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ABSTRACT Process-based models of soil-vegetation-atmosphere interactions developed for small plots (points) define vertical transfers of water and energy. One can attempt to scale to larger heterogeneous land units by disaggregating the landscape into a set of elements and applying a vertical SVAT model independently to each element (Running et al., 1989; Pierce et al., 1992). Such applications fail to consider lateral transfers. A distributed parameter, three-dimensional SVAT (Topog-IRM) developed by the CSIRO Division of Water Resources (O'Loughlin, 1990; Hatton and Dawes, 1991; Hatton et al., 1992) is used to examine the importance of lateral transfers of water for prediction of water balance components at the small catchment scale.
Simulations are used to contrast the predicted water balances from a SVAT model with and without considerations of lateral subsurface and overland flow in complex terrain. Components of the catchment water balance are shown to scale linearly except in those cases where transient perched water tables develop in landscapes with sufficient slope and hydraulic conductivity to redistribute water effectively via subsurface lateral flow. In such cases, the prediction of catchment yield and the spatial pattern of soil moisture requires the explicit treatment of lateral transfers.
INTRODUCTION
The most widely-used soil-vegetation-atmosphere (SVAT) models calculate the surface energy and water (and carbon) balances in the vertical dimension only (e.g. Running and Coughlan, 1988; Wang and Jarvis, 1990).
ABSTRACT Macroscale hydrological modelling is currently conducted using Global Climate Models (GCMs) coupled to a range of Soil-Vegetation-Atmosphere Transfer Schemes (SVATs). The most extreme type of simulation involves massive land use change. This paper reports on the results of a tropical deforestation experiment in which the tropical moist forest throughout the Amazon Basin and SE Asia has been replaced by a scrub grassland in a version of the NCAR Community Climate Model (Version 1) which also incorporates a mixed layer ocean and the Biosphere-Atmosphere Transfer Scheme (BATS). In the Amazon we find a smaller temperature increase than did all other previous experiments except Henderson-Sellers and Gornitz (1984); indeed temperatures decrease in some months. On the other hand, we find larger hydrological responses than all earlier experiments including runoff decreases and a larger difference between the changes in evaporation and precipitation which indicate a basin-wide decrease in moisture convergence. Disturbances extend beyond the region of land-surface change causing temperature reductions and precipitation increases to the south of the deforested area in S America. Changes to the surface climate in the deforested area take between 1 and 2 years to become fully established although the root zone soil moisture is still decreasing at the end of a 6-year integration. Besides temperature and precipitation, other fields show statistically significant alterations, especially evaporation and net surface radiation (both decreased). An important question raised by this type of simulation concerns the appropriateness of the microhydrological process models employed in SVATs to the GCMs in which they are currently used.
ABSTRACT A methodology is presented for downscaling GCM-output results to regional scale precipitation using atmospheric circulation patterns. A sequence of observed daily air pressure distributions is used to define circulation patterns. The classification of the circulation patterns is done with the help of a neural network. A multivariate stochastic model describes their link to observed daily precipitation amounts at a number of selected locations. To assess precipitation under changed climate circulation patterns derived from GCM output pressure values are used to condition the stochastic precipitation model. The methodology is demonstrated by results obtained for a selected location (Essen, Germany).
INTRODUCTION
Climate change will have a major influence on the hydrological cycle. It is of vital importance to assess the possible impacts as soon as possible, in order to find strategies to adapt to these changes.
The only physically based tools in predicting climate change effects are General Circulation Models (GCM). GCMs deliver meteorological variables in a fine time resolution (30 minutes to a few hours) but in a very coarse spatial grid (200–500 km × 200–500 km). Many climatic parameters like temperature, precipitation, wind, clouds, radiation, snow cover and soil moisture can be simulated by these models.
Unfortunately precipitation, which is the main input in hydrological models, cannot be well modelled by the GCMs. GCM control runs for the present climate indicate that single grid values cannot be taken as representative rainfall amounts of the corresponding area.
ABSTRACT Rainfall exhibits at every time scale a great variability which becomes extreme for short durations. We first tried to give rainfall occurrence a fractal dimension the main interest of which is to be time scale invariant. This geometrical approach appears to be of limited value, the fractal dimension being dependent upon the intensity threshold used to define the rainy character of a given period. This problem can be overcome by substituting multifractal fields to fractal sets.
The fundamental equation of such fields enables us to relate at every scale the fraction of space occupied by singularities to their probability of appearance. This equation depends only on two parameters characterizing respectively departures of the field under study from homogeneity and monofractality. A time scale invariant frequency-intensity-duration formula has been derived within this frame, which suggests the existence for all durations of a possible maximum precipitation.
FRACTALS ET MULTIFRACTALS APPLIQUÉS À L'ÉTUDE DE LA VARIABILITÉ TEMPORELLE DES PRÉCIPITATIONS
La pluie est un phénomène qui se manifeste dans l'espace et dans le temps. On peut supposer l'existence d'une fonction I(x, t), caractérisant l'intensité des précipitations au point x de l'espace à deux dimensions constitué par la surface terrestre et au temps t, cette intensité étant exprimée en hauteur d'eau par unité de temps, [L] [T]-1. Nous ne connaissons a priori rien des propriétés de cette fonction mis à part l'hypothèse de définition en tout point, mais différents types de mesurages permettent d'en estimer des intégrates selon le temps et/ou l'espace (Fig. 1).
By
W. F. Krajewski, Department of Civil and Environmental Engineering and Iowa Institute of Hydraulic Research, The University of Iowa, Iowa City, Iowa, USA,
J. A. Smith, Department of Civil Engineering and Operations Research, Princeton University, Princeton, New Jersey, USA
ABSTRACT Two Monte Carlo simulation experiments which address the problem of radar-rainfall estimation are presented. One of the problems associated with hydrologic use of radar-rainfall data is the need to adjust radar rainfall estimates to raingage estimates. The adjustment, which is performed in real time, can be done in the mean field sense. The problem of development of such an adjustment scheme is difficult due to largely unknown statistical structure of radar errors and the fundamental sampling differences between these two sensors. To investigate the problem, mean field bias is modeled as a random process that varies not only from storm to storm but also over the course of a storm. State estimates of mean field bias are based on hourly rain gage data and hourly accumulations of radar rainfall estimates. The procedures are developed for the precipitation processing system to be used with products of the Next Generation Weather Radar (NEXRAD) system. To implement the state estimation procedure parameters of the bias model must be specified. The performance of the state estimation is investigated within a Monte Carlo simulation framework. The results highlight the dependence of the state estimation problem on the parameter estimation problem. The second experiment addresses the problem of converting radar-measured reflectivity into rainfall rate. This is typically done using a Z–R relationship. The parameters of such relationship can be estimated using climatological data and nonparametric estimation framework. In the paper the effects of thresholds imposed on the observations included in the estimation are investigated.
By
W. G. Strupczewski, Civil Engineering Department, The University of Calgary, Alberta, Canada,
H. T. Mitosek, Institute of Geophysics, Polish Academy of Sciences, Warsaw, Poland
ABSTRACT If hydrological systems and properties of their input are changing year to year the stationarity assumption of hydrological time series could not hold any longer. The non-stationarity may occur due to the global climate changes and continued man-induced transformations of river basins. The assumption is made that the time series of annual values of hydrological variables are non-stationary, which in fact can be tested statistically. Then the question arises how to use such series in hydrological design if the structure is to be dimensioned on the statistical base. It seems reasonable to try to extend the existing statistical procedure to cover such a case. Following this line it is proposed to keep the type of probabilistic distribution constant and to allow its parameters to vary in time. Estimation of time dependent parameters is described. Various hypotheses regarding the form of time dependence can be compared and significance of the dependence tested. In order for a hydraulic structure to be dimensioned, its period of life shall be defined, while probability of exceedance or economic risk shall refer to this period. If the same trend in the parameter change is to be preserved in future, it will enable extrapolation of parameter values to every year of the life period and then to evaluate the probability distribution for the whole period of life.
INTRODUCTION
Many works devoted to problems of the global climatic change and of the anthropopression within the scale of the drainage area, have appeared in recent years.
ABSTRACT Different aspects and meanings of uncertainty are reviewed. This introductory review forms a basis for putting recent developments in hydrological and water resources applications of uncertainty concepts into perspective. The understanding of the term uncertainty followed herein is a logical sum of all the notions discussed. An attempt is made to justify the structure of the present volume and to sketch the areas of particular contributions in the volume and to point out their connections to different facets of uncertainty.
INTRODUCTION
It seems that there is no consensus within the profession about the very term of uncertainty, which is conceived with differing degrees of generality. Moreover, the word has several meanings and connotations in different areas, that are not always consistent with the colloquial understanding.
In the following section the notions and concepts of uncertainty both beyond and within the water resources research are discussed. Further, particular contributions in this volume are reviewed in the context of their connections to different facets of uncertainty. This is done in the systematic way, following the structure of the book.
NOTIONS OF UNCERTAINTY
Let us take recourse to established dictionaries and see how the words ‘uncertain’ and ‘uncertainty’ are explained. Among the meanings of the word ‘uncertain’, given by Hornby (1974) and Webster's (1987) dictionaries, are the following: not certain to occur, problematical, not certainly knowing or known, doubtful or dubious, not reliable, untrustworthy, not clearly identified or defined, indefinite, indeterminate, changeable, variable (not constant).
By
M. W. Kemblowski, Department of Civil and Environmental Engineering, Utah State University, Logan, Utah,,
Jet-Chau Wen, Department of Civil and Environmental Engineering, Utah State University, Logan, Utah, USA
ABSTRACT Stochastic analysis of flow and transport in subsurface usually assumes that the soil permeability is a stationary, homogeneous stochastic process with a finite variance. Some field data suggest, however, that the permeability distributions may have a fractal character with long range correlations. It is of interest to investigate how the fractal character of permeability distribution influences the spreading process in porous media. Dispersion in perfectly stratified media with fractal distribution of permeability along the vertical was analyzed. Results were obtained for the transient and asymptotic longitudinal dispersivities. The results show that the macroscopic asymptotic dispersivity depends strongly on the fractal dimension of vertical permeability distribution. Macroscopic dispersivity was found to be problem-scale dependent in development and asymptotic phases.
INTRODUCTION
The impact of heterogeneities on flow and mass transport in groundwater has been investigated for some two decades. Usually this type of investigation is performed using a stochastic, as opposed to deterministic, framework. This choice is not based on the assumption that the flow process itself is stochastic, but rather on the recognition of the fact that the deterministic description of the parameter distributions would be impractical, if not impossible.
Initial research in this area did not consider the spatial structure of flow properties, assuming that either they behaved like the white noise process (lack of spatial correlation), or had a layered structure in the direction parallel or perpendicular to the flow (perfect correlation in one direction). The next step was to consider spatial correlation of flow properties.
ABSTRACT Some scaling properties of the distribution of rain rate in space are investigated. The scales of concern range from the radar coverage range (of the order of 400 km) down to individual raindrops. Preliminary results show that over this wide range of scales rain fields exhibit: preferential scales in the range of a few tens of kilometers; behaviour compatible with multifractal structure between scales of 0.5 to 12 km and some clustering properties of the distribution of the small raindrops in space probably related to raindrop collisions and breakup.
INTRODUCTION
Rain rate fields exhibit variability at all scales down to individual raindrops. In this sense the answer to the title question is positive. However, our interest focuses more on restrictive properties, such as scale invariance, that could serve in modelling the process. One should not expect the restrictive properties (if they exist) to extend uniformly over all scales of the rainfall fields. On scales smaller then the size of individual cumulus turbulence probably prevails in determining the distribution of water substance. On larger scales other phenomena will affect markedly the distribution of precipitation in space. For example, orography (including the distribution of humidity sources) plays undoubtedly a role in organizing convective elements.
The ability to study rain at all scales is limited. A single radar does not cover a typical precipitation system. Quantitative data from networks of radars covering extended areas are now only becoming operational.
By
G. Tsakiris, Laboratory of Rural Technology, National Technical University of Athens, Greece,
O. Manoliadis, Laboratory of Rural Technology, National Technical University of Athens, Greece
ABSTRACT The irrigation system design of pressurized networks is often dimensioned based on the probability of hydrant operation. Simple statistical techniques have been extensively used in the past to model the hydrants operation and to calculate the design capacity of each reach of the network. Such methods as, for example, Clemment's ‘on demand’ approach, are adopted by designers and agencies in the design of irrigation systems. The objective of this paper is to attempt to model the hydrants operation in the irrigation network using the Alternating Renewal Process in continuous time. Extensive data were gathered from collective irrigation networks in Crete. These data were used to estimate the parameters of the Alternating Renewal Process model. A graphical representation of the results could assist in drawing useful conclusions.
INTRODUCTION
Design of collective pressurized irrigation systems is often based on the probability of hydrants operation. The method known as ‘on demand’ was introduced by Clemment (1955) for the estimation of peak season discharge requirements. Therefore the probability of operation of hydrants as a design factor has a significant effect on the overall economy of the irrigation project (construction, operation and management). Common practice for the description of the demand pattern when designing an irrigation project is to calculate a probability of hydrant operation based on earlier experience or on assumed pattern of operation.
Numerous studies on modelling irrigation networks can be found in the literature.
By
A. Kozlowski, Institute of Geophysics, Polish Academy of Sciences, Warsaw, Poland,
A. Lodziński, Institute of Geophysics, Polish Academy of Sciences, Warsaw, Poland
ABSTRACT Decision making in the process of control of water storage reservoirs is always combined with risk, whose evaluation is of utmost practical importance. Define the risk as the probability of failure within an operational control process, in the sense of water deficit or water surplus. The control is the sequence of interventions (releases) on future intervals. The risk is estimated on the basis of probability distributions of the total inflows within the horizon of an intervention. The stochastic process of total inflow is conceptualized as a non-stationary Markov chain of first or second order, under discrete time. The methodology is illustrated at the example of the water supply system of a cascade of reservoirs on the river Sola.
INTRODUCTION
In a real decision making problem a decision is made under the conditions of uncertainty, i.e. the decision maker does not have complete information about all elements that influence his decision.
In the water resources management the estimation of the quality of control is carried out a posteriori as a result of analysis of water management system performance within a long period of time, usually several years. A probabilistic estimation of failure in the control process is conducted through the determination of the periods of assurance of various desirable outflows. Recently some specific performance indices of water resources system, such as reliability, vulnerability, resilience and robustness have been considered (cf. Cohen, 1982; Haimes et al., 1984; Hashimoto et al., 1982a, b).
By
P. F. Rasmussen, Institute of Hydrodynamics and Hydraulic Engineering, Technical University of Denmark, Lyngby, Denmark,
D. Rosbjerg, Institute of Hydrodynamics and Hydraulic Engineering, Technical University of Denmark, Lyngby, Denmark
ABSTRACT In order to obtain a good description of the exceedances in a partial duration series it is often necessary to divide the year into a number (2–4) of seasons. Hereby a stationary exceedance distribution can be maintained within each season. This type of seasonal model may, however, not be suitable for prediction purposes due to the large number of parameters required. In the particular case with exponentially distributed exceedances and Poissonian occurrence times the precision of the T-year event estimator has been thoroughly examined considering both seasonal and non-seasonal models. The two-seasonal probability density function of the T-year event estimator has been deduced and used in the assessment of the precision of approximate moments. The non-seasonal approach covered both a total omission of seasonality by pooling data from different flood seasons and a discarding of nonsignificant season(s) before the analysis of extremes. Mean square error approximations (bias second order, variance first and second order) were employed as measures for prediction uncertainty. It was found that optimal estimates can usually be obtained with a non-seasonal approach.
INTRODUCTION
Since its introduction into flood frequency analysis, the partial duration series (PDS) method has gained increased acceptance as an appealing alternative to the annual maximum series (AMS) method. PDS models were introduced in hydrology by Shane & Lynn (1964), and Todorovic & Zelenhasic (1970). They assumed independent and identically distributed exceedances occurring according to a Poisson process with time-dependent intensity.
By
M. Sowinski, Department of Water Resources and Environmental Engineering, Ahmadu Bello University, Zaria, Nigeria,
M. I. Yusuf, Civil Engineering Programme, Abukabar Tafawa Balewa University, Bauchi, Nigeria
ABSTRACT In the existing design methods consideration is given to stochastic processes of flood flows imposed on the structure in order for the hydrological uncertainty to be accounted. However, there are also various uncertainties associated with flood conveyance structures which have to be considered in the design of hydraulic structures. A static model integrating hydrological and hydraulical uncertainties in the design of the Ogee spillway is devised in the present contribution. Results show that the conventional method of the evaluation of risk, where hydrological risk only is accounted, produces underestimation of the risk of failure. This becomes particularly significant if the return period and the safety factor are large.
INTRODUCTION
There are many parameters and variables subject to uncertainty in the process of design of a flood conveyance structure. These uncertainties have been classified as hydrological, hydraulic, structural and economical ones (cf. Tung & Mays, 1980). In the conventional method of design of a spillway structure it is considered that the annual flood flow input is a stochastic process and that the capacity of the structure is deterministic. This approach underestimates the risk of failure and consequent economic losses. The present work deals with hydrological and hydraulic uncertainties in the development of a composite risk model, as applied to an Ogee type spillway.
By
P. D. Meyer, Department of Civil Engineering, University of Illinois at Urbana-Champaign, USA,
J. W. Eheart, Department of Civil Engineering, University of Illinois at Urbana-Champaign, USA,
S. Ranjithan, Department of Civil Engineering, University of Illinois at Urbana-Champaign, USA,
A. J. Valocchi, Department of Civil Engineering, University of Illinois at Urbana-Champaign, USA
ABSTRACT Designing a system to monitor groundwater for contamination from landfills involves a tradeoff between cost, time of detection, and probability of detection. As monitoring wells are spaced more closely together, the probability of detecting a leak improves. Locating monitoring wells further downgradient of the landfill also improves detection probability because the plume disperses more and is less likely to move undetected between two monitoring wells. However, closer spacing costs more, and location further away from the source implies a greater time of detection and a greater probability that a water supply well will become contaminated.
An important problem in designing a monitoring system is that the hydraulic conductivity properties of the aquifer around and under the landfill are often poorly understood. It is possible to test for these properties only at points and interpolation between them may be done only with some uncertainty.
A method is discussed for designing a monitoring system under parameter uncertainty. This method places a given number of wells (the number selected by the analyst or user) in locations that maximize the probability of detection of a plume. The method requires some prior knowledge of the statistical properties of the conductivity parameters of the aquifer and some knowledge of the probability of a leak occurring at any given point in the landfill. The method is microcomputer based and currently runs on an advanced microcomputer workstation. The possibility for its adaptation to a more readily available microcomputer is discussed.
By
P. Hubert, CIG, Ecole des Mines de Paris, Fontainebleau, France,
F. Friggit, Eiier, Ouagadougou, Burkina Faso,
J. P. Carbonnel, CNRS, Université P. & M. Curie, Paris, France
ABSTRACT Rainfall occurrence related to a particular location, denned as the set of rainy periods observed, can be regarded as a fractal object belonging to the 1-D space of time. The dimension of this object, which is bounded by 0 and 1, is estimated via the functional box counting method. A large number of West African rainfall time series has been analysed. The resulting dimension is a function of the time scale and of the accepted threshold of rainfall intensity. In all cases under study, for a given time scale, a decreasing fractal dimension of rainfall occurence with increasing rainfall intensity threshold was observed. A main time scale range of practical interest was found to be from some days to some months. It is possible to attribute a multifractal structure to the process of rainfall occurrence. It can be used for simulation and/or estimation purposes. Attempts to find regional patterns and trends, and to compare them to those of inter annual rainfall means were undertaken.
INTRODUCTION
In a given location, rainfall is an intermittent process. That means that, for this location, one can observe a succession of wet and dry states. These states must be carefully defined, with areal, time interval and threshold references. A time period would be defined as wet if a given area receives during a given time interval an amount of water greater than the given threshold.
A raingauge defines accurately an observed area, being its collection surface (generally 400 cm2).
By
F. Konecny, Institute of Mathematics and Applied Statistics, Universitat fur Bodenkultur, Vienna, Austria,
H.-P. Nachtnebel, Institute of Water Resources Management, Hydrology and Hydraulic Construction, Universitat für Bodenkultur, Vienna, Austria
ABSTRACT The objective of this paper is to describe daily discharge series by a stochastic differential equation which is based on the mass balance of a linear reservoir. The input consisting of a series of jumps reflects the rainfall while the output refers to the discharges of a river basin. To account for random phenoma such as evaporation during the transformation process a perturbation term was introduced. The point process describing the shots (jumps) is based on an intensity function alternating randomly between two levels. Thus clustering of shots can be incorporated into the model.
INTRODUCTION
Numerous stochastic models have been applied to streamflow series. They can be grouped, for instance, into ARMAtype models (Fiering, 1967; Hipel et al., 1917; Noakes et al 1985; Kottegoda & Horder, 1980; Salas & Smith, 1981), long term memory models such as fractional Gaussian noise models (Mandelbrot & van Ness, 1968; Mandelbrot & Wallis, 1969) and related broken line models (Meija et al., 1972). The third class of models refers to the transformation of an intermittent rainfall process into a continuous discharge series (Treiber & Plate, 1975; Weiss, 1973, 1977; Miller et al., 1981; Kavvas & Delleur, 1984; Koch, 1985; Bodo & Unny, 1987). In this paper daily streamflow series (Beard, 1967; Quimpo, 1967; Valencia & Schaake, 1973; Mejia & Rousselle, 1976; Yakowitz, 1979; Morris, 1984; Miller et al 1981; Weiss, 1977; O'Cornell, 1977) are being modelled.