The Role of Vegetation in Minimising GW Recharge – application to mining and waste management industries Derek Eamus, C Macinnis-Ng, I Yunusa, M Zeppel.

Slides:



Advertisements
Similar presentations
A Simple Production Efficiency Model 1/18 Willem de Kooning ( ) A Tree in Naples.
Advertisements

Colin S. Campbell, Ph.D. Decagon Devices
University of Wales Swansea CEH Wallingford CEH Monks Wood University of Durham MetOffice CLASSIC –AMMA Fieldwork 2005/2006 and modelling activities Jon.
Evergreen tree dynamics in tropical savanna
CYCLOPS: Modelling the Role of Vegetation Type & Fire on Permafrost Thaw Aaron Thierry, C. Estop-Aragones, J.Fisher, I.Hartley, J. Murton, G. Phoenix,
2003 Sap Flow CWSI Vine Sap Flow Stress Measurement Objectives: Transpiration measurement method – Collect data to measure Crop Water Stress Index using.
GIS – BASED DRASTIC MODEL FOR ASSESSING
D.L. Farmer (1), M. Sivapalan (1), and I. Lockley (2) Assessing vegetation influence on water balance in rehabilitation landscapes using simple storage.
Hydrologic Abstractions
Leibniz-Centre for Agricultural Landscape Research (ZALF) Müncheberg, Germany Institute of Landscape Systems Analysis Funded by Martina Puhlmann, Hubert.
Water use and water use efficiency in west coast Douglas-fir Paul Jassal, Andy Black, Bob Chen, Zoran Nesic, Praveena Krishnan and Dave Spittlehouse University.
Soil and vegetation components Ecophysiology Group - Mica Creek.
Alan F. Hamlet Dennis P. Lettenmaier JISAO Center for Science in the Earth System Climate Impacts Group and Department of Civil and Environmental Engineering.
CGMS/WOFOST model principles
PREFER 1 st Annual Review Meeting, 5-6 Dec 2013, Milano-Italy PREFER WP3.1 - Information Support to Preparedness/Prevention Phase Product: “Daily Fire.
Soil Physics 2010 Outline Announcements Measuring evaporation.
By Andrew Lee and Oliver Royle. Definition The Water Cycle, also know as the hydrological cycle, is the journey that water takes through mainly evapotranspiration,
Data for Irrigation Modelling Hector M Malano. Outline Modelling: what processes? What data gaps are there? Frequency of collection Level of disaggregation.
SWAT – Land Phase of the Hydrologic Cycle Kristina Schneider Kristi Shaw.
Jefferson High School Compton Creek Research Project UCLA and Los Angeles Waterkeeper Funded by the Environmental Protection Agency.
 Tropical montane cloud forests (TMCF) are unique ecosystems characterized by a highly variable weather conditions including strong.
Effects of Forest Management on Carbon Flux and Storage Jiquan Chen, Randy Jensen, Qinglin Li, Rachel Henderson & Jianye Xu University of Toledo & Missouri.
Global Environments Introducing Physical Environments.
Strategic sampling of microclimate, soil moisture and sapflux for improving ecohydrological model estimates in the California Sierra Kyongho Son and Christina.
Soil-Vegetation-Atmosphere Transfer (SVAT) Models
Applications of Bayesian sensitivity and uncertainty analysis to the statistical analysis of computer simulators for carbon dynamics Marc Kennedy Clive.
Testing the assumptions in JULES: chalk soils Nataliya Bulygina, Christina Bakopoulou, Adrian Butler, and Neil McIntyre.
2009 Hydrologic Synthesis Reverse Site Visit – Arlington VA Water balance partitioning at the catchment scale: Hydrosphere-biosphere interactions Peter.
NCA-LDAS Meeting, Sept 23, 2014 NCA-LDAS: An Integrated Terrestrial Water Analysis System for the National Climate Assessment “Water Indicators” Hiroko.
Experiments and Modeling of Water and Energy Transfer in Agro-ecosystem Yi LUO Zhu OUYANG Yucheng Comprehensive Experiment Station, CAS Sept, 2002.
Estimating Groundwater Recharge Using the Oklahoma Mesonet
Routing GenRiver 1.0 Distributed process-based model spatial scale: ha,temporal scale: daily Can be used as a tool to explore our understanding.
A process-based, terrestrial biosphere model of ecosystem dynamics (Hybrid v. 3.0) A. D. Friend, A.K. Stevens, R.G. Knox, M.G.R. Cannell. Ecological Modelling.
NWS Calibration Workshop, LMRFC March, 2009 Slide 1 Analysis of Evaporation Basic Calibration Workshop March 10-13, 2009 LMRFC.
These notes are provided to help you pay attention IN class. If I notice poor attendance, fewer notes will begin to appear on these pages 1.
Water and Carbon Cycles in Heterogeneous Landscapes: An Ecosystem Perspective Chapter 4 How water and carbon cycles connect the organizational levels of.
Estimating ET Type of method used will be determined by: 1. Type of surface (e.g. open water vs. leaf) 2. Availability of water for evaporation
Hydrologic Equation Inflow = outflow +/- Changes in storage Equation is simple statement of mass conservation.
Variation of Surface Soil Moisture and its Implications Under Changing Climate Conditions 1.
The Soil-Plant-Atmosphere (SPA) Model Multilayer canopy and soils, 30 minute time-step Standard components –Radiative transfer scheme (sun/shade) –Soil.
Liebermann R 1, Kraft P 1, Houska T 1, Müller C 2,3, Haas E 4, Kraus D 4, Klatt S 4, Breuer L 1 1 Institute for Landscape Ecology and Resources Management,
BioVeL MS11 Workshop - Ecosystem functioning & valuation web services and workflows Recent model developments in Hungary: Biome-BGC MuSo Zoltán Barcza,
ChEAS 2005 D.S. Mackay June 1-2, 2005 Reference canopy conductance through space and time: Unifying properties and their conceptual basis D. Scott Mackay.
Ф Physical change from liquid to gas Ф 600 calories evaporate 1 gram H 2 O Ф Solar Radiation, Air Temperature, Vapor Pressure, Wind all affect rate.
Page 1© Crown copyright 2004 Meteorological Inputs Groundwater Workshop, Birmingham Murray Dale, 4/11/04.
Estimating Groundwater Recharge in Porous Media Aquifers in Texas Bridget Scanlon Kelley Keese Robert Reedy Bureau of Economic Geology Jackson School of.
Conclusions The states of the surface and root zoon soil moisture are considered as key variables controlling surface water and energy balances. Force-restore.
Atmosphere 0.002% Ocean 97.2% Ice caps & glaciers 2% biosphere Rivers, lakes 0.6% Underground- lithosphere I P Et S E+C.
Parameterisation by combination of different levels of process-based model physical complexity John Pomeroy 1, Olga Semenova 2,3, Lyudmila Lebedeva 2,4.
Results Time Study Site Measured data Alfalfa Numerical Analysis of Water and Heat Transport in Vegetated Soils Using HYDRUS-1D Masaru Sakai 1), Jirka.
Kristina Schneider Kristi Shaw
Estimating the Reduction in Photosynthesis from Sapflow Data in a Throughfall Exclusion Experiment. Rosie Fisher 1, Mathew Williams 1, Patrick Meir 1,
Perspectives on water cycling in ecosystem models Sarah Davis June 12, 2012 Water in Bioenergy Agroecosystems Workshop.
4.6 INTRODUCING ‘SWAM’ (SOIL WATER ACCOUNTING MODEL)
1 UIUC ATMOS 397G Biogeochemical Cycles and Global Change Lecture 18: Nitrogen Cycle Don Wuebbles Department of Atmospheric Sciences University of Illinois,
Water Budget IV: Soil Water Processes P = Q + ET + G + ΔS.
Bayesian analysis of a conceptual transpiration model with a comparison of canopy conductance sub-models Sudeep Samanta Department of Forest Ecology and.
Influence of tree crown parameters on the seasonal CO2-exchange of a pine forest in Brasschaat, Belgium. Jelle Hofman Promotor: Dr. Sebastiaan Luyssaert.
Plot scale processes Jan Vanderborght: Soil Physics, modelling in terrestrial systems Nicolas Brüggemann: Stable Isotopes Mathieu Javaux: Soil Physics,
EVAPORATION.
Kristina Schneider Kristi Shaw
Hydraulic Redistribution of Soil Water in a Drained Loblolly Pine Plantation: Quantifying Patterns and Controls over Soil-to-Root and Canopy-to-Atmosphere.
3-PG The Use of Physiological Principles in Predicting Forest Growth
Marcos Heil Costa Universidade Federal de Viçosa
Potential Evapotranspiration (PET)
Ecosystem Demography model version 2 (ED2)
Watershed Hydrology NREM 691 Week 3 Ali Fares, Ph.D.
Liquid Phase Water Flow Rs2 Rp Rsn Rs1 C Ys1 Ysn Ys2 E Rr1 Rr2 Rrn Plant Soil Atmosphere CO2 gs Leaf Stem Roots Yl Root resistance (Rr) Plant resistance.
SWAT – Land Phase of the Hydrologic Cycle

Presentation transcript:

The Role of Vegetation in Minimising GW Recharge – application to mining and waste management industries Derek Eamus, C Macinnis-Ng, I Yunusa, M Zeppel Terrestrial Ecohydrology Research Group University of Technology, Sydney

Outline of the talk Why do we need to minimise GW recharge?Why do we need to minimise GW recharge? How can we minimise it?How can we minimise it? Design of store-release caps requires knowledge of rate of water use by vegetationDesign of store-release caps requires knowledge of rate of water use by vegetation How might we model veg water use?How might we model veg water use?

Outline of the talk A modified Jarvis-Stewart modelA modified Jarvis-Stewart model Using a Soil-Plant Atmosphere modelUsing a Soil-Plant Atmosphere model A case study of a site in NSWA case study of a site in NSW

Minimising GW recharge is important for: Minimising development of dryland salinityMinimising development of dryland salinity Preventing leachates from waste storage dumps poisoning an aquiferPreventing leachates from waste storage dumps poisoning an aquifer Preventing acid drainage from mine-site rock dumpsPreventing acid drainage from mine-site rock dumps

How can we minimise GW recharge? Use vegetation to transpire rain back to the atmosphere before it percolates beyond the root zoneUse vegetation to transpire rain back to the atmosphere before it percolates beyond the root zone Therefore need to design a “cap” on the siteTherefore need to design a “cap” on the site This raises many questions of design, eg:This raises many questions of design, eg: How deep should the soil be on the clay cap?How deep should the soil be on the clay cap? How do we know how much water the vegetation will transpire on a daily/seasonal/annual basis?How do we know how much water the vegetation will transpire on a daily/seasonal/annual basis?

Water use by vegetation – a reminder Water use by vegetation is determined by:Water use by vegetation is determined by: Solar radiation inputSolar radiation input Soil moisture contentSoil moisture content Atmospheric water content (humidity or vapour pressure deficit)Atmospheric water content (humidity or vapour pressure deficit) Leaf area index of the vegetationLeaf area index of the vegetation

Current models require parameterisation for each site individually – eg SPA, VADOSE, Penman-MonteithCurrent models require parameterisation for each site individually – eg SPA, VADOSE, Penman-Monteith Models have a large number of input variables – SPA has about 15, VADOSE has far too many, the P-M has 6Models have a large number of input variables – SPA has about 15, VADOSE has far too many, the P-M has 6 We can model veg water use

Parameterising models for every site and vegetation type is too slow and expensiveParameterising models for every site and vegetation type is too slow and expensive We have developed a modified Jarvis- Stewart model that can be used for any ecosystem dominated by woody vegetationWe have developed a modified Jarvis- Stewart model that can be used for any ecosystem dominated by woody vegetation We can model veg water use

Modelling tree water use – the original JS approach Penman-Monteith Equation and Jarvis-Stewart Model 1.Needs measurements of G c 2.Circular, Complex and Time Consuming A modified Jarvis-Stewart Model 1.Measurements in E c 2.Retains Mechanistic understanding of processes

Model Functional Dependencies Dependence of G c and E c on changing solar radiation Dependence of G c on changing vapour pressure deficit Dependence of G c and E c on changing soil moisture content Dependence of E c on changing vapour pressure deficit

Veg water use varies as a function of light, VPD and soil moisture

How well does the modified Jarvis-Stewart model perform? We compared it to the standard P-M approach and to an artificial neural network statistical model

Summer Winter

With our modified JS model, the slope of the regression for observed and modelled is close to oneWith our modified JS model, the slope of the regression for observed and modelled is close to one

A comparison of three sites – all three behave similarly

Do we need to parameterise the model independently for each site? If average parameter values work, this would be a massive saving in effort.....If average parameter values work, this would be a massive saving in effort.....

The modified JS using average parameter values does very well (Paringa data)

Using an averaged set of parameter values allows us to generate daily rates of water use from just a set of met data

Applying a modelling approach to testing the mechanism We applied the Soil-Plant-Atmosphere model of Williams et al to the problemWe applied the Soil-Plant-Atmosphere model of Williams et al to the problem The SPA model is a detailed mechanistic model that calculates C fluxes, water fluxes, leaf water potential and GPP of landscapesThe SPA model is a detailed mechanistic model that calculates C fluxes, water fluxes, leaf water potential and GPP of landscapes

The SPA models water flux from Soil, through the Plant to the Atmosphere Plant data Soil data Soil water uptake Sap flow Leaf water potential Met data Stomatal conductance Photosynthesis GPP Transpiration INPUTS OUTPUTS

The SPA model does well in modelling sap flow at our site

Veg water use was independent of the water content of the upper 80 cm of soil – highlighting the importance of deep roots in the clay layer

Conclusions The modified JS model allows quantification of water use from basic met data and using average parameter valuesThe modified JS model allows quantification of water use from basic met data and using average parameter values The SPA model is a detailed model that allows us to examine the mechanisms underlying observed behaviourThe SPA model is a detailed model that allows us to examine the mechanisms underlying observed behaviour Management of deep drainage through vegetation is a realistic option for the waste and mining industriesManagement of deep drainage through vegetation is a realistic option for the waste and mining industries

Published by CSIRO 2006 ISBN