Analyzing the dynamics of Dafeng coastal wetland based on remote sensing image

Dafeng wetland is the largest coastal wetland in Asia, located on the shore of the Yellow Sea. Recently, inning, irrationality utilizing, and water contaminating all threaten it, so the area of the wetland is decreasing and its quality is declining increasingly. Therefore, it is significative to analyze the dynamics of wetland with RS image of Dafeng coastal wetland. To enhance the clustering, fuzzy c-mean algorithm is improved and used to cluster Dafeng coastal wetland. Through the improvement, the problem is solved that assortment is not very good bringing by the difference of sample number. Furthermore, changing information about Dafeng coastal wetland is analyzed by dynamic degree model and the check module of software erdas is used to analyze the dynamics of wetland. Integrating local data with improved fuzzy c-mean algorithm and dynamic degree model mentioned above, dynamics degree of Dafeng coastal wetland＇s area is calculated. The calculating result shows that the area of tour and residence increases greatly while that of bulrush and grassplot decreases largely, that of woodland changes little. The conclusion accords with the fact the main factors include natural and man-made ones, which lead to Dafeng coastal wetland resource change. From nature, coast expansion caused by bedload sediment makes wetland away from sea, disappearing finally. On the other hand, many tour projects are constructed, including training center, reception center, education center, etc; Part of the wetland is utilized as residence, pound, farm, salt field, etc. All of those account for about half of the wetland. Further, fertilizer, pesticide and machine noise contaminate the wetland environment. Finally, problem of management is one of the main restriction factors. Managing manner of traditional agriculture, growth of tourism and expansion of coast are the main driving factors for wetland changes.     

Phosphorus removal by constructed wetland treating agricultural runoff in Dianchi region of China

Phosphorus (P) in agricultural runoff may cause eutrophication of recipient waterbodies. As one of the key waterbodies to be protected in China, the Dianchi Lake is highly sensitive to pollution sources, so agricultural runoff of the region must be treate…     

Dynamics of the Kopački Rit (Croatia) wetland floodplain water regime

Kopa?ki Rit Nature Park is part of the Danube River natural floodplain and one of the last oases of wild life in the Danube River Basin. Due to its extraordinary value, it was inscribed on the list of Wetlands of International Importance in 1993. More than 2,000 species have been registered in this area, which consists of lakes, canals, grassland, marshland and forests. Even the number of investigations which have been performed on its biological and ecological features, hydrological and water resources characteristics, as a prerequisite for ecohydrological analyses, are still rather unknown in the scientific community. Mainly the Danube River and partly the River Drava cause flooding of Kopa?ki Rit and inundations enter the area from both the northern and southern parts. Results of hydrological and meteorological analysis show a decreasing trend of both mean and minimum, annual water levels in the Rivers Drava and Danube (respectively 1.8 and 1.38 cm/year). These reductions in water level can reduce the replenishment periods of Kopa?ki Rit Nature Park. In addition, a significant rise of mean annual air temperature and consequently water temperature (data 1988–2011) may be causing increasing evapotranspiration and loss of water within Kopa?ki Rit. But an encouraging counteracting finding is that, the results of frequency analysis show, even a discharge of 5-years’ return period on the River Danube inundates 70 % of the Danube floodplain and Kopa?ki Rit Nature Park.     

Hydrogeochemical investigation of Küçük Menderes River coastal wetland,Selçuk–Izmir,Turkey

Küçük Menderes River forms a rich coastal wetland inside in the Selçuk plain. Three saline/brackish lakes, one swamp and Küçük Menderes River are these wetlands’ components. Alkaline-slightly alkaline type lakes are recharged from precipitation and karstic springs that discharge from marble-schist and marble-alluvium contacts in the northern and southern parts of the study area. Water types of the wetland are Na–Cl and Na–Ca–Mg–HCO₃–Cl in both rainy and dry seasons. Both seawater intrusion and evaporation, as being the sources of the ions, justify the presence of Na–Cl, Na–SO₄ and Cl–SO₄, in the wetland water. Environmental isotopes were used to identify the relationship between wetland and groundwater in the Selçuk plain. The δ¹⁸O and δD composition of wetland area samples have changed between ?6.42 to ?4.56‰, and ?36.40 to ?23.80‰, respectively. The lakes and rivers are plotted on the mixing line by slope of 5.2 and these data indicate that wetland is affected from seawater intrusion. The recharge area that was sampled in order to compare the wetland has Ca–HCO₃ water type with a neutral-slightly alkaline pH values and the main hydrogeochemical process is weathering the different types of silicates. Iron, manganese and selenium are the dominant minor ions due to the high biological activities and organic matters in the lakes. There are two contamination risks for this wetland: (1) waste disposal site and (2) water treatment plant where the purified waters are released into the river. EC, Al, As, Cd, Cu, Fe and Zn values exceed those of aquatic life standards. In the near future these sites will pose a danger for wetland wild life and surrounding irrigation water suppliers.     

Towards hydrological and geochemical understanding of an ephemeral palustrine perched water table “wetland” (Lanseria Gneiss,Midrand, South Africa)

Wetland delineation is commonly based on terrain unit, soil form, soil wetness and vegetation indicators which along with the shallow groundwater or proximate surface water are often absent in many ephemeral inland South African areas due to, for instance, prolonged dry periods (seasons to years) which mask these indicators, as well as disruption of surface materials due to construction, agricultural activities and field fires. Furthermore, many “wetlands” in South Africa comply with the four indicators, but the notable absent requirement for wetlands is missing, namely the shallow groundwater table, as many of these systems form in hillslope seeps, catenas or from perched water tables. A 200-m-long excavation through one such a system is being studied in Midrand (Gauteng, South Africa). The site is underlain by Lanseria Gneiss and is waterlogged after long and intense periods of intense rainfall. Frequent downslope soil profiling, horizon-specific laboratory analyses for grading and Atterberg Limits, X-Ray Diffraction and X-Ray Fluorescence Spectroscopy data are interpreted together with soil percolation tests to generate a conceptual model of the system. The results are discussed in terms of the need to consider these temporary systems that do not have a shallow groundwater table and that are not in direct contact with surface drainage features as a possible special type of wetlands, notably in arid regions where they play a very important role in biodiversity and should, therefore, be protected.     

Model of hydrological behaviour of the anthropized semiarid wetland of Las Tablas de Daimiel National Park (Spain) based on surface water–groundwater interactions

Las Tablas de Daimiel National Park (TDNP) in Spain is one of the most important semiarid wetlands of the Mediterranean area. The inversion of the regional groundwater flow, primarily due to overexploitation and inadequate aquifer management, has led to degradation. The system has turned from a groundwater discharge zone into a recharge zone, and has remained mostly dry since the 1980s. High heterogeneity and complexity, enhanced by anthropogenic management action, hampers prediction of the surface–groundwater system response to flooding events. This study analyses these interactions and provides empirical evidence to define a conceptual model of flooding-infiltration-groundwater dynamics through the application of a few simple analysis tools to basic hydrological data. Relevant surface water–groundwater interactions are mainly localized in the left (west) margin of TDNP, as confirmed by the fast responses to flooding observed in the hydrochemic, hydrodynamic and isotopic data. During drying periods, small artificial and/or low-flow natural floods are followed by infiltration of evaporated poor-quality ponding water into saline low-permeability layers. The results allow an improved understanding of the hydrological behaviour essential to support efficient management practices. The relative simplicity of the methodology allows for its application in other similar complex groundwater-linked wetlands where detailed knowledge of local geology is still absent.     

Dynamics of ammonia-oxidizing archaea and bacteria in relation to nitrification along simulated dissolved oxygen gradient in sediment–water interface of the Jiulong river estuarine wetland,China

Dissolved oxygen (DO) is a very important factor controlling the nitrogen cycle in wetlands. However, it is still unclear to what extent the presence of ammonia-oxidizing archaea (AOA) and bacteria (AOB), and related nitrification, are influenced by DO in estuarine wetlands. The aims of this study were to determine changes of nitrification at the sediment–water interface, to examine the abundance and diversity of archaeal and bacterial ammonia oxidizers in estuarine sediments, and to identify the correlation between nitrification and ammonia-oxidizing microorganisms along a simulated dissolved oxygen gradient in a Chinese estuarine wetland. The results showed that the nitrification rate was positively correlated with the diversity and abundance of AOA but not AOB, and the abundance and diversity of AOA can explain 87 % of the total variance of the first axes in the redundancy analysis. This indicates that AOA were primarily involved in ammonia oxidation in this study. Additionally, AOB were much more influenced by DO than AOA inferred from the assessment of dominant species and principal coordinates analysis of AOA and AOB. Higher diversity and abundance of AOA occurred in the mangrove sediments, which explain the higher nitrification rates in the mangrove sediments compared to the bare mudflat sediments. Notably, the trend of nitrification rate in the bare mudflat sediments was different from that in the mangrove sediments, suggesting that the extent of nitrification as impacted by DO depends largely on the sediment biotic and nutrient properties, and its environmental conditions including DO levels.     

Common reed grass,<Emphasis Type="Italic">Phragmites australis</Emphasis>, expansion into constructed wetlands: Are we mortgaging our wetland future?

The use of constructed wetlands to replace natural wetlands has become a widespread management tool. Because of the inherent disturbed nature of these sites, constructed wetlands are susceptible to colonization by undesirable plant species. Vegetated communities in 15 constructed wetland sites ranging in age from 1 to 12 yr and in size from 0.4 to 5.3 ha were surveyed using differential global positioning system (GPS) technology in 1994. These sites were re-surveyed in 2000. Colonization of the sites byPhragmites australis expanded from 73% of the sites in 1994 to 80% of the sites in 2000. The total area colonized byP. australis within the sites increased from 3.47 to 4.96 ha. In some sites, the area ofP. australis decreased, which appears to be correlated with an increase in scrub-shrub vegetation (0.986, p=0.014). Similar to results from the previous study, sites that are surrounded by subtidal perimeter ditches have significantly lessP. australis than those sites without perimeter ditches (p=0.019).P. australis expansion rates within the sites varied from 0.1 to 5.6 yr^?1. Colonization of constructed wetland sites byP. australis should be a continued concern of resource managers. Activities such as planting scrub-shrub species on the upland-wetland berm and construction of subtidal perimeter ditches should be considered as methods to reduce the probability of invasion.