Interaction of Ground Water and Surface Water in Different Landscapes
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The Hyporheic Handbook a Handbook on the Groundwater–Surface Water Interface and Hyporheic Zone for Environment Managers
The Hyporheic Handbook A handbook on the groundwater–surface water interface and hyporheic zone for environment managers Integrated catchment science programme Science report: SC050070 The Environment Agency is the leading public body protecting and improving the environment in England and Wales. It’s our job to make sure that air, land and water are looked after by everyone in today’s society, so that tomorrow’s generations inherit a cleaner, healthier world. Our work includes tackling flooding and pollution incidents, reducing industry’s impacts on the environment, cleaning up rivers, coastal waters and contaminated land, and improving wildlife habitats. This report is the result of research funded by NERC and supported by the Environment Agency’s Science Programme. Published by: Dissemination Status: Environment Agency, Rio House, Waterside Drive, Released to all regions Aztec West, Almondsbury, Bristol, BS32 4UD Publicly available Tel: 01454 624400 Fax: 01454 624409 www.environment-agency.gov.uk Keywords: hyporheic zone, groundwater-surface water ISBN: 978-1-84911-131-7 interactions © Environment Agency – October, 2009 Environment Agency’s Project Manager: Joanne Briddock, Yorkshire and North East Region All rights reserved. This document may be reproduced with prior permission of the Environment Agency. Science Project Number: SC050070 The views and statements expressed in this report are those of the author alone. The views or statements Product Code: expressed in this publication do not necessarily SCHO1009BRDX-E-P represent the views of the Environment Agency and the Environment Agency cannot accept any responsibility for such views or statements. This report is printed on Cyclus Print, a 100% recycled stock, which is 100% post consumer waste and is totally chlorine free. -
Root Zone Salinity Modeling Within Kalaat El Andalous Irrigated District (Tunisia) Using Saltmod Model
Root zone salinity modeling within Kalaat El Andalous irrigated district (Tunisia) using SaltMod model Ahmed Saidi 1*, Moncef Hammami 2, Hedi Daghari 3, Hedi Ben Ali4, Amor Boughdiri 5 1,3 Carthage University, National Agronomic Institute of Tunis, 43 Charles Nicolle Street, Mahrajene City, 1082 Tunis, Tunisia 2,5 Carthage University, Higher Agronomic School of Mateur, Road of Tabarka, 7030 Mateur, Tunisia 4Agency of agricultural investment promotion, 6000 Gabes, Tunisia Abstract—SaltMod simulations indicate a slight change of root zone salinity remaining between 3 and 6 dS/m and do not causes risks to forage and cereal crops. However, such salinity is causing a yield decrease of 10 to 20% for tomato crop. During the next 10 years, groundwater water table depth will range between 1.33 and 1.76 m. and remains lower than that of the root zone (0.6 m). Therefore, groundwater table will not pose problems as long as we keep the same management conditions during this period. Moreover, the simulation of drainage system depth variation impacts on root zone salinity indicates that a decrease of drainage lines depth does not affect root zone salinity which remains constant (4.94 dS/m and 3.68 dS/m respectively during the first season and the second season). Regarding groundwater table depth, it is noted that there is a variation for each drainage lines depth variation and groundwater level is ranging from 1.26 to 0.26 m and 1.76 to 0.76 m during the first season and the second season respectively. Thus, optimum drainage lines depth corresponds to that for which salinity and groundwater level have acceptable values not threatening crops and generating minimum drainage flow. -
Managing Storm Water Runoff to Prevent Contamination of Drinking Water
United States Office of Water EPA 816-F-01-020 Environmental Protection (4606) July 2001 Agency Source Water Protection Practices Bulletin Managing Storm Water Runoff to Prevent Contamination of Drinking Water Storm water runoff is rain or snow melt that flows off the land, from streets, roof tops, and lawns. The runoff carries sediment and contaminants with it to a surface water body or infiltrates through the soil to ground water. This fact sheet focuses on the management of runoff in urban environments; other fact sheets address management measures for other specific sources, such as pesticides, animal feeding operations, and vehicle washing. SOURCES OF STORM WATER RUNOFF Urban and suburban areas are predominated by impervious cover including pavements on roads, sidewalks, and parking lots; rooftops of buildings and other structures; and impaired pervious surfaces (compacted soils) such as dirt parking lots, walking paths, baseball fields and suburban lawns. During storms, rainwater flows across these impervious surfaces, mobilizing contaminants, and transporting them to water bodies. All of the activities that take place in urban and suburban areas contribute to the pollutant load of storm water runoff. Oil, gasoline, and automotive fluids drip from vehicles onto roads and parking lots. Storm water runoff from shopping malls and retail centers also contains hydrocarbons from automobiles. Landscaping by homeowners, around businesses, and on public grounds contributes sediments, pesticides, fertilizers, and nutrients to runoff. Construction of roads and buildings is another large contributor of sediment loads to waterways. In addition, any uncovered materials such as improperly stored hazardous substances (e.g., household Parking lot runoff cleaners, pool chemicals, or lawn care products), pet and wildlife wastes, and litter can be carried in runoff to streams or ground water. -
Toward a Conceptual Framework of Hyporheic Exchange Across Spatial Scales
Hydrol. Earth Syst. Sci., 22, 6163–6185, 2018 https://doi.org/10.5194/hess-22-6163-2018 © Author(s) 2018. This work is distributed under the Creative Commons Attribution 4.0 License. Toward a conceptual framework of hyporheic exchange across spatial scales Chiara Magliozzi1, Robert C. Grabowski1, Aaron I. Packman2, and Stefan Krause3 1School of Water, Energy and Environment, Cranfield University, Cranfield, Bedfordshire, MK43 0AL, UK 2Department of Civil and Environmental Engineering, Northwestern University, Evanston, Illinois, USA 3School of Geography, Earth and Environmental Sciences, University of Birmingham, Birmingham, Edgbaston, B15 2TT, UK Correspondence: Robert C. Grabowski (r.c.grabowski@cranfield.ac.uk) Received: 15 May 2018 – Discussion started: 30 May 2018 Revised: 19 October 2018 – Accepted: 28 October 2018 – Published: 30 November 2018 Abstract. Rivers are not isolated systems but interact con- 1 Introduction tinuously with groundwater from their confined headwaters to their wide lowland floodplains. In the last few decades, Hyporheic zones (HZs) are unique components of river sys- research on the hyporheic zone (HZ) has increased appreci- tems that underpin fundamental stream ecosystem functions ation of the hydrological importance and ecological signif- (Ward, 2016; Harvey and Gooseff, 2015; Merill and Ton- icance of connected river and groundwater systems. While jes, 2014; Krause et al., 2011a; Boulton et al., 1998; Brunke recent studies have investigated hydrological, biogeochem- and Gonser, 1997; Orghidan, 1959). At the -
Surface Water
Chapter 5 SURFACE WATER Surface water originates mostly from rainfall and is a mixture of surface run-off and ground water. It includes larges rivers, ponds and lakes, and the small upland streams which may originate from springs and collect the run-off from the watersheds. The quantity of run-off depends upon a large number of factors, the most important of which are the amount and intensity of rainfall, the climate and vegetation and, also, the geological, geographi- cal, and topographical features of the area under consideration. It varies widely, from about 20 % in arid and sandy areas where the rainfall is scarce to more than 50% in rocky regions in which the annual rainfall is heavy. Of the remaining portion of the rainfall. some of the water percolates into the ground (see "Ground water", page 57), and the rest is lost by evaporation, transpiration and absorption. The quality of surface water is governed by its content of living organisms and by the amounts of mineral and organic matter which it may have picked up in the course of its formation. As rain falls through the atmo- sphere, it collects dust and absorbs oxygen and carbon dioxide from the air. While flowing over the ground, surface water collects silt and particles of organic matter, some of which will ultimately go into solution. It also picks up more carbon dioxide from the vegetation and micro-organisms and bacteria from the topsoil and from decaying matter. On inhabited watersheds, pollution may include faecal material and pathogenic organisms, as well as other human and industrial wastes which have not been properly disposed of. -
Estimation of Surface Runoff Using NRCS Curve Number in Some Areas in Northwest Coast, Egypt
E3S Web of Conferences 167, 02002 (2020) https://doi.org/10.1051/e3sconf/202016702002 ICESD 2020 Estimation of surface runoff using NRCS curve number in some areas in northwest coast, Egypt Mohamed E.S1. Abdellatif M.A1. Sameh Kotb Abd-Elmabod2, Khalil M.M.N.3 1 National Authority for Remote Sensing and Space Sciences (NARSS), Cairo, Egypt 2 Soil and Water Use Department, Agricultural and Biological Research Division, National Research Centre, Cairo 12622, Egyp 3 Soil Science Department, Faculty of Agriculture, Zagazig University, Zagazig, Egypt. Abstract. The sustainable agricultural development in the northwest coast of Egypt suffers constantly from the effects of surface runoff. Moreover, there is an urgent need by decision makers to know the effects of runoff. So the aim of this work is to integrate remote sensing and field data and the natural resource conservation service curve number model (NRCS-CN).using geographic information systems (GIS) for spatial evaluation of surface runoff .CN approach to assessment the effect of patio-temporal variations of different soil types as well as potential climate change impact on surface runoff. DEM was used to describe the effects of slope variables on water retention and surface runoff volumes. In addition the results reflects that the magnitude of surface runoff is associated with CN values using NRCS-CN model . The average of water retention ranging between 2.5 to 3.9m the results illustrated that the highest value of runoff is distinguished around the urban area and its surrounding where it ranged between 138 - 199 mm. The results show an increase in the amount of surface runoff to 199 mm when rainfall increases 200 mm / year. -
Chapter 3. Hydrology
3 Hydrology Robert R. Ziemer and Thomas E. Lisle Overview transient snow packs during rain on snow events. l Streamflow is highly variable in mountainous l Removal of trees, which consume water, areas of the Pacific coastal ecoregion. The tends to increase soil moisture and base stream- timing and variability of streamflow is strongly flow in summer when rates of evapotranspira- influenced by form of precipitation (e.g., rain- tion are high. These summertime effects tend to fall, snowmelt, or rain on snow). disappear within several years. Effects of tree l High variability in runoff processes limits removal on soil moisture in winter are minimal the ability to detect and predict human-caused because of high seasonal rainfall and reduced changes in streamflow. Changes in flow are usu- rates of evapotranspiration. ally associated with changes in other watershed l The rate of recovery from land use processes that may be of equal concern. Studies depends on the type of land use and on the of how land use affects watershed responses are hydrologic processes that are affected. thus likely to be most useful if they focus on how runoff processes are affected at the site of disturbance and how these effects, hydrologic Introduction or otherwise, are propagated downstream. l Land use and other site factors affecting Streamflow is an essential variable in under- flows have less effect on major floods and in standing the functioning of watersheds and large basins than on smaller peak flows and in associated ecosystems because it supplies the small basins. Land use is more likely to affect primary medium and source of energy for the streamflow during rain on snow events, which movement of water, sediment, organic mate- usuallv produce larger floods in much of the rial, nutrients, and thermal energy. -
Introduction and Characteristics of Flow
Introduction and Characteristics of Flow By James W. LaBaugh and Donald O. Rosenberry Chapter 1 of Field Techniques for Estimating Water Fluxes Between Surface Water and Ground Water Edited by Donald O. Rosenberry and James W. LaBaugh Techniques and Methods Chapter 4–D2 U.S. Department of the Interior U.S. Geological Survey Contents Introduction.....................................................................................................................................................5 Purpose and Scope .......................................................................................................................................6 Characteristics of Water Exchange Between Surface Water and Ground Water .............................7 Characteristics of Near-Shore Sediments .......................................................................................8 Temporal and Spatial Variability of Flow .........................................................................................10 Defining the Purpose for Measuring the Exchange of Water Between Surface Water and Ground Water ..........................................................................................................................12 Determining Locations of Water Exchange ....................................................................................12 Measuring Direction of Flow ............................................................................................................15 Measuring the Quantity of Flow .......................................................................................................15 -
Land Degeneration Due to Water Infiltration and Sub-Erosion
sustainability Article Land Degeneration due to Water Infiltration and Sub-Erosion: A Case Study of Soil Slope Failure at the National Geological Park of Qian-an Mud Forest, China Xiangjian Rui, Lei Nie, Yan Xu * and Hong Wang Construction Engineering College, Jilin University, Changchun 130026, China * Correspondence: [email protected] Received: 7 August 2019; Accepted: 26 August 2019; Published: 29 August 2019 Abstract: Sustainable development of the natural landscape has received an increasing attention worldwide. Identifying the causes of land degradation is the primary condition for adopting appropriate methods to preserve degraded landscapes. The National Geological Park of Qian-an mud forest in China is facing widespread land degradation, which not only threatens landscape development but also endangers many households and farmlands. Using the park as a research object, we identified the types of slope failure and the factors that contribute to their occurrence. During June 2017, a detailed field survey conducted in a representative area of the studied region found two main types of slope failure: soil cave piping and vertical collapse. Physicochemical properties of the soil samples were measured in the laboratory. Results show that soil slope failure is controlled by three factors: (1) the typical geological structure of the mud forest area represented by an upper layer of thick loess sub-sandy soil and the near-vertical slope morphology; (2) particular soil properties, especially soil dispersibility; and (3) special climate conditions with distinct wet and dry seasons. Keywords: landscape; mud forest; land degeneration; water infiltration; sub-erosion; soil slope failure 1. Introduction Recently, the sustainable development of natural landscapes has received an increasing attention worldwide. -
Surface Water and Groundwater Interactions in Traditionally Irrigated Fields in Northern New Mexico, U.S.A
water Article Surface Water and Groundwater Interactions in Traditionally Irrigated Fields in Northern New Mexico, U.S.A. Karina Y. Gutiérrez-Jurado 1, Alexander G. Fernald 2, Steven J. Guldan 3 and Carlos G. Ochoa 4,* 1 School of the Environment, Flinders University, Bedford Park, SA 5042, Australia; karina.gutierrez@flinders.edu.au 2 Water Resources Research Institute, New Mexico State University, Las Cruces, NM 88003, USA; [email protected] 3 Sustainable Agriculture Science Center, New Mexico State University, Alcalde, NM 87511, USA; [email protected] 4 Department of Animal and Rangeland Sciences, Oregon State University, Corvallis, OR 97331, USA * Correspondence: [email protected]; Tel.: +1-541-737-0933 Academic Editor: Ashok K. Chapagain Received: 18 December 2016; Accepted: 3 February 2017; Published: 10 February 2017 Abstract: Better understanding of surface water (SW) and groundwater (GW) interactions and water balances has become indispensable for water management decisions. This study sought to characterize SW-GW interactions in three crop fields located in three different irrigated valleys in northern New Mexico by (1) estimating deep percolation (DP) below the root zone in flood-irrigated crop fields; and (2) characterizing shallow aquifer response to inputs from DP associated with irrigation. Detailed measurements of irrigation water application, soil water content fluctuations, crop field runoff, and weather data were used in the water budget calculations for each field. Shallow wells were used to monitor groundwater level response to DP inputs. The amount of DP was positively and significantly related to the total amount of irrigation water applied for the Rio Hondo and Alcalde sites, but not for the El Rito site. -
Impact of Geomorphic Structures on Hyporheic Exchange, Stream Temperature, and Stream Ecological Processes
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Carolina Digital Repository Impact of Geomorphic Structures on Hyporheic Exchange, Temperature, and Ecological Processes in Streams Erich T. Hester A dissertation submitted to the faculty of the University of North Carolina at Chapel Hill in partial fulfillment of the requirements for the degree of Doctor of Philosophy in the Curriculum in Ecology. Chapel Hill 2008 Approved by: Martin W. Doyle Lawrence E. Band Emily S. Bernhardt Michael F. Piehler Seth R. Reice Abstract Erich T. Hester: Impact of Geomorphic Structures on Hyporheic Exchange, Temperature, and Ecological Processes in Streams (Under the direction of Martin W. Doyle) Water exchange between streams and groundwater (hyporheic exchange) facilitates exchange of heat, nutrients, toxics, and biota. In-stream geomorphic structures (IGSs) such as log dams and steps are common in natural streams and stream restoration projects, and can significantly enhance hyporheic exchange. Hyporheic exchange is known to moderate temperatures in streams, a function important to a variety of stream organisms. Nevertheless, the connection between IGS form, hydrogeologic setting, hyporheic exchange, and hyporheic thermal impacts are poorly known. In this dissertation, I used hydraulic modeling and field experiments to quantify how basic characteristics of IGSs and their hydrogeologic setting impact induced hyporheic water and heat exchange and stream temperature. Model results indicate that structure size, background groundwater discharge, and sediment hydraulic conductivity are the most important factors controlling induced hyporheic exchange. Nonlinear relationships between many such driving factors and hyporheic exchange are important for understanding IGS functioning. Weir-induced hyporheic heat advection noticeably affected shallow sediment temperatures during the field experiments, and also caused slight cooling of the surface stream, an effect that increased with weir height. -
Impact of Cattle Access to Watercourses
Report No. 260 Impact of Cattle Access to Watercourses: Literature Review on Behalf of the COSAINT Project Authors: Paul O’Callaghan, Mary Kelly-Quinn, Eleanor Jennings, Patricia Antunes, Matt O’Sullivan, Owen Fenton and Daire Ó hUallacháin www.epa.ie ENVIRONMENTAL PROTECTION AGENCY Monitoring, Analysing and Reporting on the The Environmental Protection Agency (EPA) is responsible for Environment protecting and improving the environment as a valuable asset • Monitoring air quality and implementing the EU Clean Air for for the people of Ireland. We are committed to protecting people Europe (CAFÉ) Directive. and the environment from the harmful effects of radiation and • Independent reporting to inform decision making by national pollution. and local government (e.g. periodic reporting on the State of Ireland’s Environment and Indicator Reports). The work of the EPA can be divided into three main areas: Regulating Ireland’s Greenhouse Gas Emissions • Preparing Ireland’s greenhouse gas inventories and projections. Regulation: We implement effective regulation and environmental • Implementing the Emissions Trading Directive, for over 100 of compliance systems to deliver good environmental outcomes and the largest producers of carbon dioxide in Ireland. target those who don’t comply. Knowledge: We provide high quality, targeted and timely Environmental Research and Development environmental data, information and assessment to inform • Funding environmental research to identify pressures, inform decision making at all levels. policy and provide solutions in the areas of climate, water and sustainability. Advocacy: We work with others to advocate for a clean, productive and well protected environment and for sustainable Strategic Environmental Assessment environmental behaviour. • Assessing the impact of proposed plans and programmes on the Irish environment (e.g.