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Ecosystems characterization

According to the creators, USEtox provides a parsimonious and transparent tool for human health and ecosystem characterization factor (CF) estimates. It has been carefully constructed as well as evaluated via comparison with other models and falls within the range of their results while being less complex. [Pg.101]

Ecosystem characterization Long-term monitoring should continue in order to enable estimation of natural variability, as well as to establish a baseline against which to evaluate the effects of disturbances. Standard environmental risk assessment approaches may not be useful if the components of the ecosystem in question have not been determined. Further research on... [Pg.24]

Assessment end points directly influence the type, characteristics, and interpretation of data and information used for analysis and the scale and character of the assessment. For example, an assessment end point such as fecundity of bivalves defines local population characteristics and requires very different types of data and ecosystem characterization compared with aquatic community structure and function. When concerns are on a local scale, the assessment end points should not focus on landscape concerns. But if ecosystem processes and landscape patterns are being considered, survival of a single species would provide inadequate representation of this larger scale. [Pg.505]

The marine environment is a vast resource for the discovery of structurally unique bioactive secondary metabolites, some belonging to totally novel chemical classes.8 Sessile benthic organisms including the Porifera, Cnidaria, Bryozoa, and Tunicata as well as marine algae have developed an arsenal of compounds which have been demonstrated to confer a competitive advantage in ecosystems characterized by extreme resource limitations. Interactions of these organisms at the genetic,... [Pg.523]

Buzzelli, C.P. (1998) Simulation modeling of littoral zone habitats in lower Chesapeake Bay. I. An ecosystem characterization related to model development. Estuaries 21, 659-672. [Pg.556]

During ecosystem characterization, the ecological context of the assessment is further analyzed. In particular, the spatial and temporal distributions of the ecological component are characterized, and the ecosystem attributes that influence the distribution and nature of the stressor are considered. [Pg.447]

The spatial and temporal distributions of ecological components also are considered in ecosystem characterization. Characteristics of ecological components that influence their exposure to the stressor are evaluated, including habitat needs, food preferences, reproductive cycles, and seasonal activities such as migration and selective use of resources. Spatial and temporal variations in the distribution of the ecological component (e.g., sediment invertebrate distribution) may complicate evaluations of exposure. When available, species-specific information about activity patterns, abundance, and life histories can be very useful in evaluating spatial and temporal distributions. [Pg.448]

Discuss the main links of the biogeochemical food web in aquatic ecosystems. Characterize the interplay between terrestrial and aquatic links of biogeochemical cycles. Give examples. [Pg.354]

The evolution of the business ecosystem provides a framework for considering the strategies and relationships in the value networks in terms of the business life-cycle. Here the business ecosystem characterizes the opportunity and risk environment which allow different value networks and core businesses to grow and co-evolve. According to Moore (1996), this co-evolution is defined as a... [Pg.37]

A risk estimate indicates the likelihood of occurrence of the different types of health or enviromiiental effects in exposed populations. Risk assessment should include both human healtli and environmental evaluations (i.e., impacts on ecosystems). Ecological impacts include actual and potential effects on plants and animal (otlier than domesticated species). The numbers produced from the risk characterization, representing tlie probability of adverse health effects being caused, must be evaluated. [Pg.395]

The response of tundra, bogs, and moist or wet boreal forest to new climate regimes is expected to be large. Sufficient research to characterize the response of these ecosystems over the next 50 to 100 years is a high priority. [Pg.409]

Land use changes in the tropics have resulted in a landscape characterized as a mosaic of logged forests, cleared fields, and successional forests. This results in the transformation from extremely fire resistant rainforest ecosystems to anthropogenic landscapes in which fire is a common event (16, 17), Fires occur in disturbed tropical forests because deforestation has a dramatic effect on microclimate. Deforestation results in lower relative humidities, increased wind speeds, and increased air temperatures. In addition, deforestation results in increased quantities of biomass that are susceptible to fire. This biomass may be in the form of forest slash, leaf litter, grasses, lianas or herbaceous species (16, 18). [Pg.427]

The lEP provides the monitoring fi amework to characterize the status and trends of Delta aquatic ecosystems. The lEP strives to provide information on the many factors that affect ecological resorrrces in the Delta. Key near-term goals for the lEP include (1) collecting and analyzing data needed to understand factors controlling the distribution and abundance of selected fish and wildlife resources, (2)... [Pg.63]

Environmental Fate. Having characterized the entry of materials into the environment, we move into the second step of our procedure. The goal at this stage of analysis is to define ambient concentration of the material or its products in areas of concern for receptor (e.g., people, materials or ecosystem components) exposure. A family of computer simulation models has been developed for calculating the ambient levels of a... [Pg.93]

Garland JL, Mills AL (1991) Classification and characterization of heterotrophic microbial communities on the basis of patterns of community-level sole-carbon-source utilization. Appl Environ Microbiol 57 2351-2359 Giuffre L, Piccolo G, Rosell R, Pascale C, Heredia OS, Ciarlo E (2001) Anthropogenic effect on soil organic phosphorus fractions in tropical ecosystems. Commun Soil Sci Plant Anal 32 1621-1628 Gottlieb S (1976) The production and role of antibiotics in soil. J Antibiot 29 987-1000... [Pg.341]

Quantitative nature of the CLL approach. Numerical tolerable exposure levels for pollutants of concern are defined to establish quantitative thresholds for risk characterization therefore the CLL approach provides a basis for quantitative ecosystem risk and damage assessment. [Pg.15]

Critical load exceedances may serve as the basis for interpreting ecological impacts as ecological risks (or rather changes in the level of current risk to ecosystem health ). This would refer to the process of ecological risk characterization. [Pg.20]

There are a number of approaches to measuring risks depending on assessment and measurement endpoints selected. At ecosystem level, one can propose a percentage of the affected area with CLs exceeded as an acceptable quantitative parameter for ecosystem risk magnitude. In pristine areas, actual state of the environment may be taken as a reference point for risk characterization. [Pg.20]

CHARACTERIZATION OF SOIL-BIOGEOCHEMICAL CONDITIONS IN THE WORLD S TERRESTRIAL ECOSYSTEMS... [Pg.23]

With respect to soils, a receptor is thus characterized as a specific combination of land use (e g., Forest ecosystem types, agricultural crops) and soil type. The critical loads can be calculated for both agricultural soils (grassland, arable land) with HM inputs with deposition, fertilizers, and wastes, and non-agricultural (forest and steppe) soils, where atmospheric deposition is the only input to the system. [Pg.60]

With respect to aquatic ecosystems, a receptor is thus characterized as a like, a river or a sea. The major receptor that we will consider here is a lake, including catchment (see small catchment studies in Chapter 18). The reason is that the suggested models are all relatively simple and based on the assumption that the water compartment is homogeneously mixed. Much more complicated models are necessary to calculate... [Pg.61]

We can compare these values with those characterizing the fluxes of trace metals in biogeochemical cycles. The biological productivity of the Polar Tundra ecosystem grown on the low terrace in the region of Barentsberg, Spitzbergen Island, is shown in Table 5. [Pg.132]


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