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Artykuły w czasopismach na temat "Aquatic habitats"

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Monira Akter Ame, Lima Khatun, Sonia Khatun, Shamima Afroj Sumona i AHM Mahbubur Rahman. "Investigation of aquatic vascular flora at Sadullapur Upazila of Gaibandha District, Bangladesh". GSC Biological and Pharmaceutical Sciences 21, nr 1 (30.10.2022): 175–87. http://dx.doi.org/10.30574/gscbps.2022.21.1.0395.

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The present article focused on aquatic vascular plants diversity and their conservation status in natural and manmade wetlands habitats of Sadullapur Gaibandha. The study was conducted in between May 2019 to June 2020. A total of 52 aquatic plant species was recorded from Sadullapur Gaibandha in the present study. These are assigned to 35 genera under 30 families. For each species scientific name, local name, family, division, habit, habitat, use and status are provided. Ecological habitats analysis of aquatics shows variations. Among them, 37% species prefers to grow near the edge of water, 13% submerged, 11% as emergent, 11% as free floating and 28% as rooted floating in the aquatic habitat. In case of submerged species, they produce flowers on surface of the water. After pollination fruits remain under water up to maturation. Among them, 49% species used as fodder, 22% as medicinal, 4% as aquarium purpose, 9% as vegetable, 6% as edible, 10% as fish food in the study area. The population number of different aquatic plant species in habitats is not uniform. Overall analysis showed that 46% aquatic plant species in the study area found to be rare, 44% species found common and 10% species found as abundant. This status of aquatic plant species is very preliminary. Based on field observations and discussion with local people we are able to identify a good number of rare aquatic plants and also pointed some conservation measures for them in future. The investigation recorded a number of rare aquatic plant species from the study area. These are Trapa bispinosa (Singara), Nelumbo nucifera (Paddo), Nymphaea pubescens (Sada shapla), Oenanthe javanica (Panidhone), Nymphaea rubra (Lal shapla), Ottelia alismoides (Panikola), Enhydra fluctuans (Titidata) and Centrostachys aquatica (Thuash). Populations of such species in the wild are very rare because of local demand for the use. These species need to be cared for conservation.
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Smith, Dwight G., i Irving Leskowitz. "Classifying Aquatic Habitats". American Biology Teacher 49, nr 3 (1.03.1987): 157–63. http://dx.doi.org/10.2307/4448467.

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Mackay, Rosemary J. "Temporary Aquatic Habitats". Journal of the North American Benthological Society 15, nr 4 (grudzień 1996): 407. http://dx.doi.org/10.1086/jnortamerbentsoc.15.4.1467794.

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Danks, H. V. "How aquatic insects live in cold climates". Canadian Entomologist 139, nr 4 (sierpień 2007): 443–71. http://dx.doi.org/10.4039/n06-100.

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AbstractIn cold climates most aquatic habitats are frozen for many months. Nevertheless, even in such regions the conditions in different types of habitat, in different parts of one habitat, and from one year to the next can vary considerably; some water bodies even allow winter growth. Winter cold and ice provide challenges for aquatic insects, but so do high spring flows, short, cool summers, and unpredictable conditions. General adaptations to cope with these constraints, depending on species and habitat, include the use of widely available foods, increased food range, prolonged development (including development lasting more than one year per generation), programmed life cycles with diapause and other responses to environmental cues (often enforcing strict univoltinism), and staggered development. Winter conditions may be anticipated not only by diapause and related responses but also by movement for the winter to terrestrial habitats, to less severe aquatic habitats, or to different parts of the same habitat, and by construction of shelters. Winter itself is met by various types of cold hardiness, including tolerance of freezing in at least some species, especially chironomid midges, and supercooling even when surrounded by ice in others. Special cocoons provide protection in some species. A few species move during winter or resist anoxia beneath ice. Spring challenges of high flows and ice scour may be withstood or avoided by wintering in less severe habitats, penetrating the substrate, or delaying activity until after peak flow. However, where possible species emerge early in the spring to compensate for the shortness of the summer season, a trait enhanced (at least in some lentic habitats) by choosing overwintering sites that warm up first in spring. Relatively low summer temperatures are offset by development at low temperatures, by selection of warm habitats and microhabitats, and in adults by thermoregulation and modified mating activity. Notwithstanding the many abiotic constraints in cold climates, aquatic communities are relatively diverse, though dominated by taxa that combine traits such as cold adaptation with use of the habitats and foods that are most widely available and most favourable. Consequently, except in the most severe habitats, food chains and community structure are complex even at high latitudes and elevations, including many links between aquatic and terrestrial habitats. Despite the complex involvement of aquatic insects in these cold-climate ecosystems, we know relatively little about the physiological and biochemical basis of their cold hardiness and its relationship to habitat conditions, especially compared with information about terrestrial species from the same regions.
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MacCracken, James G., Victor Van Ballenberghe i James M. Peek. "Use of aquatic plants by moose: sodium hunger or foraging efficiency?" Canadian Journal of Zoology 71, nr 12 (1.12.1993): 2345–51. http://dx.doi.org/10.1139/z93-329.

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Use of submergent aquatic plants by North American moose (Alces alces) has been linked to sodium hunger. Habitat preferences, seasonal diets, forage abundance and quality, and population surveys indicated that emergent plants in small shallow ponds were important to moose on the Copper River Delta, Alaska. However, sodium was abundant in terrestrial browse. We propose that foraging in aquatic habitats, particularly on emergent species, may be highly efficient based on the following habitat attributes and behavioral observations: (i) ponds dominated by either emergent or submergent species produced about 4 times more forage than terrestrial habitats, (ii) emergent and submergent plants were more digestible and had higher concentrations of minerals than browse, (iii) use of aquatic habitats followed trends in forage production over the growing season, (iv) indirect evidence suggested that forage intake rates were greater in aquatic habitats, and (v) use of aquatic habitats by male and female moose was in proportion to the sex structure of the population. These data provide consistent circumstantial evidence that use of emergent species, and possibly submergents, may maximize the intake of nutrients and also reduce conflicts between cropping forage and vigilance during a foraging bout.
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Muliani, Muliani, Asriyana Asriyana i Muhammad Ramli. "Preferensi Habitat Ikan Gabus [Channa striata (Bloch 1793)] di Perairan Rawa Aopa, Sulawesi Tenggara". Jurnal Ilmu Pertanian Indonesia 26, nr 4 (27.10.2021): 546–54. http://dx.doi.org/10.18343/jipi.26.4.546.

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The use of habitat by fish is closely related to efforts to find the best conditions for the survival of these fish. This study aims to analyze the habitat preferences of Striped snakehead in Rawa Aopa waters, Southeast Sulawesi. This research was conducted from November 2018 to February 2019 in the waters of Swamp Aopa Southeast Sulawesi. Fish collection using traps. The constancy and fidelity index determined the preference of striped snakehead for habitat type. A total of 1024 striped snakehead fish were caught during the study with a length range of 200,0-420,0 mm and 69,0-596,0 g weight. Striped snakehead measuring 200-367 mm were consistent in occupying habitats with a slightly dense to dense water plant density, while sizes 368-388 and 389-430 mm were consistent in habitats with sparse water plant density. The preference level of striped snakehead fish size 389-430 mm to habitats with rare aquatic plants is very high (Fij = 6). Therefore, the size can be used as an indicator of habitats with the rare aquatic plant category. The preference for 200-367 mm striped snakehead fish in dense aquatic plant habitats indicates that these habitats are foraging, growing, and protective zones. Keywords: Channa striata, fish habitat, Rawa Aopa, Southeast Sulawesi, stripe snakehead
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Picard, Gabriel, Gabriel Blouin-Demers i Marie-Andrée Carrière. "Common Musk Turtles (Sternotherus odoratus) select habitats of high thermal quality at the northern extreme of their range". Amphibia-Reptilia 32, nr 1 (2011): 83–92. http://dx.doi.org/10.1163/017353710x541913.

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AbstractIn ectotherms, variation in body temperature (Tb) affects physiological performance and, ultimately, fitness. Therefore, reptiles regulate Tb behaviourally by choosing habitats of optimal temperature. The main goal of this study was to determine the link between patterns of thermoregulation and habitat selection in Common Musk Turtles inhabiting a thermally challenging region. We expected habitat selection to be based on the fulfillment of thermoregulatory requirements, which can be accomplished by selecting thermally superior habitats. From early May to late August 2007, we tracked 22 Common Musk Turtles with temperature-sensitive radio-transmitters and collected daily Tb profiles with automated radio-telemetry data loggers. In addition, temperature data loggers were placed in the study area to measure the range of environmental operative temperatures (Te) available to musk turtles. The habitats with the highest thermal quality were aquatic habitats with surface cover (i.e., lily pads, macrophytes, etc.) followed by shallow water. As expected, musk turtles used habitats non-randomly and had a strong preference for thermally superior habitats. This is consistent with the typical aquatic basking behaviour observed in musk turtles, suggesting that there is a strong link between thermal quality of habitats and habitat selection, even in this almost entirely aquatic turtle.
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Crews, Sarah C., Erika L. Garcia, Joseph C. Spagna, Matthew H. Van Dam i Lauren A. Esposito. "The life aquatic with spiders (Araneae): repeated evolution of aquatic habitat association in Dictynidae and allied taxa". Zoological Journal of the Linnean Society 189, nr 3 (17.12.2019): 862–920. http://dx.doi.org/10.1093/zoolinnean/zlz139.

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Abstract Despite the dominance of terrestriality in spiders, species across a diverse array of families are associated with aquatic habitats. Many species in the spider family Dictynidae are associated with water, either living near it or, in the case of Argyroneta aquatica, in it. Previous studies have indicated that this association arose once within the family. Here we test the hypothesis of a single origin via the broadest phylogeny of dictynids and related ‘marronoids’ to date, using several taxa that were not previously sampled in molecular analyses to provide the first quantitative test of the hypothesis put forth by Wheeler et al. (2016). We sampled 281 terminal taxa from 14 families, assembling a matrix with 4380 total base pairs of data from most taxa. We also assembled an atlas of morphological traits with potential significance for both ecology and taxonomy. Our resulting trees indicate that an aquatic habitat association has arisen multiple times within dictynids. Dictynidae and the genus Dictyna are polyphyletic and the genera Lathys and Cicurina remain unplaced. A review of aquatic habitat associations in spiders indicates that it occurs in members of at least 21 families. With our morphological atlas, we explore characters that have been implicated in aiding an aquatic lifestyle, which in the past may have caused confusion regarding taxon placement. Our results indicate that not all spiders with traits thought to be useful for aquatic habitat associations occupy such habitats, and that some spider taxa lacking these traits are nonetheless associated with water.
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Alho, CJR, G. Camargo i E. Fischer. "Terrestrial and aquatic mammals of the Pantanal". Brazilian Journal of Biology 71, nr 1 suppl 1 (kwiecień 2011): 297–310. http://dx.doi.org/10.1590/s1519-69842011000200009.

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Different works have registered the number of mammal species within the natural habitats of the Pantanal based on currently known records, with species richness ranging from 89 to 152 of annotated occurrences. Our present list sums 174 species. However, at least three factors have to be emphasised to deal with recorded numbers: 1) to establish the ecotone limit between the floodplain (which is the Pantanal) and its neighbouring domain like the Cerrado, besides the existence of maps recently produced; 2) the lack of intensive surveys, especially on small mammals, rodents and marsupials; and 3) the constant taxonomic revision on bats, rodents and marsupials. Some species are very abundant - for example the capybara Hydrochoerus hydrochaeris and the crab-eating fox Cerdocyon thous, and some are rare, and others are still intrinsically rare - for example, the bush dog Speothos venaticus. Abundance of species is assumed to reflect ecological resources of the habitat. Local diversity and number of individuals of wild rodents and marsupials also rely on the offering of ecological resources and behavioural specialisation to microhabitat components. A large number of species interact with the type of the vegetation of the habitat, by means of habitat selection through active patterns of ecological behaviour, resulting on dependency on arboreal and forested habitats of the Pantanal. In addition, mammals respond to seasonal shrinking-and-expansion of habitats due to flooding regime of the Pantanal. The highest number of species is observed during the dry season, when there is a considerable expansion of terrestrial habitats, mainly seasonally flooded grassland. Major threats to mammal species are the loss and alteration of habitats due to human intervention, mainly deforestation, unsustainable agricultural and cattle-ranching practices, which convert the natural vegetation into pastures. The Pantanal still harbours about a dozen of species officially listened as in danger.
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Arvisais, Martin, Esther Lévesque, Jean-Claude Bourgeois, Claude Daigle, Denis Masse i Jacques Jutras. "Habitat selection by the wood turtle (Clemmys insculpta) at the northern limit of its range". Canadian Journal of Zoology 82, nr 3 (1.03.2004): 391–98. http://dx.doi.org/10.1139/z04-012.

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We characterized the chronology of habitat use by the wood turtle, Clemmys insculpta (LeC., 1829), in the Mauricie region of Quebec, Canada. We also determined if this species used habitats according to availability within a home range and identified habitat features influencing habitat selection. Habitats were characterized for 20 wood turtles followed weekly by telemetry during the active season of 1997. Turtles used a great diversity of terrestrial and aquatic habitats. Alder (Alnus rugosa (Du Roi) Spreng.) stands were the most used terrestrial habitats throughout the active season. Habitat use varied according to activity period. Indeed, wood turtles used aquatic habitats and alder stands during prenesting and prehibernation activity periods, whereas all habitat types were used during nesting and postnesting activity periods. Wood turtles did not use habitats randomly within their home ranges, suggesting that they selected them. Wood turtles seemed to select mixed forest stands that were relatively young (16 years), short (1–4 m), had low arborescent cover (25%), moderate cover of the upper shrub layer (35%), and low total canopy closure (0%–50%). This knowledge will be helpful in the establishment of future conservation measures.
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Rozprawy doktorskie na temat "Aquatic habitats"

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Beier, Sara. "Bacterial Degradation and Use of Chitin in Aquatic Habitats". Doctoral thesis, Uppsala universitet, Limnologi, 2010. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-131128.

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Chitin belongs to the most abundant biopolymers on earth where it has an important role as a structural element in crustaceans, insects, fungi and some phytoplankton. Missing evidence for long-term accumulation of chitin in nature implies fast turnover and as chitin is composed of aminosugar subunits it holds central roles in both carbon and nitrogen cycles. The aim of this thesis was to contribute to a better understanding of organic matter cycling by learning more about the diversity, function and ecology of bacteria that degrade chitin. A metagenome-enabled study of the spatial distribution of chitinolytic bacteria in aquatic ecosystems identified salinity as the major environmental factor for shaping their community composition. To address the role of alternative environmental variables controlling chitinolytic communities, a temporally resolved study was completed in a dimictic freshwater lake. Pronounced seasonal change in the indigenous chitinolytic community was observed and parallel measured environmental parameters pointed to the availability and crystalline form of chitin as significant controlling factors.  The different ecological niches occupied by microbes that utilize chitin for growth were studied in an experimental study. Single-cell quantification of chitinolytic cells and cells incorporating chitin hydrolysis products suggested that commensal use of chitin hydrolysis products without simultaneous chitinase activity could be an important ecological strategy in freshwater bacterioplankton communities. Members of the ubiquitous and often quantitatively dominant group of freshwater Actinobacteria Ac1 were identified as particularly active in this “cheater” lifestyle. Further experiments based on artificially created gradients in bacterial diversity demonstrated the importance of specific bacterial populations and community composition rather than overall community richness in controlling more specific functions such as chitin and cellulose degradation. To conclude, results of this thesis provide insight into the biogeography, niche-separation and species interactions of the functional community of chitin degraders and the influence of general bacterial diversity to the respective system functioning.
Felaktigt tryckt som Digital Comprehensive Summaries of Uppsala Dissertations from the Faculty of Science and Technology 700
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Welsh, Daniel. "Selenium in aquatic habitats at Cibola National Wildlife Refuge". Diss., The University of Arizona, 1992. http://hdl.handle.net/10150/186067.

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I studied selenium contamination at Cibola National Wildlife Refuge (Cibola NWR) in the lower Colorado River Valley, California and Arizona. My objectives were to: (1) determine whether local irrigation practices resulted in exposure of fish to toxic levels of selenium; (2) assess the risks to humans of consuming fish from Cibola NWR; (3) assess whether diversity and abundance of fish were related to selenium concentrations or other water quality variables. Water, sediment, fish, crayfish, and aquatic plants were collected from sites which received irrigation return flows and sites which did not. Selenium was below toxic levels at sites receiving irrigation return flows. Selenium was at the toxicity threshhold for fish at two sites receiving water directly from the Colorado River. Concentrations of selenium in fillets of largemouth bass (Micropterus salmoides) from one lake exceeded levels that elicit consumption advisories in California. Most people would be unlikely to consume toxic amounts of fish, but an advisory should be posted to inform people about potential risks. Gill nets were used to determine species diversity and abundance. There were no strong correlations between selenium levels and indices of species richness and equitability. There was a consistent inverse relationship between selenium levels and catch-per-unit-effort for all species combined. This inverse relationship suggested that selenium may be one of a suite of factors limiting abundance of fish. Correlations between indices of species diversity and abundance and values of water quality variables generally were not significant. Temperature and salinity may have limited abundance of some species seasonally. Increases in selenium levels at sites that are already at the toxicity threshhold could impair reproduction of sensitive species. Population declines and concern about edibility of fish could impair the recreational fishery. Therefore, site-specific ways to reduce selenium accumulation should be studied and implemented. Site-specific limnological conditions may play a role in accumulation of selenium to toxic levels, but major sources of selenium appear to be upstream in the Colorado River basin rather than local agricultural practices. Therefore, selenium input to the Colorado River from sources throughout the basin should be monitored and reduced where possible.
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Lusk, Joel David 1963. "Selenium in aquatic habitats at Imperial National Wildlife Refuge". Thesis, The University of Arizona, 1993. http://hdl.handle.net/10150/278391.

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During 1991 and 1992, I studied environmental contamination of the aquatic communities at Imperial National Wildlife Refuge on the lower Colorado River. I collected composite samples of sediment, detritus, aufwuchs, aquatic plants, invertebrates, and fishes from 2 river sites, 5 backwater lakes, and 2 seepage lakes. Selenium concentrations (μg/g, dry weight) were elevated in sediment (geometric mean = 0.93, range = none detected (ND) to 4.1); detritus (4.50, 0.4-27.4); aufwuchs (4.85, 2.6-10.2); Najas marina (5.66, ND-21.0); Corbicula spp. (10.54, 5.8-26.5); Procambarus clarkii (7.70, 1.5-35.8); whole fishes (6.70, 1.6-17.2); and fish fillets (9.72, 5.8-22.6). Ninety-four percent of whole fishes and invertebrates (n = 185) contained concentrations of selenium that exceeded 3 μg/g, a concentration recommended by the U.S. Fish and Wildlife Service to protect aquatic birds from chronic selenium toxicity. Biological samples from seepage lakes had significantly lower (p ≤ 0.05) selenium levels than similar samples from backwater lakes. Selenium is incorporated into plants in backwater lakes and enters consumers primarily through the detrital food web.
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Gaertner, James P. "Detection of salmonellae in wild turtles and their aquatic habitats /". View online, 2007. http://ecommons.txstate.edu/bioltad/3.

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Hopson, Adrienne M. "Impacts of Anthropogenic Noise on Aquatic Invertebrates in Wetland Habitats". Kent State University / OhioLINK, 2019. http://rave.ohiolink.edu/etdc/view?acc_num=kent15645874111271.

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Pohe, Stephen Robert. "Aquatic invertebrate fauna of Matapouri, Northland". Click here to access this resource online, 2008. http://hdl.handle.net/10292/425.

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A study of the aquatic invertebrate communities from two locations (Location 1 and Location 2) within the Matapouri catchment in Northland, New Zealand, was conducted to assess community structure in differing local-scale habitats. Four data collection methods were utilised generating 33,058 adult or larval invertebrates. The sampling methods comprised benthic kick-sampling, sticky trapping, light trapping, and emergence trapping. For the sticky trapping and light trapping, sampling was carried out at three different sites (Sites 1–3) within each location. The sites were situated within three habitat types; native forest, native forest-fringe, and raupo wetland. Emergence trapping also commenced within the three sites, at both locations, but was discontinued after two months, due to the equipment being destroyed by consecutive flooding events (method described in Appendix 1). Benthic sampling was carried out within the Forest and Forest-fringe habitats. Benthic sampling, sticky trapping, and light trapping were carried out following a monthly schedule between June and November 2005. Conductivity, pH, and water temperature measurements were taken concurrently with benthic sampling on a monthly basis, while water velocity and substrate measurements were taken once to assist in habitat characterisation. Overall, 71 taxa were recorded by benthic sampling over the six month period, with a mean of approximately 30 taxa per site per month. In comparison with similar studies elsewhere in New Zealand, a figure of around 30 taxa per sample was high. The benthic macroinvertebrate fauna at all sites was dominated by Trichoptera (19 taxa), Diptera (16 taxa) and Ephemeroptera (10 taxa). This pattern of diversity is similar to that reported in other New Zealand studies. However, in contrast to previous studies, the leptophlebiid mayfly genus Deleatidium was not numerically dominant over the rest of the community, and other leptophlebiid genera (Acanthophlebia, Atalophlebioides, Mauiulus and Zephlebia) were equally represented, possibly reflecting niche partitioning between the groups. The genus Nesameletus was not recorded at any site, despite being one of the core mayfly species in New Zealand streams. The rare mayfly Isothraulus abditus was recorded at one of the forest locations. There are no published records of this species from Northland. Although acknowledged as another of the core New Zealand benthic taxa, the hydropsychid caddisfly Aoteapsyche was not recorded during the study. However, another hydropsychid, Orthopsyche, was commonly recorded, and these may be filling a similar niche to the Aoteapsyche genus. In contrast to the Trichoptera, Diptera, and Ephemeroptera, the Plecoptera fauna was relatively depauperate, probably reflecting the warmer climate of the region and lack of temperature-buffered spring-fed streams. Surprisingly, Zelandobius, a core New Zealand genus, was absent but is regularly recorded in Northland. A species of conservation interest, Spaniocercoides watti, currently recognised as a Northland endemic, was recorded in low numbers. There were no apparent trends in diversity or abundance of benthic invertebrates over time. Also, there were no significant differences in species diversity between the two locations. However, in many cases, taxa were more abundant at Location 2. This may have been due to steeper gradients at Location 2, and the consequent effects on substrate size and streambed stability, as all other physical factors appeared similar between locations. Although several significant differences of individual benthic taxa were recorded, no broad effect of habitat (sites) on species diversity was observable. However, at Location 2, abundances were significantly higher at Site 3 (Forest) compared to Site 2 (Forest-fringe). The reasons were uncertain, but may be attributed to higher retention of allochthonous organic materials, trapped by in-stream cover and larger substrates. Investigations of adult stages by sticky traps supported benthic results recording community compositions and abundances dominated by Trichoptera and Diptera. Plecoptera were poorly represented. Location 2 recorded higher abundances of taxa, particularly Ephemeroptera and Plecoptera. Investigations of adult stages by light traps however did not produce any statistically significant differences in abundances between sites, between locations, or between sites across locations, and it is believed to be due to limited sampling replication combined with some biases of light trapping. This study indicates that the aquatic invertebrate community at Matapouri is diverse but also reasonably representative. Several rare or uncommon insects inhabit the catchment. It is therefore important that Iwi and the local Landcare Group, who invited and supported this research, together with the Department of Conservation, continue their efforts in protecting these areas. The resident fauna have the capacity to restock areas downstream, which are intended to be improved and restored through sediment control and riparian management.
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Kiesel, Jens [Verfasser]. "Ecohydrologic and hydraulic stream modelling to describe aquatic habitats / Jens Kiesel". Kiel : Universitätsbibliothek Kiel, 2014. http://d-nb.info/1053653484/34.

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Lott, Derek Arthur. "The semi-aquatic habitats of terrestrial Coleoptera in a lowland river floodplain". Thesis, University of Newcastle upon Tyne, 1999. http://hdl.handle.net/10443/3632.

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281 species of terrestrial ground-living beetles were recorded from 69 riparian and wetland sites in the floodplain of the lowland River Soar, England. Differences in species composition between pitfall trapped and timed hand-collected samples were smaller than those attributable to environmental and seasonal factors. Detrended Correspondence Analysis consistently ranked all sites against seasonal variations between April and June and floodplain sites against annual variations. DCA axis 1 scores were slightly better correlated with important environmental variables at the ecohabitat (<5Om) scale rather than the microhabitat scale. Canonical Correspondence Analysis detected assemblage responses to flooding disturbance and grazing pressure along the main channel as well as to water level stability in the floodplain. A conceptual model of floodplain land-use and river management postulated a dynamic equilibrium between flooding disturbances and vegetational succession, producing geomorphic and vegetational structures which serve as semi-aquatic habitats for terrestrial beetle assemblages with appropriate species traits. Impoundment for navigation affects assemblages by modifying the severity of flooding disturbance. The effects of grazing pressure resemble flooding disturbance. The short-term (< 5yr) impact of bank regrading was explained by differences in severity, predictability and frequency compared to the beetles' generation length. Evenness and species richness were affected only by flooding and grazing disturbance. This response was not predicted by the intermediate disturbance hypothesis because the frequencies of flooding and grazing disturbances in the Soar valley are not appropriate to the hypothesis, which more closely relates to disturbance by bank regrading. In comparison to diversity indices, a rarity index was much less sensitive to environmental factors than species diversity indices and more robust against seasonal and yearly fluctuations. Consequently, it has more potential for use in site quality assessment.
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Yanoviak, Stephen P. "Community ecology of water-filled tree holes in Panama /". Full-text version available from OU Domain via ProQuest Digital Dissertations, 1999.

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Meyers, Jennifer. "Developing Non-lethal Biomarkers to Detect Exposure to Organic Contaminants in Aquatic Habitats". Fogler Library, University of Maine, 2009. http://www.library.umaine.edu/theses/pdf/MeyersJ2009.pdf.

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Książki na temat "Aquatic habitats"

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K, Koski, Hauser William Joseph 1942-, United States. Environmental Protection Agency i American Fisheries Society, red. Aquatic habitat restoration in northern ecosystems. [Anchorage, Alaska?: U.S. Environmental Protection Agency?], 1997.

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Eder, David L. Aquatic animals: Biology, habitats, and threats. Hauppauge, N.Y: Nova Science Publisher's, 2011.

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Snowball, Diane. Exploring freshwater habitats. Greenvale, N.Y: Mondo Pub., 1994.

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Barrett, Katharine. Aquatic habitats: Exploring desktop ponds : teacher's guide. Berkeley, CA: Lawrence Hall of Science, University of California at Berkeley, 1998.

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M, Crawford R. M., i Spence, David Hugh Neven, 1925-1985., red. Plant life in aquatic and amphibious habitats. Oxford [Oxfordshire]: Blackwell Scientific Publications, 1987.

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Bradley, Florentin C., United States. Army. Corps of Engineers., U.S. Army Engineer Waterways Experiment Station., Environmental Laboratory (U.S. Army Engineer Waterways Experiment Station) i Environmental Impact Research Program, red. Low-flow aquatic habitat restoration evaluation, the RCHARC Methodology, Goose Creek, Colorado. Vicksburg, Miss: U.S. Army Engineer Waterways Experiment Station, 1997.

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R, Peters Mitchell, United States. Army. Corps of Engineers., U.S. Army Engineer Waterways Experiment Station., Environmental Laboratory (U.S. Army Engineer Waterways Experiment Station) i Environmental Impact Research Program (U.S.), red. Low-flow habitat rehabilitation-evaluation, RCHARC methodology, Rapid Creek, South Dakota. [Vicksburg, Miss: U.S. Army Engineer Waterways Experiment Station, 1996.

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Eric, Archer, i Rocky Mountain Research Station (Fort Collins, Colo.), red. Testing common stream sampling methods for broad-scale, long-term monitoring. Fort Collins, CO: U.S. Dept. of Agriculture, Forest Service, Rocky Mountain Research Station, 2004.

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Sparks, Richard E. Des Plaines River long-term monitoring program: Phase I report. [Champaign], Ill: Illinois Natural History Survey Aquatic Biology Section, 1986.

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Busch, W. D. N. Development of an aquatic habitat classificationsystem for lakes. Boca Raton: CRC Press, 1992.

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Części książek na temat "Aquatic habitats"

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Koroiva, Ricardo, i Mateus Pepinelli. "Distribution and Habitats of Aquatic Insects". W Aquatic Insects, 11–33. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-16327-3_2.

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Chadd, Richard. "Assessment of Aquatic Invertebrates". W Biological Monitoring in Freshwater Habitats, 63–72. Dordrecht: Springer Netherlands, 2009. http://dx.doi.org/10.1007/978-1-4020-9278-7_7.

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Hagler, Allen N., Leda C. Mendonça-Hagler i Fernando C. Pagnocca. "Yeasts in Aquatic Ecotone Habitats". W Yeasts in Natural Ecosystems: Diversity, 63–85. Cham: Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-62683-3_2.

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Swanson, George A. "Aquatic Habitats of Breeding Waterfowl". W The Ecology and Management of Wetlands, 195–202. New York, NY: Springer US, 1988. http://dx.doi.org/10.1007/978-1-4684-8378-9_16.

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Swanson, George A. "Aquatic Habitats of Breeding Waterfowl". W The Ecology and Management of Wetlands, 195–202. Boston, MA: Springer US, 1988. http://dx.doi.org/10.1007/978-1-4684-7392-6_16.

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Joyner-Matos, Joanna, i David Julian. "Oxidative Stress in Sulfidic Habitats". W Oxidative Stress in Aquatic Ecosystems, 99–114. Chichester, UK: John Wiley & Sons, Ltd, 2011. http://dx.doi.org/10.1002/9781444345988.ch7.

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Kelly, Andrea, i Jane Harris. "Aquatic Plant Monitoring in the Broads". W Biological Monitoring in Freshwater Habitats, 261–76. Dordrecht: Springer Netherlands, 2009. http://dx.doi.org/10.1007/978-1-4020-9278-7_24.

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Pandey, Abha, Sonal Mishra, Neha Kumari, Vidya Singh i Rajeshwar P. Sinha. "Pollution Affecting Cyanobacteria in Aquatic Habitats". W Anthropogenic Pollution of Aquatic Ecosystems, 11–37. Cham: Springer International Publishing, 2021. http://dx.doi.org/10.1007/978-3-030-75602-4_2.

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Gopal, Brij. "Indian subcontinent and the aquatic habitats". W Ecology and management of aquatic vegetation in the Indian subcontinent, 7–28. Dordrecht: Springer Netherlands, 1990. http://dx.doi.org/10.1007/978-94-009-1984-6_2.

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Benedetti-Cecchi, Lisandro. "Plant Succession in Littoral Habitats". W Modern Trends in Applied Aquatic Ecology, 97–131. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-1-4615-0221-0_5.

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Streszczenia konferencji na temat "Aquatic habitats"

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"Modelling habitat suitability under hydrological change in aquatic habitats of northern Australia". W 25th International Congress on Modelling and Simulation. Modelling and Simulation Society of Australia and New Zealand, 2023. http://dx.doi.org/10.36334/modsim.2023.stratford.

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Nitta, Masayuki, Muneyuki Aoki i Mitsuru Ohira. "Assessing River Environments for Aquatic Habitats and Recreational Use". W 40th IAHR World Congress - "Rivers � Connecting Mountains and Coasts". Spain: The International Association for Hydro-Environment Engineering and Research (IAHR), 2013. http://dx.doi.org/10.3850/978-90-833476-1-5_iahr40wc-p0298-cd.

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Tubić, Bojana, Nataša Popović, Ana Atanacković, Katarina Zorić, Jelena Tomović, Momir Paunović i Nikola Marinković. "AQUATIC MACROINVERTEBRATE DIVERSITY OF RIBNICA RIVER (THE KOLUBARA BASIN)". W 53rd Annual Conference of the Serbian Water Pollution Control Society. SERBIAN WATER POLLUTION CONTROL SOCIETY, 2024. http://dx.doi.org/10.46793/voda24.137t.

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The aim of the study of the aquatic macroinvertebrate community of the Ribnica River is to provide a starting point for assessing the impact on the diversity of the community and defining protective measures during the construction of the "Struganik" dam on the Ribnica River. The material was collected in seven sites in 2019 and 2022. Macroinvertebrates community with a dominance of insect groups, is typical and reflects the preserved habitats of the studied river. A total of 121 taxa from 12 taxonomic groups were recorded. Four species protected by national and/or international legislation were recorded. The dam construction could lead to habitat changes, but would not significantly affect the population of protected species as they would move to the upstream parts of the river and tributaries.
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Turpie, Kevin, Steven Ackleson, Thomas Bell, Heidi Dierssen, James Goodman, Robert Green, Liane Guild i in. "Spectroscopy for global observation of coastal and inland aquatic habitats". W 2017 IEEE International Geoscience and Remote Sensing Symposium (IGARSS). IEEE, 2017. http://dx.doi.org/10.1109/igarss.2017.8127642.

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Kim, Jongho, April Warnock, Valeriy Ivanov, Nikolaos Katopodes i Paul Webb. "Impact of Climate and Land Use Changes on Aquatic Habitats". W Watershed Management Conference 2010. Reston, VA: American Society of Civil Engineers, 2010. http://dx.doi.org/10.1061/41143(394)8.

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Nikookar, Seyed Hassan. "Ecology and coexistence ofAnopheleslarvae in aquatic habitats in Mazandaran Province, northern Iran". W 2016 International Congress of Entomology. Entomological Society of America, 2016. http://dx.doi.org/10.1603/ice.2016.112047.

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Telat, Yanik, Yanik Telat, Aslan Irfan i Aslan Irfan. "EFFECTS OF GLOBAL WARMING AND ANTHROPOGENIC FACTORS ON AQUATIC LIFE". W XXVII International Shore Conference "Arctic Coast: The Path to Sustainability". Academus Publishing, 2019. http://dx.doi.org/10.31519/conferencearticle_5cebbc14abe349.69831818.

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Based on the assumptions of many researchers, global warming and anthropogenic factors such as pollution, transporting and trading, as well as invasionism, lessepsianism, endangerism effect negatively and will continue to effect aquatic populations and their existence in the ecosystem and related habitats. Thus, it may be stated that climate warming and anthropogenic factors will certainly cause extinction of some aquatic organisms as well as fish species in the end, by 2080 or 2100. Considering economic impacts of losing some species, the new areas of fishing should be decided to sustain current needs of human and food industry. In this paper, the effects of global warming, natural and anthropogenic factors affecting aquatic life were discussed by using the data from various reports.
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Drayer, Gregorio, i Ayanna Howard. "Educational Value of Experiments on Life Support Systems with Ground-Based Aquatic Habitats". W 42nd International Conference on Environmental Systems. Reston, Virigina: American Institute of Aeronautics and Astronautics, 2012. http://dx.doi.org/10.2514/6.2012-3568.

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Pandey, Ayoni, Nivedita Rai, Shivendra Mani Tripathi i Sudhanshu Mishra. "Pharmaceutical Waste: Risks & Challenges Faced by Aquatic Ecosystem". W International Conference on Frontiers in Desalination, Energy, Environment and Material Sciences for Sustainable Development & Annual Congress of InDA. AIJR Publisher, 2023. http://dx.doi.org/10.21467/proceedings.161.17.

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Pharmaceutical industries are experiencing a steady increase in both their numbers and demands, leading to a significant rise in the amount of waste they generate. This waste comprises various components such as organic compounds, excipients, and plastic containers. Unfortunately, a major portion of this waste is discharged into aquatic bodies through pipes, eventually reaching canal systems and ultimately the seas. This practice poses a severe threat to aquatic life, as it significantly impacts their habitat in a hazardous manner. One of the primary deleterious effects caused by pharmaceutical waste discharge is the elevation of the Biological Oxygen Demand (BOD) in the affected aquatic areas. This increase in BOD results in reduced oxygen availability for aquatic creatures, leading to mortality and ultimately causing a disruption in the natural balance of the ecosystem. Moreover, the accumulation of organic compounds from pharmaceutical waste leads to eutrophication, which accelerates the aging process of lakes, ultimately converting them into land. Another harmful consequence is biomagnification, wherein the concentration of toxicants increases as they move up the food chain through successive trophic levels. The continuous contamination of aquatic ecosystems by industrial waste is exacerbating the degradation of these fragile environments. However, the growing recognition of this issue has prompted research and implementation of various water treatment methods. These methods aim to mitigate the degradation rate and protect aquatic ecosystems from further harm. By employing advanced treatment techniques, it is possible to reduce the negative impact of pharmaceutical waste discharge and preserve the integrity of aquatic ecosystems. Efforts must be made to raise awareness among pharmaceutical industries about the importance of responsible waste management. By adopting sustainable practices and investing in environmentally friendly technologies, such as improved waste disposal systems and more efficient water treatment methods, the industry can significantly reduce its ecological footprint. Collaboration between regulatory bodies, environmental organizations, and pharmaceutical companies is essential to address this pressing issue effectively. With concerted efforts and a collective commitment to environmental stewardship, it is possible to mitigate the detrimental effects of pharmaceutical waste on aquatic ecosystems and safeguard the future of our planet's delicate aquatic habitats.
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Jägerbrand, A., A. Brutemark i P. Andersson. "ASSESSING THE USE OF ENVIRONMENTAL LIGHTING ZONES FOR THE PROTECTION OF AQUATIC NATURE CONSERVATION AREAS". W CIE 2023 Conference. International Commission on Illumination, CIE, 2023. http://dx.doi.org/10.25039/x50.2023.po021.

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Anthropogenic light can have adverse effects on species and ecosystems, effects that are numerous and challenging to anticipate due to their high variability and complexity. In this study our objective was to investigate the feasibility of utilising environmental lighting zones for the management of aquatic Natura 2000 conservation areas. The aim of the Natura 2000 network is to ensure the long-term survival of Europe's most valuable and threatened species and habitats. Maintaining a favourable conservation status and sustainable management of these habitats is of utmost importance, necessitating the avoidance of negative impacts of human activities, including anthropogenic light. Our preliminary findings indicate that employing a relatively high number of environmental lighting zones intervals is essential for effective implementation of mitigation measures. This approach facilitates the identification of protected areas experiencing the highest levels of light emissions, aiding in targeted conservation efforts.
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Raporty organizacyjne na temat "Aquatic habitats"

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Abbott, Katherine, Allison H. Roy i Keith Nislow. Restoring aquatic habitats through dam removal. U.S. Fish and Wildlife Service, listopad 2022. http://dx.doi.org/10.3996/css92498424.

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Russ, Emily, Amy Yarnall i Safra Altman. Dredged material can benefit submerged aquatic vegetation (SAV) habitats. Engineer Research and Development Center (U.S.), sierpień 2023. http://dx.doi.org/10.21079/11681/47423.

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This technical note (TN) was developed by the US Army Engineer Research and Development Center–Environmental Laboratory (ERDC-EL) to provide an overview of the ecosystem services delivered by submerged aquatic vegetation (SAV) to estuarine and coastal ecosystems and to describe potential methods for the beneficial use of dredged material (BUDM) to aid in SAV restoration. Although dredging tends to have a negative association with SAV habitats, BUDM may provide an opportunity to expand suitable SAV habitat to areas where depth is the primary limiting factor. Recent in situ observations have shown that SAV has opportunistically colonized several dredged-material placement sites. This TN provides context on BUDM for SAV habitat restoration to encourage increased strategic placement.
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Eisemann, Eve, Catherine Thomas, Matthew Balazik, Damarys Acevedo-Mackey i Safra Altman. Environmental factors affecting coastal and estuarine submerged aquatic vegetation (SAV). Engineer Research and Development Center (U.S.), październik 2021. http://dx.doi.org/10.21079/11681/42185.

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Submerged aquatic vegetation (SAV) growing in estuarine and coastal marine systems provides crucial ecosystem functions ranging from sediment stabilization to habitat and food for specific species. SAV systems, however, are sensitive to a number of environmental factors, both anthropogenic and natural. The most common limiting factors are light limitation, water quality, and salinity, as reported widely across the literature. These factors are controlled by a number of complex processes, however, varying greatly between systems and SAV populations. This report seeks to conduct an exhaustive examination of factors influencing estuarine and coastal marine SAV habitats and find the common threads that tie these ecosystems together. Studies relating SAV habitats in the United States to a variety of factors are reviewed here, including geomorphological and bathymetric characteristics, sediment dynamics, sedimentological characteristics, and water quality, as well as hydrologic regime and weather. Tools and methods used to assess each of these important factors are also reviewed. A better understanding of fundamental environmental factors that control SAV growth will provide crucial information for coastal restoration and engineering project planning in areas populated by SAVs.
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Bryant, M. D. The Copper River Delta pulse study: an interdisciplinary survey of aquatic habitats. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 1991. http://dx.doi.org/10.2737/pnw-gtr-282.

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Schad, Aaron, Daniel Allen, Lynde Dodd, Ricardo Luna, Jacob Kelly, Kristina Hellinghausen, Nathan Harms, Gary Dick i Yaretzy Charo. Aquatic ecosystem restoration in the Texas Western Gulf Coast Plain / Lower Rio Grande alluvial floodplain ecoregion : Resaca Boulevard Resaca Section 206—vegetation community adaptive management. Engineer Research and Development Center (U.S.), wrzesień 2023. http://dx.doi.org/10.21079/11681/47559.

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As part of the US Army Corps of Engineers (USACE) Continuing Authorities Program (CAP), Section 206 projects focus on restoring aquatic habitats for the benefit of fish and other wildlife. From 2017–2021, USACE Engineer Research and Development Center–Environmental Laboratory researchers in the Aquatic Ecology and Invasive Species Branch (ERDC-EL EEA) at the Lewisville Aquatic Ecosystem Research Facility (LAERF) collaborated with USACE Galveston District, The Nature Conservancy, US Fish and Wildlife Service, National Park Service, and local nonfederal sponsors—Brownsville (Texas) Public Utility Board and the City of Brownsville—to study restoration methods on former, naturally cut-off, channels of the Lower Rio Grande River. These aquatic ecosystems, locally termed “resacas,” are home to endemic plants and animals and are thus an important natural resource of national interest. This technical report documents the planning, design, construction, monitoring, and adaptive management activities throughout the Resaca Boulevard Resaca Section 206 Aquatic Ecosystem Restoration project. Methods and results for invasive species management—primarily Brazilian peppertree (Schinus terebinthfolia)—and aquatic and riparian vegetation establishment in endemic Texas ebony resaca forest, subtropical Texas palmetto woodland, and Texas ebony/snake-eyes shrubland habitats are discussed.
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Bryant, M. D. Past and present aquatic habitats and fish populations of the Yazoo-Mississippi Delta. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station, 2010. http://dx.doi.org/10.2737/srs-gtr-130.

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Bryant, M. D. Past and present aquatic habitats and fish populations of the Yazoo-Mississippi Delta. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station, 2010. http://dx.doi.org/10.2737/srs-gtr-130.

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Everest, Fred H., i Gordon H. Reeves. Riparian and aquatic habitats of the Pacific Northwest and southeast Alaska: ecology, management history, and potential management strategies. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 2007. http://dx.doi.org/10.2737/pnw-gtr-692.

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Miller, James E. Muskrats. U.S. Department of Agriculture, Animal and Plant Health Inspection Service, styczeń 2018. http://dx.doi.org/10.32747/2018.7208744.ws.

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The muskrat (Ondatra zibethicus) is a common, semi-aquatic rodent native to the United States. It spends its life in aquatic habitats and is well adapted for swimming. Although muskrats are an important part of native ecosystems, their burrowing and foraging activities can damage agricultural crops, native marshes and water control systems, such as aquaculture and farm ponds and levees. Such damage can significantly impact agricultural crops like rice that rely on consistent water levels for growth. Laws, regulations, and ordinances regarding the take of muskrats varies by state and province where they are found and regulations on seasons, bag limits, and type of traps or devices that can be used to take them must be carefully followed.
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Wehrly, Kevin E., Edward S. Rutherford, Lizhu Wang, Jason Breck, Lacey Mason i Scott Nelson. Development of a Geographic Information System-Based Decision Support Tool for Evaluating Windfarm Sitings in Great Lakes Aquatic Habitats. Office of Scientific and Technical Information (OSTI), lipiec 2011. http://dx.doi.org/10.2172/1303492.

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