湿地保护与可持续利用的国际经验借鉴

随着生产力水平的提高以及城市化进程的加剧,我国湿地资源被大力开发利用,逐渐面临面积减少、功能衰退和湿地生态系统受损的困境.本文通过借鉴世界发达国家或地区保护和可持续利用不同类型湿地的成功经验,为国内湿地的保护和利用提出建议:制定湿地保护规划,划分湿地功能区;保护湿地生物资源;实施湿地生态恢复与重建工程;探索可持续利用湿地资源的新思路;适当开发利用泥炭资源;加强湿地资源保护与利用的科学研究;强化湿地知识的宣传、教育与公众参与意识.     

弥苴河口湿地植物残体与底泥资源化利用研究

应用双室堆沤肥技术,以弥苴河口湿地植物残体、湿地底泥和当地养殖业废物制成双室堆沤肥,按不同配比设计5种施肥处理方案进行还田试验。对比研究施肥前后的蔬菜产量、蔬菜品质、土壤肥力以及土壤根际微生物,发现:方案A[50%～60%植物残体(收割物)+40%～50%养殖业废物+微生物菌剂(3 kg/t),活性液体肥作追肥,农药同习惯施肥]对增加蔬菜产量、提高蔬菜品质、增加土壤肥力和改善土壤微生态环境效果最好。在实际应用中也可适当增加1 0%～20%的湿地底泥,相应减少养殖业废物量。     

广东珠海市鹤洲湿地鸟类多样性的动态变化

2010年12月、2011年1月、2月、3月、5月和8月,利用样带法对珠海市鹤洲湿地鸟类物种多样性进行研究,利用Shannon-Wiener指数分析了生境类型的鸟类群落种数、数量、物种多样性、均匀性指数等特征。结果表明,共记录到96种,隶属12目31科66属。鸟类多样性指数(H')进行了计算,12月3.6956,1月3.7685;2月3.6551;3月3.4703;5月3.2437和8月3.1941。该湿地鸟类多样性动态表现出明显的季节性。     

Estimating rate constants of contaminant removal in constructed wetlands treating winery effluent: A comparison of three different methods

In this paper we investigated the use of three different methods for determining the rate constants for degradation of winery effluent within a sub-surface flow constructed wetland (CW). These methods comprised of using a dispersed plug flow (the Peclet) equation; a tanks-in-series (TIS) equation; and analysing the residence time distribution (RTD) directly. The last of these is described by the convolution integral (CI). We demonstrated self-similarity of the RTDs, which meant that the system's hydraulics were similar throughout the CW. We therefore extrapolated the RTD data to develop a more complete understanding of the hydraulic properties of the CW and examine how they affected the kinetics of degradation. We found that whilst both the Peclet and the TIS equation were able to predict concentration within the CW, this required the optimisation of more than one variable at the same time rendering a result that was more of a modelling exercise than a useful design tool. The CI method could be applied to predict system parameters effectively. We used it to measure rate constants of removal for both ethanol and potassium (key species for tracking the degradation/treatment of the effluent). Acetic acid, however, did not degrade implying that the CW operated aerobically. The concentration of sodium increased very slightly, indicating that it is not bioremediated/removed and that there are some minor evapotranspirative effects. The rate constant found for the biodegradation of COD was found to have significantly more uncertainty associated with it than the measurement of the rate of degradation individual components and we therefore posit that it is better to describe the processes of degradation by tracking individual components rather than lumped parameters.     

Examining the relationship between ecosystem structure and function using structural equation modelling: A case study examining denitrification potential in restored wetland soils

An ongoing debate in ecology is the relationship between community or ecosystem structure and function. This relationship is particularly important in restored ecosystems because it is often assumed that restoring ecosystem structure will restore ecosystem functioning, but this assumption is frequently not tested. In this study, we used a novel application of structural equation modelling (SEM) to examine the relationship between ecosystem structure and function. To exemplify how to apply SEM to explore this relationship, we used a case study examining soil controls on denitrification potential (DNP) in two restored wetlands. Our objectives were to examine (1) whether both restored wetland soil ecosystems had similar relationships among soils variables (i.e. similar soil ecosystem structure) and (2) whether the soil variables driving denitrification potential (DNP) were similar at both sites (i.e. the soil ecosystems were functioning in a similar manner). Using the unique ability of SEM to test model structure, we proposed a SEM to represent the soil ecosystem and tested this structure with field data. We determined that the same model structure was supported by data from both systems suggesting that the two restored wetland systems had similar soil ecosystem structure. To test whether both ecosystems were functioning in a similar way, we examined the parameters of each model. We determined that the drivers of DNP function were not the same at both sites. Higher soil organic matter was the most important predictor of higher DNP at both sites. However, the other significant relationships among soils variables were different at each system indicating that the soils were not functioning in exactly the same way at each site. Overall, these results suggest that the restoration of ecosystem structure may not necessarily ensure the restoration of ecosystem functioning. In this study we capitalize on an inherent feature of SEM, the ability to test model structure, to test a fundamental ecological question. This novel approach is widely applicable to other systems and improves our understanding of the general relationship between ecosystem structure and function.     

An ecological risk assessment model for a pulsed contaminant emission into a wetland channel flow

As a continuation of the modelling on ecological degradation and hydraulic dispersion of pollutant emission into an idealized two-dimensional free-surface wetland flow (Zeng, L., Chen, G.Q., 2009b. Ecological degradation and hydraulic dispersion of contaminant in wetland. Ecol. Model., doi:10.1016/j.ecolmodel.2009.10.024), an ecological risk assessment model for the typical case of a pulsed contaminant emission into a realistic three-dimensional wetland channel flow is presented in this paper for the fate of cross-sectional mean concentration under environmental dispersion. An environmental dispersion model for the mean concentration is devised as an extension of Taylor’s classical analysis on dispersion in fluid flows. The velocity distribution and the environmental dispersivity in the fully developed steady flow through the wetland is found and illustrated with limiting cases covering various known solutions for the porous media flow between parallel plates, flow in a shallow wetland, sweeping flow in a densely vegetated wetland, and single phase flow in a channel. Obtained by Aris’s method of moments, the environmental dispersivity is shown characterized with multi-scale asymptotic time variations with stem dominated stage, transitional stage, and width-depth-stem dominated stage. Based on the solution for the evolution of contaminant cloud in the wetland channel flow, critical length and duration of the contaminant cloud with concentration beyond given environmental standard level are concretely illustrated for typical pollutant constituents in wastewater emission. Under the same emission intensity and environmental standard, the duration of contaminant cloud in the wetland channel is revealed shorter than that in a free surface wetland, due to the lateral effect.     

人工湿地污染物去除效率稳定性分析——以沈阳市满堂河污水处理中心为例

利用沈阳市满堂河污水处理中心人工湿地8年来运行数据,对人工湿地整体系统和不同功能区的水质净化效果进行了对比分析,结果表明,潜流人工湿地对CODCr的去除效率,在50%～70%;表面流人工湿地对CODCr的去除效率,稳定在20%左右;人工湿地系统整体对悬浮物和氨氮的去除效率保持在50%以上;人工湿地系统对污染物质的去除效率,随着运行时间增加而日趋稳定。     

白洋淀湿地生态修复的现实困境及解决路径探析

白洋淀湿地有"华北之肾"的称号,是京津冀地区的重要水源地之一。近年来白洋淀湿地显现出了生态退化的趋势,生态修复工作正在开展但成效不稳固。从生态系统整体性的角度全面评估白洋淀湿地的基本情况、生态修复工作开展情况,在此基础上提出生态修复过程中将会面临的问题,并提出解决路径。     

四川若尔盖湿地退化成因分析与对策研究

本文以四川若尔盖湿地为研究对象,主要贡献为：（1）应用卫星遥感数据对若尔盖湿地退化趋势进行了科学定量分析;（2）采用博弈论的分析方法对相关利益主体进行解析,在寻求利益均衡点的基础上,提出湿地保护性开发对策;（3）针对湿地退化因素提出了多种对策,其中生态移民的设想对保护四川若尔盖湿地较为适宜;（4）提出了“禁止-限制-发展”的产业结构调整思路,以指导湿地的合理开发利用。     

Multi-element accumulation near Rumex crispus roots under wetland and dryland conditions

Rumex crispus was grown under wet and dry conditions in two-chamber columns such that the roots were confined to one chamber by a 21 μm nylon mesh, thus creating a soil-root interface (‘rhizoplane’). Element concentrations at 3 mm intervals below the ‘rhizoplane’ were measured. The hypothesis was that metals accumulate near plant roots more under wetland than dryland conditions. Patterns in element distribution were different between the treatments. Under dryland conditions Al, Ba, Cu, Cr, Fe, K, La, Mg, Na, Sr, V, Y and Zn accumulated in soil closest to the roots, above the ‘rhizoplane’ only. Under wetland conditions Al, Fe, Cr, K, V and Zn accumulated above as well as 3 mm below the ‘rhizoplane’ whereas La, Sr and Y accumulated 3 mm below the ‘rhizoplane’ only. Plants on average produced 1.5 times more biomass and element uptake was 2.5 times greater under wetland compared to dryland conditions.