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Modeling the effect of land cover land use change on estuarine environmental flowsSahoo, Debabrata 15 May 2009 (has links)
Environmental flows are important to maintain the ecological integrity of the estuary. In
a watershed, it is influenced by land use land cover (LULC) change, climate variability,
and water regulations. San Antonio, Texas, the 8th largest city in the US, is likely to
affect environmental flows to the San Antonio Bay/Guadalupe Estuary, due to rapid
urbanization.
Time series analysis was conducted at several stream gauging stations to assess trends in
hydrologic variables. A bootstrapping method was employed to estimate the critical
value for global significance. Results suggested a greater number of trends are observed
than are expected to occur by chance. Stream gauging stations present in lower half of
the watershed experienced increasing trend, whereas upper half experienced decreasing
trends. A similar spatial pattern was not observed for rainfall. Winter season observed
maximum number of trends. Wavelet analysis on hydrologic variables, suggested presence of multi-scale temporal
variability; dominant frequencies in 10 to 15 year scale was observed in some of the
hydrologic variables, with a decadal cycle. Dominant frequencies were also observed in
17 to 23 year scale with repeatability in 20 to 30 years. It is therefore important to
understand various ecological processes that are dominant in this scale and quantify
possible linkages among them.
Genetic algorithm (GA) was used for calibration of the Hydrologic Simulation Program
in FORTRAN (HSPF) model. Although, GA is computationally demanding, it is better
than manual calibration. Parameter values obtained for the calibrated model had physical
representation and were well within the ranges suggested in the literature.
Information from LANDSAT images for the years 1987, 1999, and 2003 were
introduced to HSPF to quantify the impact of LULC change on environmental flows.
Modeling studies indicated, with increase in impervious surface, peak flows increased
over the years. Wavelet analysis pointed, that urbanization also impacted storage.
Modeling studies quantified, on average about 50% of variability in freshwater inflows
could be attributed to variation in precipitation, and approximately 10% of variation in
freshwater inflows could be attributed to LULC change.
This study will help ecologist, engineers, scientist, and politicians in policy making
pertinent to water resources management.
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Modeling Land-Cover/Land-Use Change: A Case Study of a Dynamic Agricultural Landscape in An Giang and Dong Thap, VietnamHaynes, Keelin 31 July 2020 (has links)
No description available.
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LAND COVER AND STREAM BIOLOGICAL INTEGRITY IN NORTH-CENTRAL INDIANAAlexandra Ann Adams (18066691) 28 February 2024 (has links)
<p dir="ltr">The Temperate Plains ecoregion of Indiana has experienced significant agricultural development since the 19th century, which has left streams vulnerable to impacts such as sedimentation and nutrient accumulation. This thesis describes first the accuracy of the USDA Cropland Data Layer (CDL) in land cover change, and second, the relationships between agricultural and forested land covers and stream biological integrity. I first employed the CDL to review land cover change, particularly relating to agriculture and forest, for the area of interest between 2010 and 2020. I determined that the CDL improved in accuracy for the area of interest in the chosen timeframe for non-agricultural and non-forest land cover. I concluded that the CDL was best used as a supplement to primary-source land cover measures. Next, I calculated the fish Index of Biotic Integrity (IBI) scores for 20 sampled agricultural and forested streams in North-Central Indiana. I also assessed the stream habitats at all sites using the Qualitative Habitat Evaluation Index (QHEI) and percent cultivated crops in drainage basin areas for all streams. Forested streams had significantly higher QHEI scores than agricultural streams (median = 62 and 40.4, respectively). No other relationships were statistically different, including IBI and land cover category, which may have been due to the small sample size (n = 20). I concluded that future studies may build on these findings by controlling for agricultural drainage types or using precise measures of forested land cover.</p>
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