基于不同零模型的三江平原沼泽湿地主要物种小尺度点格局分析

在三江平原沼泽湿地,基于不同零模型的点格局方法,研究了常年积水环境条件下沼泽湿地主要优势种毛苔草、漂筏苔草、狭叶甜茅以及小叶章种群的空间分布格局特征。结果表明:在0—200cm尺度范围内4种物种基本都偏离完全随机模型,表现为聚集分布,但偏离的程度不同;除了数量最少的小叶章种群外,其他3种物种都在一定尺度上偏离了泊松聚块模型;毛苔草和狭叶甜茅种群在极小尺度上偏离嵌套双聚块模型,但不显著,而漂筏苔草种群在所有尺度上符合嵌套双聚块模型。种群的实测值偏离完全随机模型的程度越大,越有可能符合符合泊松聚块模型,偏离泊松聚块模型的程度越大,越有可能符合嵌套双聚块模型。4种物种在0—200cm尺度范围内形成的聚块是由营养繁殖引起的,多个分株系统组成大聚块,而每个分株系统形成一个小聚块,聚块的形成加剧了种内竞争,使得种群的聚集强度降低。     

羊草+大针茅草原退化群落优势种群空间点格局分析

草原退化的特征主要表现为群落生产力的大幅下降和植物个体的小型化, 同时, 退化的草原生态系统与一定强度的放牧压力保持平衡而相对稳定。该文应用摄影定位法测定了羊草+大针茅草原退化群落中4个优势种群羊草(Leymus chinensis)、米氏冰草(Agropyron michnoi)、大针茅(Stipa grandis)、糙隐子草(Cleistogenes squarrosa)的空间格局。点格局分析结果表明: 在空间分布格局上, 4个优势种群均偏离完全随机模型和泊松聚块模型, 而符合嵌套双聚块模型, 也就是说, 其空间格局表现为聚集分布, 且在大聚块中分布着较高密度的小聚块。严重退化的草原群落中优势种群的嵌套双聚块空间分布格局当属一种集体行为, 是种群适应过度放牧压力的一种表现形式, 为过度放牧导致的退化草原群落的主要特征之一。这种生态学现象同植物个体小型化一样, 是种群易化(正相互作用)的结果。在过度放牧的胁迫下, 种群通过改变个体性状及个体在空间的分布状况实现自我帮助, 以抵御外界的放牧压力达到自我保护, 从而维持退化草原生态系统与放牧压力间的相对平衡。     

三江平原典型沼泽湿地植物种群的生态位

采用Levins 公式,对三江平原典型沼泽湿地植物群落的优势种群生态位宽度和生态位重叠值进行了研究.结果表明：各湿地植物种的生态位宽度排序为漂筏苔草(0.907)>毛果苔草(0.864) >狭叶甜茅(0.855) >小叶章＝睡菜＝球尾花＝二歧银莲花(0.500).毛果苔草、漂筏苔草、睡菜与球尾花之间,以及狭叶甜茅、小叶章与二歧银莲花的生态位重叠值均较高,说明几种植物在同一资源位上出现的频率相近,利用资源的能力相似,在对资源利用上具有一定的竞争性.睡菜与小叶章和二歧银莲花,以及球尾花与小叶章和二歧银莲花的生态位重叠值均为0,表明几种植物适应环境的方式不同.水分是导致湿地植物生态适应性差异的主导因子,植物对环境生态位适应的程度是水分和营养状况等因素共同作用的结果.湿地植物的生态位特征能较好地表征各植物的生态适应性和分布幅度.     

荒漠草原不同土壤条件下猪毛蒿幼苗种群的点格局分析

采用摄影定位法测定了宁夏荒漠草原3种不同土壤条件下猪毛蒿（Artemisia scoparia）幼苗种群的空间格局,并应用完全空间随机模型、泊松聚块模型和嵌套双聚块模型对其分布格局进行了分析。结果表明：（1）在灰钙土生境下,猪毛蒿幼苗种群在小尺度上（0-2.85m）表现为聚集分布,随着尺度的增大先呈现为随机分布（2.85-3.75 m）,然后又呈现为均匀分布（3.75-5m）;在风沙土生境下,猪毛蒿幼苗种群在0-1.85 m之间表现为聚集分布,在1.85-2.35 m之间表现为随机分布,当尺度大于2.35 m时表现为均匀分布;而基岩风化残积土上的猪毛蒿幼苗种群在整个尺度上均呈现随机分布。（2）猪毛蒿种群幼苗在基岩风化残积土上符合泊松聚块模型,即猪毛蒿种群空间格局的聚块中不存在较高密度的小聚块;而在风沙土和灰钙土上则符合嵌套双聚块模型,即在大聚块中分布较高密度的小聚块。猪毛蒿幼苗种群空间格局的形成与土壤异质性存在着密切的联系,种群在空间中分布格局的形成机制可以通过种群空间格局的分析加以解释。     

三江平原七星河流域湿地植物多样性及影响因素

湿地植物多样性是生物多样性的重要组成部分,在维护湿地生态功能和湿地生态系统稳定性方面发挥着极其重要的作用。为研究七星河流域湿地植物的多样性,选择七星河流域的七星河国家级自然保护区和三环泡国家级自然保护区,分别于2016年和2017年,对该流域内湿地植物进行了实地植物样方调查,共计调查194个样方,利用TWINSPAN进行了样方群落划分,并采用广义线性模型分析了影响植物多样性的影响因素。结果表明七星河流域湿地植物共有532种,隶属于80科,212属,主要群落类型为湿苔草-隐果苔草群丛;狭叶甜茅群丛;萍蓬草-狐尾藻群丛;漂筏苔草群丛;小叶章-臌囊苔草群丛;甜茅-芦苇群丛;芦苇群丛;貉藻群丛等,狭叶甜茅群丛物种多样性较单一,芦苇群丛的物种多样性较丰富。广义线性模型分析结果得出物种多样性与植被密度密切相关,植被密度越大,物种的多样性越小。为七星河流域物种多样性研究提供了重要的基础数据。     

基于不同零模型的点格局分析

在种群空间格局研究中,定量分析格局及其形成过程已成为生态学家的主要目标。在量化分析的众多方法中,点格局分析是最常用的方法,而在选择零模型时,完全空间随机模型以外的复杂零模型很少使用,实际上,这些零模型可能有助于认识格局的内在特征。为此,我们在研究实例中,选择完全空间随机模型(complete spatial randomness)、泊松聚块模型(Poisson cluster process)和嵌套双聚块模型(nested double-cluster process)对典型草原处于不同恢复演替阶段的羊草(Leymus chinensis)种群空间格局进行了分析。结果发现:完全空间随机模型仅能检测种群在不同尺度下的格局类型;而通过泊松聚块模型和嵌套双聚块模型检验表明,在恢复演替的初期阶段,羊草种群在小尺度范围内偏离泊松聚块模型,而在整个取样范围内完全符合嵌套双聚块模型;随着恢复演替时间的推移,在恢复演替的后期,在整个取样尺度上,羊草种群与泊松聚块模型相吻合。这是很有意义的生态学现象。这一实例表明在应用点格局分析种群空间格局时,仅通过完全空间随机模型的检验来分析格局特征,或许很难论证复杂的生态过程,而选择一些完全空间随机模型以外的较复杂的零模型,可能发现一些有价值的生态学现象,对揭示格局掩盖下的内在机制有所裨益。     

不同恢复演替阶段糙隐子草种群的点格局分析

采用摄影定位法测定了羊草+大针茅草原不同恢复演替群落中糙隐子草种群的空间格局,并应用完全空间随机模型、泊松聚块模型和嵌套双聚块模型对其格局进行分析.结果表明:在严重退化的群落中,糙隐子草种群格局表现为嵌套双聚块结构,即在大聚块中分布着较高密度的小聚块;在恢复5年、8年和21年的群落中,则为以母体为中心的泊松聚块结构,即在糙隐子草种群空间格局的聚块中不存在较高密度的小聚块.这说明在严重退化的群落中正相互作用居主导,而在恢复演替群落中负相互作用居主导.糙隐子草种群在恢复演替过程中的格局变化主要是由于伴随放牧胁迫的消失,种群正相互作用(易化)向负相互作用(竞争)转化所致.     

不同降水条件下沙鞭种群生殖株丛空间格局

植物空间分布格局是物种自身生物学特性与环境因素相互作用的结果,生殖株丛空间分布格局则能够揭示物种有性繁殖过程应对异质生境的生态学适应机制。本研究利用群落学调查和基于完全随机、泊松聚块和嵌套双聚块模型的点格局方法,分析了沙鞭(Psammochloa villosa)种群生殖株丛空间分布格局特征,并探讨了空间格局对降水梯度的响应和适应机制。结果表明：(1)聚集分布是沙鞭种群生殖株丛的主要类型。在89、107.8、117.4、186、191.1 mm·a^-1降水梯度上聚集尺度分别为0～90、0～35、0～100、0～125、0～70 cm;(2)基于完全随机模型的空间分布格局对降水的响应规律显著,整体表现为随干旱程度加剧,沙鞭种群生殖株丛聚集尺度从0～125 cm下降至0～35 cm,聚集强度从24.92增长至97.14;(3)在89和107.8 mm·a^-1降水条件上,基于泊松聚块的空间分布格局分别在27～28和6～7 cm中正向偏离泊松聚块模型,但符合基于嵌套双聚块模型的空间分布格局。沙鞭生殖株丛空间格局变化规律反映了物种有性繁殖过程及应对环境...     

基于零模型的宁夏荒漠草原优势种群点格局分析

植物种群空间分布格局是多种生态过程综合作用的结果。明确植物优势种群个体的空间分布格局与形成机制有助于认识种群生态适应对策与群落多样性维持机制。以宁夏荒漠草原优势种群蒙古冰草、短花针茅、牛枝子和牛心朴子为研究对象,采用完全空间随机零模型分析其种群空间分布格局特征,并通过异质泊松零模型与泊松聚块零模型探讨生境异质性、扩散限制等因子在其空间分布格局形成过程中的作用。结果显示:(1)完全空间随机零模型下,4个物种在4 m尺度范围内表现为聚集分布,随尺度增大,逐渐过渡到随机分布和均匀分布。(2)在排除生境异质性的异质泊松零模型下,蒙古冰草种群在整个研究尺度上表现为随机分布;牛枝子、短花针茅和牛心朴子种群仅分别在0—0.2、0.1—0.4 m与0—0.2 m尺度范围内发生偏离,表现为均匀分布与聚集分布,其他尺度均为随机分布。(3)在排除扩散限制的泊松聚块零模型下,所研究种群均表现为随机分布。综上,荒漠草原优势种群在小尺度范围内主要表现为聚集分布;生境异质性与扩散限制均是驱动其空间分布格局形成的重要因子,相对而言,小尺度空间范围内扩散限制的作用更为显著。     

不同降水条件下沙鞭种群非生殖株丛空间格局分析

植物空间分布格局是物种自身生物学特性与环境因素共同作用的结果,非生殖株丛空间分布格局能够揭示物种无性繁殖与种群扩张过程对异质生境的生态学适应机制。利用基于完全随机、泊松聚块和嵌套双聚块模型的点格局方法和群落学调查,分析了沙鞭(Psammochloa villosa)种群非生殖株丛空间分布格局,探讨了空间格局对降水梯度的响应和适应过程。结果表明：(1)聚集分布是沙鞭种群非生殖株丛的主要类型。在89 mm/a、107.8 mm/a、117.4 mm/a、186 mm/a、191.1 mm/a、363 mm/a降水梯度上聚集尺度分别为3—126 cm、9—200 cm、9—129 cm、6—77 cm、2—95 cm、2—96 cm;(2)基于完全随机模型的空间分布格局对降水的响应规律显著,整体表现为随干旱程度加剧,沙鞭种群非生殖株丛聚集尺度从2—96 cm下降至6—77 cm;(3)在107.8 mm/a、117.4 mm/a、191.1 mm/a、363 mm/a降水梯度上,基于泊松聚块模型的空间分布格局分别在15—19 cm、2—6 cm、2—4 cm、9—25 cm尺度正向偏离泊松聚...     

Vegetation and environmental conditions in recently restored wetlands in the prairie pothole region of the USA

How closely the vegetation of restored wetlands resembles that of comparable natural wetlands is a function of the probability of propagules of wetland species reaching reflooded wetlands and how similar environmental conditions in the restored wetland are those in the natural wetlands. Three years after reflooding, we examined the vegetation composition, water level fluctuations, soil organic carbon content, and soil bulk density as well as surface water pH, alkalinity, conductivity, and calcium and magnesium concentrations of 10 restored and 10 natural wetlands. In the restored wetlands, more species of submersed aquatics colonized than were found in natural wetlands, and they rapidly spread to form extensive beds that were larger than those found in natural wetlands. Emergent and wet meadow species in restored wetlands, however, were found in only sparse stands as were a variety of annuals. The vegetation of natural wetlands was predominantly large stands of emergent species. Fluctuations in water storage volume and basin surface area were similar for both restored and natural wetlands. The surface water in restored wetlands had higher pH and lower alkalinity, conductivity, and calcium and magnesium concentrations than that in natural wetlands. Soils of restored wetlands have a lower organic carbon content and higher bulk density than do those of natural wetlands. Our results suggest that for submersed aquatics, dispersal of propagules to restored wetlands is rapid and environmental conditions in restored wetlands are very suitable for their establishment. For other guilds of wetland species, e.g., sedges and other wet meadow species, dispersal to restored wetlands is likely much slower and may pose a serious problem for the re-establishment of these species in restored wetlands. Even if dispersal is not limiting, low surface organic carbon and high bulk density may prevent the establishment of these species in restored wetlands.     

Biological diversity versus risk for mosquito nuisance and disease transmission in constructed wetlands in southern Sweden

In southern Sweden, many wetlands have been constructed, and maintaining or increasing biological diversity is often included in the aims. Some wetlands are constructed near human settlements, thus raising the problem of wetlands being associated with mosquitoes (Diptera: Culicidae). Increased biodiversity (including mosquito diversity) is considered desirable, whereas mosquito nuisance from a human point of view is not. Adult mosquito abundance, diversity and species assemblages of constructed wetlands were compared to natural wetlands. The potential of constructed wetlands for mosquito nuisance and transmission of mosquito-borne viruses was evaluated. The study areas included five constructed and four natural wetlands. Mosquito abundance and species richness were higher in the natural than in the constructed wetlands, and showed a positive correlation with wetland size. Mosquito species assemblages formed three clusters, which were not explained by origin, size and water permanence of wetlands. In a redundancy analysis, however, mosquito faunas showed significant relationships with these variables, and size and origin of wetlands were most important. Major nuisance species (multivoltine species feeding on mammals and laying eggs on soil) were found in all wetlands, although in relatively low numbers. Risk assessment for Sindbis virus transmission showed moderate risk for two constructed wetlands near human settlements. It is concluded that small size of constructed wetlands has the advantage of low mosquito numbers from a human point of view. The use of functional groups is recommended as a tool for presenting mosquito data to the public, and for helping communication between scientists and administrative decision makers.     

State and management of wetlands in Bangladesh

Wetlands are a vital link between land and water in Bangladesh. A majority of the people of Bangladesh are critically dependent on wetlands. In this paper, the values of wetlands, causes and effects of wetlands degradation, as well as the present wetlands management approach, are analyzed and recommendations for wetlands management are suggested based on participatory rural appraisal (PRA), field visit, personal experience, and existing literature and information. Wetlands play a crucial role in maintaining the ecological balance of ecosystems, but wetlands habitat of Bangladesh is under constant threat due to increase of population, intensive agriculture, overfishing, siltation, pollution, ill-planned infrastructures, lack of institutional coordination, lack of awareness, etc. As a result biodiversity is reducing, many species of flora and fauna are threatened, wetlands-based ecosystem is degenerating, and the living conditions of local people are deteriorating as livelihoods, socioeconomic institutions, and cultural values are affected. Wetlands management is not addressed separately in water management activities of Bangladesh. In order to balance human needs and wetlands conservation, a mainly community-based wetlands management approach has been taken in Bangladesh, but this is not enough to prevent the degradation of wetlands. Therefore, Bangladesh now needs a comprehensive strategy combining political, economic, social, and technological approaches to stop further degradation of wetlands. Therefore, wetlands management should be incorporated into a system of integrated land and water use and, indeed, into the socioeconomic system of the country. Policies, strategies, and management plans for sustainable use and conservation of wetlands of Bangladesh must be based on solid knowledge and understanding of their ecological and socioeconomic functions and processes.     

The role of constructed wetlands in secondary effluent treatment and water reuse in subtropical and arid Australia

Water reclamation and reuse is being actively promoted in Australia. In Queensland, surface-flow constructed wetlands with a diversity of macrophyte types offer the greatest potential for effluent polishing. Constructed wetlands in subtropical climates in coastal regions and arid climates in inland western regions are conducive to high macrophyte growth rates and nutrient removal, in particular nitrogen, producing an effluent suitable for irrigation, restoration of wetlands and/or release into natural waterways. Faecal-coliform removal is also high, producing effluent with <1000 cfu/100 mL and as low as 100 cfu/100 mL, acceptable for agricultural irrigation. Constructed wetlands can be designed to maximise the removal of both nutrients and pathogens by enhancing macrophyte diversity and natural disinfection processes by incorporating lagoons, shallow-water wetlands and subsurface-flow wetlands into the treatment train. Surface-flow wetlands can also be designed to minimise mosquito breeding by increasing macro-invertebrate predators, thereby alleviating community concerns about potential health risks. This paper addresses the role of constructed wetlands in nutrient and pathogen removal in Queensland's wetlands, and presents three case studies with respect to effluent reuse.     

Assessing the relationship between biomass and soil organic matter in created wetlands of central Pennsylvania, USA

Created wetlands are frequently structurally different from the natural wetlands they are intended to replace. With differences in structure might come differences in function. Most created wetlands in central Pennsylvania have very low amounts of soil organic matter relative to levels found in natural wetlands. However, anecdotal evidence also suggests that plant production is equivalent in created wetlands to natural wetlands. There is little evidence to indicate that this plant biomass in created wetlands is finding its way into the soil as organic matter. This might translate into a lack of function in the mitigation wetlands. To address this issue, we studied plant biomass production in seven created wetlands in central Pennsylvania (USA). We measured above- and below-ground biomass and compared results with known values of soil organic matter and hydrology for the same wetlands. We found biomass to be approximately equivalent to that produced in natural freshwater marshes, although the below-ground component was somewhat higher. We found no relationship of biomass to soil organic matter, even though site conditions were wet enough to retard plant decomposition.     

Effects of vegetation state on biodiversity and nitrogen retention in created wetlands: a test of the biodiversity–ecosystem functioning hypothesis

1. Nitrogen retention in wetlands provides an example of an ecosystem function that is desired by human society, and is a rationale for the creation of wetlands to decrease nitrogen fluxes from nitrate‐loaded river catchments to coastal waters. 2. Here, we tested the impact of different vegetation states on species diversity and nitrogen retention during 4 years in surface‐flow wetlands receiving nitrate‐rich water. Tall emergent vegetation or submerged vegetation was introduced to six experimental wetlands each and six wetlands were left as unplanted controls for free development of vegetation. This resulted in three vegetation states dominated by emergent vegetation, by a mixture of submerged vegetation and filamentous green algae or by filamentous green algae. 3. Species diversity (species richness and Shannon diversity) of plants was initially lowest in free development wetlands, but during the study became lower in the emergent vegetation wetlands than in the other wetlands. Diversity of macroinvertebrates was initially lower in the submerged vegetation wetlands than in the other wetlands, but this difference disappeared during the study. Nitrogen retention was consistently higher in emergent vegetation wetlands than in the other wetlands throughout the study. 4. We conclude that plant diversity in wetlands dominated by tall emergent vegetation gradually became lower than in other wetlands, due to dominant species competitively excluding other plants. However, these wetlands were more efficient at removing nitrogen than those dominated by filamentous algae or submerged macrophytes. 5. Management of wetlands often aims to decrease the dominance of tall emergent vegetation for the benefit of plant species diversity and habitat heterogeneity. Our results demonstrate a biodiversity benefit, but also show that this strategy may decrease the ability of wetlands to remove nitrogen. In this case, there is no support for the hypothesis that biodiversity enhances ecosystem function.     

湿地生物地球化学过程研究进展

1　湿地生物地球化学过程的概念及内涵营养物质在生态系统之间的输入和输出以及在生物各圈层之间进行的物质和能量交换称为生物地球化学循环 (ｂｉｏｇｅｏｃｈｅｍｉｃａｌｃｉｒｃｕｌａｔｉｏｎ) [4 ] ,它实质上是指生物有机体及其产物与无机环境之间进行的物质交换和能量转换过程。湿地是介于陆地生态系统和水生生态系统之间的过渡地带[3 ] ,它是一种特殊的生态系统 ,其独特多样的生物条件显著影响着生物地球化学过程。这些过程不仅改变了物质的化学组成 ,而且使它们在湿地内发生空间位移以及生物地球化学转化。湿地生物地球化学过程是…     

A comparison of wetland characteristics between Agricultural Conservation Easement Program and public lands wetlands in West Virginia,USA

In West Virginia, USA, there are 24 conservation easement program wetlands enrolled in the Agricultural Conservation Easement Program (ACEP). These wetlands are located on private agricultural land and are passively managed. Due to their location within fragmented agricultural areas, wetlands enrolled in ACEP in West Virginia have the potential to add wetland ecosystem services in areas that are lacking these features. We evaluated ACEP wetlands compared to reference wetlands on public land in West Virginia by using surrounding land cover, vegetative cover, and wetland features and stressors such as the presence or absence of erosion, upland inclusion, algal mats, and evidence of impacts from the surrounding landscape as surrogate measurements of wetland function on 13 ACEP wetlands and 10 reference wetlands. ACEP wetlands had higher percentages of tree coverage and a higher proportion of agricultural land in the areas immediately surrounding the wetland. Reference wetlands had higher percent coverage of emergent vegetation and had a higher proportion of forest in the immediate landscape. Our findings suggest that ACEP wetlands provide valuable early successional and forested wetland cover in a state that is largely forested. Because of this, it is important to maintain and even expand ACEP in West Virginia to continue providing a valuable source of early successional wetland habitat.     

Wetlands as landscape units: spatial patterns in salinity and water chemistry

Athalassic wetlands play a pivotal role in sediment and nutrient cycling and retention at the catchment level and are important ecosystems for local and regional biodiversity. Yet, the management of wetlands outside of riverine floodplains (non-riverine wetlands) is difficult, as there is limited understanding of these water bodies and of the processes that threaten them, like secondary salinisation. Accordingly, we describe the patterns of variation in wetland salinity and water chemistry across a regional landscape that is threatened by secondary salinisation. Spatial analyses indicated the distribution of the study wetlands was non-random and there was considerable positive spatial auto-correlation in water chemistry among wetlands—indicating a lack of independence. We detected massive variation in water chemistry among wetlands compared to minimal within-wetland variation and conductivity accounted for most of the among-wetland variation confirming its prominence in non-riverine wetland water chemistry. Wetland salinities were classified by their chemical evaporative pathway and we found a number of wetlands that may have become secondary salinised. The results reported here support the notion that the study, conservation and management of non-riverine wetlands should include assessments made at multiple spatial scales from individual waterbodies through to catchments. This is important because wetlands may not be independent units, but components of larger systems. However, we also note that the use of individual wetlands as units of replication may be problematic under some circumstances. We also argue that the identification of secondarily salinised wetlands will often require a multiple lines of evidence approach.     

Differences exist in bird communities using restored and natural wetlands in the Parkland region,Alberta, Canada

Wetland restoration is used to compensate for historic and ongoing wetland losses. We compared bird community composition in 24 restored wetlands and 36 natural wetlands in the Parkland region of Alberta. Natural wetlands ranged in exposure to agricultural activity and were binned into three classes (low, medium, and high disturbance). Although the abundance and average species richness of birds were similar between restored and natural wetlands (analysis of variance: p > 0.22), the avian community composition differed significantly among wetland types (multiresponse permutation procedure [MRPP]: A = 0.05, p < 0.001). The avifauna using restored wetlands was distinct from the avifauna using natural wetlands spanning a range of disturbance levels (A = 0.02–0.06; p ≤ 0.006). Notably, restored wetlands were surrounded by less shrub/forest cover and more open water than low‐disturbance, natural wetlands. The majority (58%) of species using the surveyed wetlands were not classified as wetland‐dependent. Interestingly, if only wetland‐dependent species are considered, the avifauna using restored wetlands is no longer distinctive (MRPP: A < 0.01, p = 0.187), although the abundance of wetland‐dependent birds was marginally higher in restored wetlands (n = 24) than in low‐disturbance, natural wetlands (n = 10; Tukey's honestly significant difference test: p = 0.041). Overall, restored wetlands had reduced beta diversity compared to natural wetlands, regardless of whether the avifauna were restricted to wetland‐dependent species or considered comprehensively. This draws into question the legitimacy of the assumption that restoration can fully offset continued losses of natural wetlands.