Browsing by Subject "stormwater"
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Item Performance of vegetated roadsides in removing stormwater pollutants(Texas A&M University, 2006-08-16) Rammohan, PavitraStormwater runoff from highways can contain pollutants such as suspended solids, nitrogen and phosphorus, organic material, and heavy metals. Growing awareness leading to regulatory requirements reflects the need to protect the environment from highway runoff effects. The management practice discussed in this study is the use of vegetated roadsides. The primary objective of this research is to document the potential treatment values from vegetated roadsides typical of common rural highway cross sections in two Texas cities: Austin and College Station. Three sites in each city were examined in this study over a 14-month monitoring period. No significant difference between the edges of pavement pollutant concentrations were observed at any of the research sites in the two study areas. This allowed for direct comparisons of the vegetated roadsides and their associated site characteristics such as annual daily traffic (ADT), dry period, and rainfall intensity. The scatter plots of College Station data show that concentrations of total suspended solids (TSS), total Pb, and chemical oxygen demand (COD) in runoff are dependent on the antecedent dry period and decrease with longer dry periods. The results show that pollutant concentrations are not highly dependent on ADT. However, the results show that the number of vehicles during the storm (VDS) was evaluated and accepted as a satisfactory independent variable for estimating the loads of total Pb and TSS. The results of correlation analysis show that the concentrations of total Pb and chemical oxygen demand are significantly correlated with TSS levels. The findings indicate that nitrate concentrations in runoff is most dependent on the average daily traffic using the highway during the preceding dry period as well as the duration of that dry period. Sites 2 and 3 in College Station are steeper but outperformed Site 1 which has much flatter slopes. This could be accounted for by the poor vegetative cover (brown patches) at Site 1. In the Austin sites, the permeable friction course appeared to have a significant impact on the quality of runoff leaving the road surface. On the whole, the results of this study indicate that vegetated roadsides could be used as a management practice for controlling and treating stormwater runoff from Texas highways.Item Reactive Transport Modeling of Natural Attenuation in Stormwater Bioretention Cells and Under Land Application of Wastewater(2014-04-29) Zhang, JingqiuNatural attenuation is a cost effective method to treat wastewater applied into soil. The natural attenuation process includes diffusion, dispersion, microbial activity, oxidation, mineral precipitation, sorption, and ion exchange to mitigate hydrocarbon, nutrient, metals, and solids. Vegetation also plays an important role in reducing water volume, and removing nutrients and solutes from the contaminated soil. We used a reactive transport model MIN3P-THM to simulate the natural attenuation on stormwater runoff, and oil and gas produced wastewater. In bioretention systems, the model results indicated that the bioretention systems were able to remove most of heavy metals, nitrate, and organic carbon through natural attenuation in the soil. Due to macropores and fast flow paths created by roots in vegetated cells, the water can carry ions flowing out of the system very quickly leading to a higher outflow rate and less removal efficiency than non-vegetated cells. The model also tested a range of possible design configurations to determine the optimal saturated zone thickness and outlet location for nitrate removal. In addition, different rainfall levels did influence the natural attenuation performance of bioretention cells under long time application. Due to less water and chemical input, climate patterns may lead to better removal of heavy metals. For land application of Oil and Gas Exploration and Production wastewater, five scenarios were developed to study the impact of chloride, salts, and organic matters on natural attenuation. Water and salinity stress were considered in the model to deal with high salinity wastewater in the root zone. For High-FDS and High-Cl treatments, long time application of high salinity wastewater did accumulate salts in the root zone and affect groundwater quality. Under the High-TOC treatment, TOC begins to build up in the root zone in concentrations up to 750 mg/L. More attention should be paid on long-term land application of high salinity wastewater; the application process may pollute groundwater and nearby rivers causing human health hazard. Plants would reduce water uptake to survive themselves when water and solute stress occurred under high salinity conditions.