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1.
  • 1. Ecological water reserves are part of the new water management philosophy in South Africa. The estuaries are threatened by excessive water abstraction from their rivers and the consequent reduction in freshwater input. This study was conducted to further improve our understanding of freshwater requirements in terms of nutrients for South African estuaries.
  • 2. The Gamtoos Estuary was sampled between November 1996 and November 1998 to determine its nutrient status and freshwater input rates. Furthermore, the possible existence of a distinct river‐estuarine interface (REI) in terms of nutrients has been investigated. Nutrients analysed included phosphate, nitrate, nitrite, ammonia, dissolved organic nitrogen (DON), dissolved organic carbon (DOC), particulate organic nitrogen (PON) as Kjieldahl nitrogen, total particulate phosphorus and total particulate carbon.
  • 3. The Gamtoos River was found not to be the ultimate source of nutrients to the estuary, but non‐point sources such as the seepage of fertilisers from adjacent agricultural fields determined to a great extent the nutrient status of the estuary.
  • 4. Results showed that it was not possible to identify a defined river‐estuarine interface region for all nutrients. Most were measured in higher concentrations in the lower salinity reaches (<17‰) where we observed the combined effect of inputs from the Gamtoos River, an agricultural drainage pipe, and fertilizer seepage from non‐point sources on nutrient concentration.
  • 5. Prolonged water withdrawal for human use impacts the continuous renewal of the nutrient pool so important to other South African estuaries with relative pristine catchment areas. However, reduced fresh water inputs could enhance eutrophication in polluted estuaries due to a decreased flushing potential of the estuary. In this case the Gamtoos Estuary has a freshwater requirement for freshets and floods to “clean” the estuary of accumulated nutrients and other organic material.
  • 6. This should be a consideration in further freshwater abstraction policies. Conservation issues arise since the Gamtoos Estuary is one of the few permanently open estuaries along the South African coast and serve in this study as an example and as a first attempt to relate freshwater requirements to nutrient dynamics in a South African context.
Copyright © 2002 John Wiley & Sons, Ltd.  相似文献   

2.
  • 1. The Ter Vell (NE Iberian Peninsula) is a eutrophic coastal lagoon that has been mostly flooded by excessive irrigation water during recent decades. During 2001 and 2002 the lagoon was subject to several water management actions, the main consequence of which was a change in the hydrological regime due to drastically reduced irrigation water inputs to the lagoon.
  • 2. In order to comply with the Water Framework Directive, all the management actions in an ecosystem should be focused on protecting and, where necessary, improving its ecological status.
  • 3. The aims of this study were (1) to analyse whether the hydrological change caused by management actions have affected the ecological status of the lagoon, and (2) to discuss the suitability of several physicochemical and biological indicators for the assessment of the ecological status in this kind of coastal ecosystem.
  • 4. After the change in the hydrological regime, a general improvement of the ecological status was observed mainly as a result of the significant decrease in the nitrogen Trophic State Index and in the abundance of rotifer indicative of eutrophy, and in turn by the significant increase in the water quality index QAELS, based on crustaceans and insect assemblages.
  • 5. Contradictory results emerged with regard to some of the indicators used. After the hydrological change, the increase in the phosphorus Trophic State Index was related with the fact that Mediterranean confined coastal ecosystems are typically P‐enriched. In contrast with general assumptions, low diversity and richness of the zooplankton and the dominance of a few species have been related with an improvement of the ecological status after the hydrological change, when freshwater inputs were reduced and the lagoon became more confined.
Copyright © 2008 John Wiley & Sons, Ltd.  相似文献   

3.
  • 1. Macroinvertebrates and phytobenthic organisms (e.g. diatoms) are frequently used as bioindicators of water quality, yet few studies compare their effectiveness despite both being emphasized in the EC Water Framework Directive.
  • 2. Here, as a case study, the efficacy of each group in assessing acid–base status in the catchment of the Welsh River Wye was evaluated from surveys in 2 years.
  • 3. Ordination showed that both diatom and macroinvertebrate assemblages varied highly significantly with pH, alkalinity and calcium concentrations. Moreover, ordination scores were highly inter‐correlated between these groups in both study years.
  • 4. There were also contrasts, with diatoms and macroinvertebrates changing in differing ways with catchment land‐use and channel hydromorphology. These differing responses suggest complementary indicator value, while variation in generation times between diatoms and macroinvertebrates suggests potentially contrasting speeds of response to variations over different timescales.
  • 5. These data reveal that significant water quality problems in the River Wye, a proposed Special Area of Conservation, are generated from the continued acidification of low‐order, headwater streams and this has considerable significance for the objectives of the Water Framework Directive, and the EC Habitats Directive.
Copyright © 2006 John Wiley & Sons, Ltd.  相似文献   

4.
  • 1. River restoration is now widely undertaken and may be considered an increasingly important aspect of river management. Recent developments in European legislation (Habitats Directive and the Water Framework Directive) should give further impetus to river restoration across EU member states, as this legislation places greater emphasis on the processes that support river ecology.
  • 2. Traditional river restoration approaches have been reach‐focused and opportunistic, capitalizing on flood defence works and the cooperation of sympathetic landowners.
  • 3. Furthermore, many schemes have been species‐ or habitat‐driven and, thus, have sought to recreate channel forms believed to be favoured by particular species or associated with particular habitats. Such approaches have not always given due attention to the underlying geomorphological processes that create channel form and, consequently, the schemes have not been self‐sustaining, requiring continued management input.
  • 4. Consistent with the ethos of the Water Framework Directive, an eco‐hydromorphic approach to river restoration is proposed here. This approach views spatial and temporal heterogeneity as fundamental characteristics of fluvial systems and advocates recreating a framework within which natural processes, such as sediment transport and nutrient dynamics, can occur.
  • 5. Mesoscale habitat approaches are considered as one possible way to plan and achieve this framework, providing the potential to link the wide range of spatial and temporal scales that characterize river systems.
  • 6. It is argued that river restoration will only be sustainable if it is undertaken within a process‐driven and strategic framework with inputs from a wide range of specialists. Such an approach needs to be reviewed constantly in light of appraisal and monitoring of previous river restoration schemes.
Copyright © 2003 John Wiley & Sons, Ltd.  相似文献   

5.
A participatory on-farm study analysed water and nutrient budgets of six low and four high water-exchange ponds of integrated agriculture–aquaculture (IAA) farms in the Mekong delta. Water, nitrogen (N), organic carbon (OC) and phosphorus (P) flows through the ponds were monitored, and data on fish production and nutrient accumulation in sediments were collected during a fish culture cycle. Results showed that, on average, only 5–6% of total N, OC or P inputs introduced into ponds were recovered in the harvested fish. About 29% N, 81% OC and 51% P accumulated in the sediments. The remaining fractions were lost through pond water discharges into adjacent canals. Fish yields and nutrient accumulation rates in the sediments increased with increasing food inputs applied to the pond at the cost of increased nutrient discharges. High water-exchange ponds received two to three times more on-farm nutrients (N, OC and P) while requiring nine times more water and discharging 10–14 times more nutrients than the low water-exchange ponds. Water and nutrient flows between the pond and the other IAA-farm components need to be considered when optimizing productivity and profitability from IAA systems.  相似文献   

6.
  • 1. Anthropogenic‐derived nutrient inputs to coastal environments have increased dramatically worldwide in the latter half of the 20th century and are altering coastal ecosystems. We evaluated the effects of nitrogen loading on changes in macrophyte community structure and the associated fauna of a north temperate estuary. We found that a shift in primary producers from eelgrass to macroalgae in response to increased nutrient loading alters habitat physical and chemical structure and food webs. As nitrogen load increased we found increased macroalgal biomass, decreased eelgrass shoot density and biomass, decreased fish and decapod abundance and biomass, and decreased fish diversity.
  • 2. The central importance of macroalgae in altering eelgrass ecosystem support of higher trophic levels is evident in the response of the ecosystem when this component was manipulated. Removal of macroalgae increased eelgrass abundance and water column and benthic boundary layer O2 concentrations. These changes in the physical and chemical structure of the ecosystem with lower macroalgal biomass resulted in higher fish and decapod abundance and biomass.
  • 3. Both a 15N tracer experiment and the growth of fishes indicated that little of the macroalgal production was immediately transferred to secondary consumers. δ15N values indicated that the most abundant fishes were not using a grazing food web based on macroalgae. Fish tended to grow better and have a greater survivorship in eelgrass compared to macroalgal habitats.
  • 4. Watershed‐derived nutrient loading has caused increased macroalgal biomass and degradation and loss of eelgrass habitat, thus reducing the capacity of estuaries to support nekton.
Copyright © 2002 John Wiley & Sons, Ltd.  相似文献   

7.
  1. Streams with Ranunculion fluitantis and Callitricho‐Batrachion vegetation – or habitat type 3260 according to the European Habitats Directive – require particular conservation at biogeographic level but Member States carry individual responsibility. Within this framework, the environmental requirements of this habitat type in lower Belgium (Flanders) were analysed.
  2. Overall, current vegetation composition was not significantly related to adjacent land‐use but correlated mainly with physical–chemical conditions and to a lesser extent with distance to source and channel width. Even though sites with habitat 3260 generally showed lower levels of human impact, their abiotic features overlapped considerably with those of sites without habitat 3260 but still showing hydrophyte development.
  3. Thresholds occurred in the distribution of responsive macrophyte taxa, including the more common characteristic species of the habitat type, along gradients of increasing solutes and nutrients. Comparison with water quality standards proposed so far to support good ecological status for the European Water Framework Directive in lowland rivers suggests that compliance would probably allow this habitat to persist in most cases, although some discrepancies occur. This implies that more stringent objectives may be required in some water bodies.
  4. The present analysis focuses on the conditions delimiting occurrence of HT 3260, and therefore its range and area in lower Belgium. A comprehensive understanding of its favourable conservation status remains difficult in lowland regions where most rivers are subject to strong human impact and will require a more long‐term perspective that also considers management regime, physical habitat structure and connectivity.
Copyright © 2014 John Wiley & Sons, Ltd.  相似文献   

8.
A one‐time monitoring event was initiated by an aquaculture fishery in North Queensland to assess if the discharges from the aquaculture fishery were increasing nutrient input into the Great Barrier Reef Marine Park. Leaf samples from Avicennia marina (grey mangrove) were used to compare the nitrogen (N) and phosphorous (P) concentrations, and δ15N values in the receiving waters of the adjacent creeks and a set of reference sites established in a neighbouring creek. The same indicators were also measured in macroalgae from the nutrient extraction ponds. The mangrove leaves in the Mixing Zone of the receiving creek were slightly elevated in N concentrations (22 mg g?1 compared to 17.5 mg g?1 at the Reference sites) and δ15N values (6.5 compared to 4.5 at the Reference sites) showing there was an influence from the outputs of the aquaculture fishery. However, P concentrations were the same in the Mixing Zone and Reference sites. Downstream of the Mixing Zone, the concentration of N and P, and the δ15N values in the Receiving Waters were the same as the Reference sites, at levels considered normal in other studies. These results show that aquaculture fisheries can be managed to maintain nutrients at reference levels in mangrove foliage in estuaries of the receiving zones.  相似文献   

9.
10.
  • 1. Concentrations of major nutrients (NH4+‐N, NO3?‐N, NO2?‐N, HPO4?‐P, Si(OH)4‐Si) were measured, nutrient enrichment experiments (oxygen‐production bioassay) were conducted and phytoplankton were analysed at typical long‐line‐culture areas in Laizhou Bay and Sanggou Bay, northeastern China, from March 2001 to March 2002.
  • 2. Generally, much variation of nutrient indices was detected among the sampling stations, between the two bays and in different seasons: the concentration of dissolved inorganic nitrogen (DIN) fluctuated more violently and ranged much more widely in Sanggou Bay. N‐limitation was usually found in both bays, and the ranking of limiting potentials of major nutrients was N>Fe>P=Si in Laizhou Bay and N>P>Fe>Si in Sanggou Bay. Diatoms dominated the phytoplankton community in Sanggou Bay, but only dominated in eight months (with flagellates dominant in four months) in Laizhou Bay.
  • 3. Linear and nonparametric correlation analyses suggested that a large number of the nutrient and phytoplankton variables measured have intrinsic relationships within themselves. Much more complicated correlations between phytoplankton and nutrient indices were found in Laizhou Bay than in Sanggou Bay. This, together with the violent fluctuations of DIN concentrations, indicated a more fragile ecosystem stability in Sanggou Bay.
  • 4. The relatively exposed locations and less crowded settings of the rafts in the long‐line‐culture areas in Laizhou Bay allowed for a better water exchange, and the effect of aquaculture activity on the environment was not significant. Because of the intensity of aquaculture activities in Sanggou Bay, the biological, chemical and physical characteristics in the bay are greatly affected; a reduced cultivation density based on more comprehensive studies of carrying capacity of the bay is suggested.
Copyright © 2004 John Wiley & Sons, Ltd.  相似文献   

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