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This article was downloaded by: [Stony Brook University] On: 28 October 2014, At: 21:47 Publisher: Taylor & Francis Informa Ltd Registered in England and Wales Registered Number: 1072954 Registered office: Mortimer House, 37-41 Mortimer Street, London W1T 3JH, UK Hydrological Sciences Bulletin Publication details, including instructions for authors and subscription information: http://www.tandfonline.com/loi/thsj19 UTILIZATION OF THE RESULTS FROM REPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT OF WATER RESOURCES / Utilisation des résultats obtenus sur les bassins représentatifs et expérimentaux en vue de l'aménagement des ressources en eau J. A. RODIER a a Hydrological Service ORSTOM , Scientific Consultant to ‘Electricité de France’ , 19 rue Eugène Carrière, 75018, Paris, France Published online: 25 Dec 2009. To cite this article: J. A. RODIER (1976) UTILIZATION OF THE RESULTS FROM REPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT OF WATER RESOURCES / Utilisation des résultats obtenus sur les bassins représentatifs et expérimentaux en vue de l'aménagement des ressources en eau, Hydrological Sciences Bulletin, 21:4, 531-544, DOI: 10.1080/02626667609491672 To link to this article: http://dx.doi.org/10.1080/02626667609491672 PLEASE SCROLL DOWN FOR ARTICLE Taylor & Francis makes every effort to ensure the accuracy of all the information (the “Content”) contained in the publications on our platform. However, Taylor & Francis, our agents, and our licensors make no representations or warranties whatsoever as to the accuracy, completeness, or suitability for any purpose of the Content. Any opinions and views expressed

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Page 1: UTILIZATION OF THE RESULTS FROM REPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT OF WATER RESOURCES / Utilisation des résultats obtenus sur les bassins représentatifs

This article was downloaded by: [Stony Brook University]On: 28 October 2014, At: 21:47Publisher: Taylor & FrancisInforma Ltd Registered in England and Wales Registered Number: 1072954Registered office: Mortimer House, 37-41 Mortimer Street, London W1T 3JH,UK

Hydrological Sciences BulletinPublication details, including instructions for authorsand subscription information:http://www.tandfonline.com/loi/thsj19

UTILIZATION OF THE RESULTSFROM REPRESENTATIVE ANDEXPERIMENTAL BASINS WITH AVIEW TO THE MANAGEMENT OFWATER RESOURCES / Utilisationdes résultats obtenus surles bassins représentatifs etexpérimentaux en vue del'aménagement des ressources eneauJ. A. RODIER aa Hydrological Service ORSTOM , Scientific Consultant to‘Electricité de France’ , 19 rue Eugène Carrière, 75018,Paris, FrancePublished online: 25 Dec 2009.

To cite this article: J. A. RODIER (1976) UTILIZATION OF THE RESULTS FROMREPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT OFWATER RESOURCES / Utilisation des résultats obtenus sur les bassins représentatifs etexpérimentaux en vue de l'aménagement des ressources en eau, Hydrological SciencesBulletin, 21:4, 531-544, DOI: 10.1080/02626667609491672

To link to this article: http://dx.doi.org/10.1080/02626667609491672

PLEASE SCROLL DOWN FOR ARTICLE

Taylor & Francis makes every effort to ensure the accuracy of all theinformation (the “Content”) contained in the publications on our platform.However, Taylor & Francis, our agents, and our licensors make norepresentations or warranties whatsoever as to the accuracy, completeness, orsuitability for any purpose of the Content. Any opinions and views expressed

Page 2: UTILIZATION OF THE RESULTS FROM REPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT OF WATER RESOURCES / Utilisation des résultats obtenus sur les bassins représentatifs

in this publication are the opinions and views of the authors, and are not theviews of or endorsed by Taylor & Francis. The accuracy of the Content shouldnot be relied upon and should be independently verified with primary sourcesof information. Taylor and Francis shall not be liable for any losses, actions,claims, proceedings, demands, costs, expenses, damages, and other liabilitieswhatsoever or howsoever caused arising directly or indirectly in connectionwith, in relation to or arising out of the use of the Content.

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Hydrological Sciences-Bulletin-des Sciences Hydrologiques, XXI, 4 12/1976

UTILIZATION OF THE RESULTS FROM REPRESENTATIVE AND EXPERIMENTAL BASINS WITH A VIEW TO THE MANAGEMENT

OF WATER RESOURCES

J.A. RODIER Hydrological Service, ORSTOM; and Scientific Consultant to 'Electricité de France',

19 rue Eugène Carrière, 75018 Paris, France

Abstract. The management of water resources requires knowledge of the spatial and temporal distribu­tion of surface and groundwater resources, and an assessment of the influence of man on the hydrological regime.

For small water courses regional estimates can be made from representative basins which offer guide­lines (1) for the computation of mean annual flow and in some cases for the determination of the statistic­al distribution of the annual flow; (2) for the computation of the 10-year flood maximum discharge and volume.

An example concerning the tropical African Sahel is given. From a general study of the daily precipi­tation, a simple rainfall/runoff model used on a daily basis and calibrated on data from representative basins, and also the direct comparison of results from 55 representative basins, statistical distribution curves were established for annual runoff based on mean annual precipitation and the geomorphological characteristics of the basins.

Another example concerning tropical Africa west of Congo presents a methodology for the computa­tion of the 10-year flood (maximum discharge and volume).

The systematic study of 60 representative basins makes it possible to plot the runoff coefficient R/P as a function of basin climate, mean slope and soil permeability. Other curves are used to determine the time of rise and the base time of the hydrograph as a function of the basin area and the mean slope.

The experimental basin is a good tool for the assessment of the influence of man on hydrological parameters. An example shows the influence of land use on the regression between annual precipitation and annual runoff.

Utilisation des résultats obtenus sur les bassins représentatifs et expérimentaux en vue de l'aménagement des ressources en eau

Résumé. L'aménagement des ressources en eau exige la connaissance de la distribution spatiale et temporelle des ressources en eaux de surface et en eaux souterraines et l'évaluation de l'influence de l'homme sur le régime hydrologique.

Pour les petits cours d'eau, les bassins représentatifs permettent de réaliser des synthèses régionales après lesquelles il est possible de présenter des directives: (1) pour le calcul du volume moyen annuel et dans certains cas pour la mise au point de la distribution statistique des volumes annuels; (2) pour le calcul du débit maximal et du volume de la crue décennale.

Un exemple concernant le Sahel tropical africain est donné plus loin: l'étude générale des précipita­tions journalières, l'utilisation d'un modèle simple pluie/débit, utilisé suivant un pas de temps journalier et ajusté sur des bassins représentatifs, ainsi que la comparaison directe des résultats obtenus sur 55 bassins représentatifs, ont permis de tracer la courbe de distribution statistique de l'écoulement annuel pour di­verses valeurs de la hauteur de précipitation moyenne annuelle et pour différents types géomorphologiques de bassins versants.

Un autre exemple concernant l'Afrique tropicale à l'ouest du Congo présente la méthodologie pour le calcul de la crue décennale (débit maximal et volume).

L'étude systématique de 60 bassins représentatifs a permis de tracer les courbes de variations du coef­ficient de ruissellement R/P en fonction de la surface du bassin versant pour différents climats et diffé­rentes valeurs de la pente moyenne et de la perméabilité du sol. D'autres courbes sont utilisées pour la détermination du temps de montée et du temps de base de l'hydrogramme en fonction de la superficie du bassin pour différentes valeurs de la pente moyenne.

Le bassin expérimental constitue pour l'hydrologue un bon outil pour apprécier l'influence de l'homme sur les paramètres hydrologiques. Un exemple montre l'influence de l'utilisation du sol, dans des conditions simples, sur la régression entre la hauteur de précipitation annuelle et l'écoulement annuel.

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INTRODUCTION

It is often believed that representative and experimental basin studies should be classified exclusively within the field of fundamental research. This is not entirely correct as they may also be extremely useful for the study of water resources management projects. It is not necessary to provide for applied studies all the sophisticated equipment required for funda­mental research. As a means of study perhaps representative and experimental basins are a little costly but they are particularly effective.

The management of water resources poses two types of problems:

( 1) The spatial distribution of surface and groundwater resources and the temporal dis­tribution at each point, including the extremes. The spatial distribution is generally present­ed by maps which are frequently drawn well before all the elements necessary for making an accurate map are available. These maps are drawn for the various statistical parameters which will be dealt with later. The temporal distribution is represented either by the classic parameters of the statistical distribution (average, standard deviation, skewness, values corresponding to the differing frequencies), or hydrological characteristics (annual discharge, flood flow and low flow), or more and more by a simulated time series of long duration. The generation of this series is such that its temporal distribution is the same as that of the river being studied and it presupposes a good knowledge of the laws of statistical distribution which are most suitable for the flow regime of that river.

(2) The influence of man on the various characteristics defining the hydrological regime, including those concerning sediment transport and water quality. It would be advisable to fit into this type of study those which may be carried out on the influence of man on the bal­ance of ecosystems. This diverges a little from the domain of hydrology, but studies of this nature ought not to be neglected.

The first set of problems may often be solved from the results of studies made on re­presentative basins, and the second set by data gathered on experimental basins.

KNOWLEDGE OF THE HYDROLOGICAL REGIME UNDER STATIONARY CONDI­TIONS

We prefer the expression 'the hydrological regime under stationary conditions' to that of 'the hydrological regime in the natural environment'. Only rarely does one deal with a true natural environment. In a catchment there is land under cultivation, forests which are man­aged to a greater or lesser extent and built-up areas. Occasionally this has been stable for centuries. Main roads are a little more impermeable than in the past but the change in the behaviour of some basins has been small for at least a hundred years. Generally the hydro-logical regime has not changed, with the result that the long period of time series provided by the networks has some measure of consistency, as would be the case in a natural environ­ment. On the other hand, in other areas evolution is so rapid, and the hydrological effects so significant, that it is impossible to consider the catchment as being in a stationary state. We will return to this subject later.

Under stationary conditions the engineer has recourse to the data from the hydrometric and rainfall networks, but in many cases the network data do not provide answers to all the questions posed by the management project.

Where large basins are concerned it frequently happens that studies may be carried out using the results from sufficiently reliable neighbouring gauging stations. However, for very rare frequencies, in particular for the determination of the design flood, the hydrologist may often be taking a serious risk, even when using a series taken over a period of 70 to 80 years.

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Where small water courses are concerned the situation is much more difficult, as even in developed countries there are few series of high quality flow data extending over several decades. It is rare for a network of gauging stations to provide the completely reliable data so necessary for a management project. In developing countries the situation is worse. The reasons for this are simple:

( 1) Small rivers are seldom equipped with gauging stations as part of the national net­work. The choice of records from a few representative stations is difficult and, in practice, is rarely made in a rational way.

(2) The accuracy and precision of the results are very much inferior to those from sta­tions on large rivers. The variations in flow are very rapid and special arrangements are need­ed to measure flood flow. It takes only very little to modify the cross section sufficiently for the rating curve to become unusable. In short, almost everywhere in the past, studies of small water courses have been greatly neglected.

Small watercourses It is precisely for these small rivers that representative basins are of greatest service. In gen­eral, a study of a representative basin is not started for the study of one management scheme; often it would cost as much as the management scheme itself. A regional hydrological study is designed by equipping two or more representative basins, the aim being to estimate values for a particular region where a fair number of management schemes are envisaged. On a na­tional scale, the whole country is equipped with a certain number of representative basins. They are selected after the country has been divided up into hydrologically homogeneous zones, and from the results of these basins one may proceed to studies of syntheses. Suffi­ciently reliable quantitative values may be drawn from these studies for most civil engineer­ing projects.

If only surface water resources are taken into account the three most useful characteris­tics are: the average annual flow, flood flows, and the minimum annual flow.

The average annual flow often correlates with the depth of annual precipitation, and the correlation may be sufficiently close for one to be able to use a regression to estimate one from the other, but only when the depth of annual precipitation is much greater than the runoff deficit. The scatter is great, especially in arid and semiarid zones: the relation between depth of runoff in millimetres and depth of precipitation often varies between 0 and 15 per cent. The runoff deficit, the difference in millimetres between the depth of annual precipi­tation and runoff, is nearly equal to that depth of annual precipitation. In these conditions, knowledge of the runoff deficit and even its spatial distribution will be of little help, where­as a representative basin may provide all the necessary data for the study of average annual flows. We will now give as an example the general study of flows in the tropical African Sahel.

In these arid regions runoff comprises a series of floods without permanent flow. The correlations between rainfall and flow on the annual scale are not usable. Girard (1975) has perfected a simplified model which permits the determination of the depth of runoff for each individual flood from the depth of precipitation for each storm at a point situated to­wards the centre of the basin and from the depth of the preceding precipitations. The depth of annual runoff {ox the volume of runoft) is the sum of the depths of runoff corresponding to the various storms. It is sufficient to use as an input to the model the daily precipitation data from a raingauge station which has been observed for several-decades in order to obtain a long series of average annual flows and consequently average annual flow rates.

The model has been tested on several representative basins, some of which have been carefully observed. For one of the latter drainage basins, that of Kadiel (in Mauretania), we have reproduced one of Girard's graphs representing the depth of annual flowi? in terms of the depth of annual precipitation P(Fig. 1). The basin is sufficiently impermeable and the runoff values obtained are fairly realistic. In these conditions, if the accuracy of the simpli-

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fied model's results is acceptable for an individual flood flow then it is very adequate for the estimation of the total annual flow.

In Fig. 1 established under good conditions, it may be seen that the correlation between E and P—if it is significant— is too inaccurate to establish directly a regression with the ob­servations made over two or three years. Also it may be seen that it is difficult to estimate the average value of E with observations made over two or three years.

E E

run

off

a

nn

ua

E

tota

l

3 0 0

2 0 0

100

0

l

o Observed values

• Computed values

* o 1966

1964 / O / • • /

• / * 1965 * * * / *

h - : / . / * O 1967

/ •

400 600 800

P annual prec ip i ta t ion depth in mm

Fig. 1 - Total annual runoff related to annual precipitation for the representative basin of Kadiel.

By using the model, however, it is possible to reconstruct a series of around forty values of E with which the parameters of the statistical distribution of annual flows can be cal­culated.

In many instances it is not necessary to have such good conditions as those in the re­presentative basin of Kadiel in order to evaluate the depth of the average annual flow, and to arrive at an outline of its temporal distribution curve. We can mention the example of the

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Abou Goulem representative basin (in Chad) on a rocky subsoil with mostly porous soils. Here the quality of observation data was poor. It was only possible to make use of a single year of rainfall and flow readings. This was enough to set up the simplified model which transformed the rainfall into flow from the storm depth. Annual flows were then determined from daily precipitation with an accuracy acceptable for this type of basin with low flows— where it would almost be enough to determine the order of magnitude of the flows.

Thus it has been possible to calculate the median flows for most types of small basin in the sahelian zone.

Representative basins in this case enable much better results to be obtained. For small reservoirs it is often asked what the annual volume is in a 1 in 10 dry year and in a 1 in 10 wet year. Now representative drainage basins, at least in this climatic zone, allow calculations to be made of annual volumes for these frequencies since flows are calculated storm by storm. For very wet years the method is less reliable because it is difficult to extrapolate from the observations made during a drier period due to the effect of a much more saturated terrain. In point of fact one can obtain the distribution curve. In this way it has been possible to draw diagrams like Fig. 2 which shows the distribution curves for several different 25-km2

basins in the Sahel. These range from highly permeable sandy basins to basins of very low permeability. Without any representative basins it would have been impossible to obtain these results.

For areas of from 100 to 500 km2 the methodology is far more tricky. It is difficult for convective tropical storms to represent rainfall on the basin by means of data from a single raingauge. It is necessary to make use of the data from representative basins and at the same time to make use of the sparse runoff data from the basins in the network.

Where estimation of high flows is concerned the 1 in 10 frequency is often taken into consideration for small drainage basins. In tropical zones the flood flows very often corre­spond to surface runoff for the very high frequencies. So this is an instance when the unit hydrograph method is most easily applied. On a representative basin where observations have been made for three years, one can reliably determine three parameters from the unit hydro-graph: time of rise TR , time of surface flow Tg and ratio K of the peak discharge and average value of the surface flow rate during the time 7#. In the same way it is possible to predeter­mine the value of the volume of surface runoff or of the coefficient of surface runof f^ from the characteristics of the storm generating the flood flow. This is done either by using the residuals method taking the depth of precipitation as the principal factor, with antece­dent precipitation indices representing the soil moisture and intensity of rainfall as second­ary factors, or by using more elaborate models.

In any case in this way one can determine the volume of the flow and the shape of the hydrograph, and thus the maximum flow for any given storm (these simplified models are often valid only for heavy storms).

In this way it is possible to reconstruct the 10-year flood by working from the 10-year storm and taking certain precautions. This is not without risks, for without precautions one may calculate a flood flow with a frequency either higher or lower than the 1 in 10 frequen­cy. It can also be done by reconstructing the whole series of flood flows from the data from a raingauge station used for several years and, by the study of the statistical distribution of these flood flows to deduce from this the 10-year flood flow or the flow of another frequency.

When one has determined the characteristics of the flood flow on a representative basin it is then necessary to generalize. This is done by using the data from several drainage basins in a homogeneous region, if it is a regional study, or for a set of homogeneous regions if the study is made on a national scale. Occasionally only the zones which a priori present the most dangerous flood flows are considered.

The different parameters of the rainfall/flow model are therefore determined in terms of the physiographic characteristics of the basin and its rainfall regime. In this way one plots graphs similar to Figs. 3 and 4 which were established for the Sahel in 1965.

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Figure 3 provides the coefficient of surface runoff for the 10-year flood flow in terms of a permeability index, an index of slope and the area of the basin; the vegetation cover varying very little over the whole sahelian zone. Figure 4 provides the time of rise as a func­tion of the slope index and the area of the basin.

0,01 0,02 0,06 0.1 0,2 0,3 0,4 0,5 0,6 0,7 0,8 0.9 0 .95" 0,98 0,99

Frequencies '

Fig. 2 - Total annual runoff for basins of 25 km2 in the sahelian zone.

The most difficult problem is to find one or more quantitative indices which permit the determination of the permeability characteristics of the whole basin, keeping in mind the fact that these basins are not homogeneous.

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These few examples concerning the complex zone of the Sahel show that through re­presentative basins it is possible to obtain quantitative results which have been verified by numerous control studies.

Representative basins are far less attractive when it comes to making a direct evaluation of minimum flows, because the geographical transposition of the results is frequently diffi­cult and presents too many risks. Fundamental research on the groundwater increment and on depletion does, it is true, facilitate this kind of study but it does not bring direct solutions. On the other hand, it is often easy within the limits of hydrometric networks to include sys­tematic programmes of measuring base flow over a good number of small basins which supply data useful to management.

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Waraniene

1962

Waraniene

Waraniene

1969

Doka

Cultivated areas

Anacards

Teak

Doka

Savannah witch

Q J Forest shrubs

Fig. 5 - Maps showing changes in land use in the representative basin of Korhogo on the Ivory Coast.

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Sediment transport in stationary conditions may be studied without too much difficulty in a representative basin, thanks to the continuing presence of the field officers. The results obtained may often be transposed from one basin to another, whereas in developing coun­tries the study of sediment transport on small drainage basins using existing networks of sta­tions would pose serious problems.

Representative basins may provide answers to most hydrological problems concerned with the management of small water courses and, except in the case of basic networks fully equipped with automatic instruments, they are the only means of doing so.

H ' r observed H r corrected

1962-1967 • 1968-1971 o

I-,

200

100

800 1000 1200 1400 1600

Fig. 6 - Correlation between total annual runoff (H?) and precipitation (P\) in the rainy season in the representative basin of Korhogo: Hj. =f(JP{).

Large rivers Calculations are made from the data from hydrological networks, but, in the case of large management projects, the hydrological characteristics must be determined accurately and the frequencies to be taken into account for the design flood are usually very low. In these conditions it is essential to be thoroughly conversant with the regime of the river, not only at the dam site but also over the whole basin. If the hydrometric network is sparse and/or if it has only been set up for a short time, some well-sited representative basins may provide precious information.

In the case of the dam project of Sounda on the Kouilou in the Congo (basin area 55 000 km2) the stations in the network had only been set up for five years. The two main stations had been managed and operated very carefully but the determination of the design flood, the return period of which in theory may exceed 1000 years, posed some difficult problems. An idea of the response of the various parts of the basin was wanted for a period of exceptional rainfall. The basin comprised four parts: a zone of limestone, a zone of sand and sandstone which was extremely unfavourable to surface runoff, a forest zone on crystal-

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line rocks and a zone of savannah on limestone-schist which had a very bad reputation as far as flood flows were concerned. Two representative basins had been studied, one in the forest zone—that of the Leyou—the other in the limestone-schist—that of the Comba. They allowed an estimation to be made of the limiting value of the drainage ratio in the case of a season of exceptional rainfall, and this provided a far more sound basis for the study of the volume of the exceptional flood.

From the foregoing it may be established that the use of representative basins must not be limited to the study of the problems of fundamental research. As a matter of fact, if at the start of planning and equipping these basins one had provided the elements for evaluat­ing the common hydrological characteristics (average annual discharge, total hydrological balance, flood flows and low flows) then these may directly contribute some solutions to practical problems.

STUDY OF MAN'S INFLUENCE ON THE HYDROLOGICAL CYCLE

It is hard to find a basin in a natural state, even in undeveloped countries with a low popula­tion density. It is a frequent occurrence in these countries to find a small dam in the middle of a basin which otherwise would be very well suited for study as a representative basin. It is still more difficult to find a basin from 5 to 10 km2 in size in a dense tropical forest area which may neither be managed nor altered in the five years to come.

The stationary state, as far as soil management is concerned, tends to be an exception, and the following example shows this. In 1962 our service had equipped a representative basin at Korhogo on the Ivory Coast in the savannah zone, and as we had a difficult research programme ahead the basin was observed for ten years. After several summary interim re­ports made every two or three years we wanted to bring out a general report on the runoff characteristics of the area. It was then established that the conditions of vegetation and soil could not be accepted as stationary. Figure 5 shows a sequence of three maps of the basin which give the evolution which had taken place. This shows that the proportion of the slopes under cultivation has increased, and cultivation has developed at the bottom of the valley. One section of the basin, after deep digging, has been transformed into anarcardium and teak plantations and, of course, the hydrological characteristics had been modified. Camus et al. (1976) have shown that, even when simplifying the study of the changes in this basin, the period over which observations were made must be divided in two parts: 1962-1967 and 1968-1971. Figure 6 shows the differences in the hydrological behaviour with regard to one simple element: the depth of annual runoff (If). H was determined as a function of depth of annual precipitation, with a correction to take into account the depth of the previous year's precipitation. Two successive regression curves are significantly different. The development of land comprising the teak plantations caused considerable modifications to the soil profile. This clearly increased infiltration and consequently the losses by differing évapotranspiration amounts.

These transformations were brought about by primitive hand methods and, originally, it was a question of a cultivated savannah and not of a forest.

This example was given to demonstrate that hydrologists often work on drainage basins in evolution without realizing it, and this evolution is all the more dangerous because it is progressive. Cut down a forest and replace it with grassland and the hydrologist will be on his guard. He will be a good deal less vigilant in the case of less dramatic changes; more es­pecially where long statistical series are available. These series have been analysed and values have been reached for 100-year floods or even 1000-year floods. These values are considered valid and it is supposed that they will even be improved by the pursuit of better quality ob­servations. Now very often this is a mistake: the basin is no longer the same as before and

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the long statistical series which is looked for is not homogeneous. What is more serious, this will not even be suspected.

That is not to say that in regions where man's influence on the hydrological regime is significant, observations on the basic hydrometric network may be neglected. On the con­trary, they are more necessary than ever, because the safety margin between the water re­sources and the requirements for water will continually diminish. It is therefore more and more urgent to try and acquire quantitative data on the modifications to the hydrological regime.

Most often studies are undertaken from the start of important management projects on drainage basins, preferably they should start earlier. In either case the data from the basic hydrometeorological networks cannot be used. Two methods can be employed: studies made on experimental plots and studies on experimental basins. In this case the sense of the word 'experimental' is clear, the plot or drainage basin is the object of experiments: the physio-graphical conditions are modified deliberately. One cannot keep a passive attitude as in the case of a representative basin where, on the contrary, the basin cannot be made the object of experiment.

However, the equipment of the basin or the plot entails considerable expense, and this leads one to restrict as far as possible the area to be studied. In addition, in order to ascertain the influence of the different factors as accurately as possible, one must preferably consider a homogeneous medium. That is why this kind of study is often limited to observations and measurements made over experimental plots with or without replication.

However, a plot, or even a lysimeter, does not permit the study of a hydrological bal­ance which is comparable to that of a drainage basin on the scale of a number of square kilo­metres, or even 1 or 2 km2. The plot is an open system and the lysimeter is not, as it is al­most always too restricted in size. Whereas the substratum of the basin is impermeable and the lateral changes insignificant in the zone of soil moisture variations, the experimental basin permits a complete hydrological balance. The drainage basin allows consideration not only of the conditions of runoff from the interfluves but also within the hydrographie net­work. The plot gives no information on the form of the flood flow hydrograph and its evolu­tion. This type of study is made possible on the experimental basin by means of the extend­ed timing of hydrological events linked with the increased area. Here there is also the possi­bility of intervention in that very often the bottoms of the valleys are the object of manage­ment schemes.

For sediment transport the experimental plot accounts for sheet erosion but not for ero­sion in gullies, and it is seldom able to provide details about the colluvium at the bottom of slopes. The representative basin gives a more comprehensive idea of the balance of sediment transport. On the other hand it gives a poor indication of the erosion of interfluves, unless it is extremely small. This is the reason why it is useful to provide some erosion plots or micro-basins (of a few hectares in size) on an experimental basin.

A drainage basin by the very nature of its characteristics imposes constraints on the an­alysis. Studies on plots of land escape these constraints to the extent that the selected site is chosen in terms of the proposed experiment, and consequently, the results obtained are more satisfying from a theoretical standpoint because they are more systematic and of a more an­alytical nature. This is a further reason for equipping one or more plots in an experimental basin.

In brief, the experimental basin, whatever its size, is a small complete valley which fre­quently comprises all the morphological elements of a far more important valley. Thus it constitutes a sort of reduced model of a vastly greater whole, and permits an easy regional extension of the results. This is particularly important in the case of complex regional man­agement schemes where the drainage basin comprises zones of diversified agricultural devel­opment, industrial establishments and modern built-up areas.

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To conclude, the experimental plot is most useful, often indispensable, but it is not in itself enough, and one is led therefore to set up experimental basins which, for the reasons given earlier, one makes as small as possible.

The best known of these experimental basins (and probably the oldest) are those which have been set up by foresters to study the effects of deforestation or forest management on water resources: annual runoff, flood flows, minimum flow. However, experimental basins are used for the study of many other modifications to the natural environment, and in them not only the variations in discharge are studied but also the problems of water quality.

Whatever the type of experimental basin, one attempts in the analysis to eliminate the influence on the hydrological characteristics of the singularities affecting the climatological elements during the observation period. The comparison of the hydrological characteristics, before and after treatment of the basin, will be effected when considering either the averages of one of the characteristics corresponding to a very long observation period (for example, the average of the mean annual flow), or a value of given frequency (for example, the flow rate of the 10-year flood), or else an element from the transformation model from rainfall to flow (for example, the regression line as shown in Fig. 6).

Equipped with these elements, one may then pass on to the complete study of the re­percussions of the proposed modifications on the water resources of a larger zone. At this stage of the study one must not lose sight of the problems of scale. It is not always possible to extrapolate to infinity, and this, as we have already said, often prescribes the linking of the experimental plot with an experimental basin.

It is not within the scope of this account to' present the various types of experimental basins, nor the results which each yields. However, I should like to stress the following points:

(1) The experimental basins constitute an irreplaceable tool for the study of man's in­fluence on water resources, and for this reason it is necessary to dwell on their usefulness.

(2) The number of these basins is almost always insufficient in relation to the import­ance and urgency of the problems posed by the changes to which we are subjecting our. un­fortunate planet.

(3) The selection of basins and their management, like the analysis of runoff factors, pose difficult problems, and by taking precautions it is possible to transpose the results from one country to another, and so one cannot encourage enough the exchange of information in the field of experimental basins.

(4) The research workers who are working on these basins are generally most enthusi­astic about their researches but do not always apply themselves sufficiently to the swift extraction of the practical recommendations derived from their labours.

In a perpetually changing world it appears that studies on experimental basins, despite their high cost, have a brilliant future, especially if, as should be the case, one takes into ac­count both the influence of man's actions on water resources and on the environment.

REFERENCES

Camus, H., Chaperon, P., Girard, G. and Molinier, M. (1976) Analyse et modélisation de l'écoulement superficiel d'un bassin tropicale. Influence de la mise en culture Côte d'Ivoire, Korhogo, 1962-1972. Travaux et documents ORSTOM, Paris.

Girard, G. (1975) Les modèles hydrologiques pour l'évaluation de la lame écoulée en zone sahélienne et leurs contraintes. Cahiers ORSTOM, série Hydrologie XII, no. 3.

BIBLIOGRAPHY

Dubreuil, P. et al. (1972) Recueil des données de bases des bassins représentatifs et expérimentaux—Années 1951-1969: ORSTOM, Service Hydrologique, Paris, 916 pp.

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Rodier, J. (1975) Evaluation de l'écoulement annuel dans le Sahel tropical africain. Travaux et documents ORSTOM, Paris.

Rodier, J. and Auyray, C. (1965) Estimation des débits de crues décennales pour les bassins versants de superficie inférieure à 200 km2 en Afrique Occidentale. Comité Interafricain d'Etudes Hydraulique, ORSTOM, Paris.

UNESCO (1970) Representative and Experimental Basins (edited by C. Toebes and V. Ouryvaev). Studies and reports in hydrology: UNESCO, Paris, 348 pp.

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