions at our study sites may provide more favorable habitats than previously when marshes were dominated by extensive Sp. patens meadows. However, there may be threshold conditions that could overwhelm the ability of M. bidentatus to maintain itself within salt marsh systems where changes in hydrology, sedimentation and other factors lead to increased numbers of bare patches and ponds and loss of short Sp. alterniflora and Sp. patens. Studies of the responses of resident and transient fauna to salt marsh change are critically needed in order to better understand the implications for salt marsh ecosystem dynamics and services.  相似文献   

14.
Artificially introduced cordgrass, Spartina alterniflora, rapidly colonized the intertidal flats of the Jiangsu coast, eastern China. The epibenthos on an intertidal flat invaded by S. alterniflora were studied, to identify how local epibenthos species react to an altered environment. Epibenthic samples and surficial sediment samples were collected along a shore-normal profile in 50 quadrats at ten stations across the Spartina salt marsh; and five control quadrats for a station located on the barren sandy-mud flat. The grain size parameters of the surficial sediments show that S. alterniflora altered the grain size gradient along the profile of the intertidal zone by trapping fine-grained sediments. Spartina alterniflora could inhabit lower elevations than indigenous salt marsh vegetation, thus creating larger areas of finer surficial sediments, which was suitable for not only native epibenthic species but also species which do not exist on the barren sandy-mud flat. Correlation analyses show that the epibenthos were sensitive to sediment grain size and type, on the invaded S. alterniflora salt marsh. Further, there was an interspecific relationship affecting the distribution of epibenthos. The results show that epibenthos preferred ecological niches, within the Spartina salt marsh, even in the same sampling station.  相似文献   

15.
Spartina alterniflora Loisel., widely recognised as an aggressive invader of estuaries and salt marshes around the world, was discovered growing in the temporarily open/closed Great Brak Estuary on the southern Cape coast of South Africa in 2004. This is the first record of this invasive plant in Africa as well as its first occurrence in an estuary that closes to the sea. Plant traits and sediment characteristics were measured in 2009 and 2011 and found to be comparable to those reported elsewhere. Prior to the 2011 sampling, S. alterniflora stands had been flooded for almost eight months. As a result, sediment redox potential (?268 + 4 mV) was significantly lower in 2011. Sediments were mostly clay in 2009 (71 ± 0.01%) compared to a predominance of sand in 2011 (40 ± 0.02%). These differences were related to the artificial breaching of the estuary one month prior to sampling in March 2011. The grass currently occupies 1.1 ha in the salt marsh, sandflat and mudflat habitats of the estuary where its cover is expanding at a rate of 0.162 ha y?1. Individual stands numbered about 12 in 2006, but have increased to 24 in 2011. These stands are expanding laterally at 0.9 m y?1 although the long period of inundation during 2010 reduced this to 0.6 m y?1. Expansion is due to vegetative spread as an analysis of the sediment seed bank showed no S. alterniflora seeds and very few salt marsh seeds (1 132 seeds m?2). If left unchecked, S. alterniflora has the potential to replace 42.9 ha or 41% of the total estuary habitat in the Great Brak Estuary, but also has the potential to invade other estuaries in South Africa, especially those with extensive intertidal habitat and containing S. maritima (19 estuaries in total). This study illustrates the adaptive potential of this invasive marsh plant and indicates the possibility of invasion in seasonally closed estuaries in other locations around the world.  相似文献   

16.
The analysis of vegetation-environment relationships has always been a study hotspot in ecology. A number of biotic, hydrologic and edaphic factors have great influence on the distribution of macrophytes within salt marsh.Since the exotic species Spartina alterniflora(S. alterniflora) was introduced in 1995, a rapid expansion has occurred at Chongming Dongtan Nature Reserve(CDNR) in the Changjiang(Yangtze) River Estuary, China.Several important vegetation-environment factors including soil elevation, tidal channels density(TCD),vegetation classification and fractional vegetation cover(FVC) were extracted by remote sensing method combined with field measurement. To ignore the details in interaction between biological and physical process,the relationship between them was discussed at a large scale of the whole saltmarsh. The results showed that Scirpus mariqueter(S. mariqueter) can endure the greatest elevation variance with 0.33 m throughout the marsh in CDNR. But it is dominant in the area less than 2.5 m with the occurrence frequency reaching 98%. S. alterniflora has usually been found on the most elevated soils higher than 3.5 m but has a narrow spatial distribution. The rapid decrease of S. mariqueter can be explained by stronger competitive capacity of S. alterniflora on the high tidal flat. FVC increases with elevation which shows significant correlation with elevation(r=0.30, p0.001). But the frequency distribution of FVC indicates that vegetation is not well developed on both elevated banks near tidal channels from the whole scale mainly due to tidal channel lateral swing and human activities. The significant negative correlation(r=–0.20, p0.001) was found between FVC and TCD, which shows vegetation is restricted to grow in higher TCD area corresponding to lower elevation mainly occupied by S. mariqueter communities. The maximum occurrence frequency of this species reaches to 97% at the salt marsh with TCD more than 8 m/m2.  相似文献   

17.
选取江苏王港潮滩的盐蒿滩、大米草滩及互花米草滩,分析这三类滩面的地面以上生物量、初级生产力、动物洞穴参数和沉积物粒度,探讨大米草和互花米草引种区的湿地生态系统相对于盐蒿滩的变化.分析结果表明,互花米草滩的生物量远大于盐蒿滩和大米草滩;单位面积上动物洞穴数量相近,但洞穴大小有一定差异,互花米草滩动物洞穴稍大,数量也相对较多,这可能与初级生产力的提高有关.表层底质的粒径以互花米草滩为最细,盐蒿滩最粗,这种分布状况与互花米草引种前不同,说明互花米草促进了细颗粒物质的堆积.互花米草的引种在江苏海岸具有促淤和提高初级生产力的作用,而它对湿地生态系统的结构和功能的影响需要进一步研究.  相似文献   

18.
Cord grass colonization on the Jiangsu coast, eastern China, modifies the native salt marshes in terms of ecosystem structure. The Landsat TM images from 1992 to 2003 were analyzed to identify salt-marsh vegetation distribution patterns and their changes over this coastal region, in order to evaluate the effects of the spreading of the artificially introduced halophyte Spartina. Supervised classification was performed using Bands 3, 4 and 5 in conjunction with in situ training samples, to derive the distribution pattern of the vegetation in the study area. Further, in order to identify the intertidal areas with different tidal elevations, a data treatment procedure was designed to combine regional water level data using harmonic analysis with the waterlines on the TM images extracted by density slice. The results show that: (1) the Spartina alterniflora area has been expanding towards the sea rapidly since it was introduced, especially at initial stages; (2) in the upper part of the inter-tidal zone, the local marsh plant Suaeda salsa and the exotic species Spartina anglica were present only near the sea dyke, occupying only a small part of the entire salt marsh, and the area of these two species has been reduced by land reclamation; (3) there has been a trend for Spartina alterniflora to become the dominant species in the salt marshes in the study area; and (4) the elevation of Spartina alterniflora’s seaward fringe was close to mean high water on neaps, and its landward boundary was slightly higher than mean high water. The salt marsh environment of the study area has been modified rapidly by the Spartina vegetation for the last 12 years.  相似文献   

19.
互花米草作为黄河三角洲外来入侵物种, 2010年开始爆发式蔓延, 2020年面积最大时可超6 000 hm2,对潮间带生物多样性造成了严重影响。自2020年起,黄河三角洲自然保护区开始大规模的互花米草整治与盐地碱蓬生态修复工作。互花米草具有较强的消浪、缓流、促淤、固滩能力,短期内、大范围的植被去除,可能导致波流和沉积动力环境的突变。基于现场观测数据和考虑植被作用的浪、流、沙耦合数值模型,研究分析了互花米草整治和盐地碱蓬修复对黄河三角洲湿地动力过程的影响,重点关注风暴作用下黄河三角洲潮滩湿地的防灾减灾能力和沉积效应变化。研究结果表明,互花米草可有效抵御极端风暴潮,最大风暴潮位衰减率可达15 cm/km。互花米草整治将导致湿地防灾减灾能力显著下降,堤前风暴潮峰值可抬升10~30 cm,同时潮间带的泥沙捕集能力大幅下降。受限于植被密度、高度,盐地碱蓬完全修复后湿地衰减风暴潮、捕集泥沙的能力显著低于原互花米草湿地。研究建议,互花米草整治工程应考虑短期内植被去除导致的近岸风暴潮抬升、侵蚀加剧等潜在风险。  相似文献   

20.
The Cumberland Basin, a 118 km2 estuary at the head of the Bay of Fundy which has an average tidal range of about 11m, contains large tracts of salt marsh (15% of the area below highest high water). Low marsh (below about 0·9 m above mean high water) is composed almost exclusively of Spartina alterniflora while the vegetation on high marsh is more diverse but dominated by Spartina patens. Because of its higher elevation, high marsh is flooded infrequently for short periods by only extreme high tides. Low marsh is inundated much more frequently by water as much as 4m deep for periods as long as 4 h per tide. Temporal variability in the occurrence of extreme tides influences the flooding frequency of high marsh for any given month and year. Using a modification of Smalley's method, the mean annual net aerial primary production (NAPP) of low and high marsh is estimated to be 272 and 172 g C m?2, respectively. Vegetation turnover times average 1·0 and 2·0 y for low and high marsh, respectively. Because of abundant tidal energy, much of the low marsh production appears to be exported and distributed widely about the estuary. Since high levels of turbidity suppress phytoplankton production, salt marshes produce approximately half of the carbon fixed photosynthetically in the Cumberland Basin. It is concluded that salt marshes play a major ecological role in the Cumberland Basin.  相似文献   

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