Transcript
MCROFKiHE REFERENCE LIBWltRY
A project of Yoltinteers in Asia
.*
Soil Conservation: Project design and lmplementation Usina l&ur Inten.sive Techniques By: Bernard Leblond & Laurent Guerin UNDP-iLO/INT/81/844
Published by: International Labour Office IL0 Publications CH-1211 Geneva 22 SWITZERLAND
Available from: International Labour Office IL0 Publications CH-1211 Geneva 22 SWlTZE,RLAND
Reproduced with pormission. Reproduction of this microfiche document in any form is subject to the same restrictions as those of the original document.
iJNDP-ILCl/INl-/“8l/LWl
Interregional Project for Implementation and Evaluation of Special Public Works Programmes
ONSERVATION PROJECTDESIGNAND IMPLEMENTATION LJSINGLABDLIR INTENSIVETECHNIQIJES
UNITED NATIONS DEVELOPMENT PROGRAMME
\
/
INTERNATIONAL LABOUR OFFICE
Bernard
LEBLONO
Laurent
GUERIPI
Geneva
1983
UNDP-lb3/INT/81/044 Interregicnal Project for lmplemenlation and Evaluation of Special Public Works Programmes
ScllL CONSERVATION PROJECTIDESIGNAND Il’IlPLEMENTATICIN USINGLABOUR INTENSIVETECHNIQUES Bernard LEBLOND, Doctor in Earth Sciences Laurent GUERIN, Adviser in Civil Engineering Emergency Employment Schemes Branch
International
Labour Office
l
Geneva
Copyright
0 International
Labour Organisatio,:
1982
Publications of the International Labour Office enjoy copyright under Protocol 2 of the Universal Copyright Convention. Nrvertheless, short excerpts from them may be reproduced without authorisation, on condition that the source is indicated. For rights uf reproduction or translation, application should be made to the Publications Branch (Rights and Permissions), International Labour Office, Cl-l-1211 Geneva 22, Switzerland. The International Labour Office welcomes such applications.
lS8N 92-2-103395-3 First published 7983 Second impression 1988
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Prmted
by the International
Labour
Offlce,
Geneva.
Swltzetland
%ef ace Soil conservation, of course, occupies an important place, often the most important, in special public works programmes in developing countries. Such programmes aim tr? increase employment and raise the ,ncome of the poorest, essentially through the creation of an infrastructure in rural areas that will improve sgricultural and forestry production, develop communications and generally improve the quality of life. In diew of their employment objectives, the programmes use the available workforce to the maximum, putting the accent on labour-intensive techniques. Such an approach is particularly weli suited to soi! conservation work from, for example, the construction of anti-erosion terraces or banks, to re-aforestation, itself related to the establishment of nurseries. It has been observed that the labour component in such projects is, on average, 70% of the total cost. Community participation is another important aspect that is shared by soil conservation activities and special public works programmes. Soil conservation is not only limited to isolated, individual interventions; to be effective, it must be undertaken at a community level, developed on the largest scale possible and, consequently, involve all the people concerned. Participation, which assumes grass-roots agreement, Is one of the fundamentals of special public works programmes, along with the crucial role played by local Administration representatives and the technical services, in mobilising the workforce. Finally, the place set aside foi so!’ conservation in the special programmes fo’,L:ws from the fact that the latter deal, by definition, with disa,vantaged groups. The zones covered by the programmes tend to be the poorest in natural resources, where ?he soils are progressively degraded as a result of deforestation and erosion. Ir, this context, special programmes can be seen as contributing, not only to reconstituting and preserving small-scale farmers’ capital, that is the land, but also to the protection Df ttie environment. ***********tttt**
The present document, prepared by two experienced consultants, Mssrs Leblond and Guertn, is part of a series of technical documents published by the International Labour Office within the framework of the UNDPllLO interregional project for the planning, organisation and execution of special public works programmes. Soil conservation is a very wide and complex subjec: irvhlch has been fully explored from all points of view. The authors have, therefore, limited themselves to a reminder of the basic thinking concerning soil erosion and an analysis of the labour-intensive techniques employed in the battle agains? erosion. Justifiably, then, a large part of the study is devoted to the presentation of a methodology for establishing a soil conservation project model that meets the criteria of special public works programmes. Finally, the authors precisely and succinctly set out the rational organisation and successive stages of a labourintensive operation. *t*.******.t.tt*t
This manual, wi;h its emphasis on a practical approach to the subject, has been written mainly for the national planners, senior engineers and technicians who must establish and execute the programmes in developing countries. Interest in the social and economic aspects of the programme is becoming more intense daily, and the international community contributes active support in the fields of financial and technical assistance. Long-term in nature but urgent, soil conservation reflects the wish of the poorest communities to preserve and improve their !and heritage, so thai iheir own and future generations’ basic needs can be assured. That, at least, is the desire expressed here and that should be rewarded by wide distribution of this remarkab!e work. The authors have drawn on Iheir practical experience and pay all due attention to the socio-economic conditions sf the populations concerned, and to the provision of appropriate techniques and instruments.
Maurice ldoux Senior adviser Division for global and interregional Projects United Nations Development Programme (UNDP)
e phenomenon of soil conservation is no new. Plato, as early as four centuries before ou age, deplored mountain erosion in Greece, bu the phenomenon has now reached preceden ted proportions, and, should it tinue at the current rate, one thhr arable land will be depicted twenty years. servation schemes in PROGRAMMES advantage of responding to mic imperative and of prouse of unskilled labour for
uctions for the
rts of erosion a standard
ice: 20 Swiss francs ISBN 92-2-103395-3
Page INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . CHAPTER A.
1
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..I....
GENERAL PRINCIPLES
3
A.I.
THE DIFFERENT FORMS OF SOIL DEGRADATION . . . . . . . . . . . . . . . . . . . . . .
3
A-2.
RAINFALL EROSION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
3
2.1. 2.1.1. 2.1.2. 2.1.3. 2.1.4. 2.1.5. 2.2.
2.2.1. 2.2.2.
A-4.
A.5.
. . . . . . . . . . . . . . . . . . . ..I......
3
Rainfall ................................ . ..*.. Nature of the so?1 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..I Slope of the land . . . . . . . . . . . ..*......*...... . ..I... .. Vegetation . . . . . . . . . . . . . . . . . . . . . . . . I.................. Man . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...* . . . . . . _ . The effects
of rainfall
erosion
5 5 6
........................
6
Mechanical effects ................................... Chemical effects ..................................... Integration
of rain
11
3.1.
Wind erosion
3.2.
The effects
water
factors of wind
erosion
factors
6 7
SOIL EROSION BY WIND . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..I
11
OTHER FORMS OF SOlL DEGRADATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
12
4.1.
Excessive
humidity
4.2.
Excess
4.3.
Unsuitable
4.4.
Socio-economic
of toxic
erosion
11
............................
.............................I.......
12
..................................
12
......................
12
salts
agricultural
practices
.............
73
LAND USE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
13
aspects
of soil
degradation
5.1.
Land employment
. . . . . . . . . . . . . . . . . . . . . . . . ..I.............
5.2.
Land classification
. . . . . . . . . . . . . . . . . . . ..I..............
5.2.2.
B-1.
erosion
7
5.2.1.
CHAPTER B.
in rainfall
.............*
2.3.
A-3.
Factors
13 13
Classification system developed by the Soil Conservation Service of the US Department of Agriculture . .. ... .. . .. ". . . . . .. .. .. . . . . . . . . .. ... . "S....,...... Other classification systems . . ..I........
EROSION PROTECTION TECHNIQUES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . CONSERVATION OF ?ROTECTED LAND . . . . . ..I....................... 1.1.
1.1.1. 1.1.2. 1 .1 .3. 1.1.4. 1.1.5. 1.1.6. 1.1.7.
1.1.8. 1.1.9.
Forests
13 17 21 21
................................................
Role of the forest in soil conservation mechanisms ............ Main forest species used in afforestation Preparing a reafforestation plan ..................... Ground preparation .................................. Seed preparation ..................................... Afforestation using the direct sowing method ......... ............................ Afforestation by planting Maintaining the afforested area ...................... .............................. Plantation conservation
.
...
21 21 22 27 28 ;: 32 33 40
--Page 1.2. 1.2.1.
1.2.2.
B.2.
..............................................
43
.....
of pastures in soil conservation mechanisms R31e Techniques for the creation, conservation and ............................ improvement of pastures
2.1.1 2.1.2. 2.1.3. 2.1.4. 7.1.5. 2.1.6. 2.1.7. 2.2. 2.2.1. 2 >.2. 2:;.3. 2.3.
2.3.1. 2.3.2.
2.3.3. 2.4. 2.4.1. 2.4.2.
2.5. 2.5.1.
2.5.2. 2.5-Z.
2.6. 2.6.1. 2.6.2. 2.7. 2.7.1. 2.7.2. 2 .7.3.
Cover
44
..................................
procedures
Biological
44
............................................. Mulching ........................................ Crop rotation ............... ....................... Mixed cropping Lea crops ............................................ ........................ Rotation field-strip cropping ............... organic reserves Increasing the soil's Farming
practices
......................................
46
Contour ploughing .................................... Contcur or slightly inclined ridging ................. ............................ Subsoiling and chiselling Defence
networks
terraces
Terraces Terraces Drainage
3.1.1. 3.1.2. 3.1.3.
3.2. 3.2.1. 3.2.2.
3.3.
47 49 49
The role of defence networks and the ........................................... Main types ........................................... Dimensions Bench
47
....................................... systems
used
....
.........................................
constructed const.:ucted works
at a single progressively
go .................. .................
.........................................
Characteristics of gully erosion and the role of control works ................................... ....................... Determining run-off conditions ........................... Main types of construction Bank,
channel
Stabilising Protection Correcting
49 50 54 60
and gully
protection
banks with vegetation of banks by construction the
slope
of water
64 65 69 70
.....................
courses
.................... works ............
70 70
..................
73
Role of constructions ................................ Type of work ......................................... Prlnclples of calculating structure dimensions
73 73 78
WIND EROSION PROTECTICN TECHNIQUES ........................... 3.1.
45 45 45 45 45 45 46
..........................................
CrOpS
Q3 43
CONSERVATION OF CROP LAND .................................... 2.1.
B-3.
Pastures
Dune stabilisation
.....................................
Conventional techniques for stabilising maritime dunes ..................................... Techniques for the stabilisation of continental dunes .............................................. Dune stabilisation by a coating of bituminous ........................................... products Crop
land
protection
...................................
........................................... Windbreaks Other techniques ..................................... Pasture
protection
.....................................
.......
81 81
81 82 83 83 83 83 04
Page REHABILITATION TECHNIQIJES FOR WATERLOGGEDSGILS .............
CHAPTER C.
85
C.I.
AIMS OF DRAINAGE .............................................
85
c-2.
DIFFERENT TYPES OF DRAINAGE ..................................
85
2.1.
Open ditches
...........................................
85
2.2.
Underdrains
.............................................
86
2.2.1. 2.2.2. 2.2.3. 2.2.4.
2.2.5. 2.2.6. 2.2.7.
2.2.8.
2.2.9.
c.3.
2.3.
Mole drai:lage
2.4.
Subsoiling
i; 88
.............................................
89
.......................
Water movement in a drained
soil
3.2.
Determination
............................
3.2.4.
3.2.5. 3.3. 3.3.1. 3.3.2.
3.3.3. 3.3.11. 3.3.5.
of basic
data
91
Causes of wetness .................................... Optimal water table level ............................ Permissible submersion time .......................... .......................... Type of soil - permeability Intrinsic flow rate of network .......................
91 92
.......................
95
Calculating
the drainage
network
;'3 94
Network design ....................................... Drain depth .......................................... Drain spacing ........................................ Drain diameter and length ............................ ............................ Calculation of collectors
95 96 97 101 101
PRELIMINARY STUDIES .......................................... 1.1.
Aims ........................................
1.2.
Situation
1.3. 1.3.1. 1.3.2.
89 89
METHODOLOGY FOR SETTING UP A SOIL CONSERVATIONPROJECT ......
1.2.1. 1.2.2.
D-2.
i; 87
..........................................
3.1.
3.2.3.
D.1.
i"6 87 a7
DETERMINING THE CHARACTERISTICS OF A DRAINAGE NETWORK........
3.2.1. 3.2.2.
CHAPTERD.
....................................... Fascine drains Stone slab drains .................................... ........................... Drains with stone backfill Wooden box drains .................................... Peat drains .......................................... Earthenware piping drains ............................ .................................. Concrete drainpipes .......................... Bituminous fibre drainpipes ................................... Plastic drainpipes
103
. ..........
....................................
analysis
the extent
of possible
measures
.Damage assessment .................................... ................................. Envisaged investment
DRAFT PROJECT ................................................ 2.1.
Aims ...................................................
2.2.
Analysis
2.3.
Hypothesis
of basic
data
.................................
of improvements
.............................
103 103
The physical context ................................. ........................... The socio-economic context Assessing
103
103 106
..............
106 106 107 108 108 108 109
Page 2.4. 2.4.1, 2.1!.2. 2.4.3. 2.5. D.3.
..................................... The expenditures Income ............................................... Balance sheet ........................................ Selection
of improvements
110 110 110 111
~................~............
111
3.1.
Objectives
111
3.2.
Field
3.3.1.
3.3.2.
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
studies
................ ... ..... ....... ...........
Topographic work ..................................... ....................................... Survey borings Project
document
111
111 112
. . . . . . . . . . . . . . . . . .._...................
112
Written documents .................................... Drawings .............................................
112 112
PROJECT IMPLEMENTATION ......................................
113
GENERAL SITE ORGANISATION ....................................
113
1 .I. 1.1.1.
1.1.2. 1.2. 1.2.1. 1.2.2. 1.2.3. 1.2.4.
1.2.5. 1.2.6. 1.3. 1.3.1.
1.3.2. 1.3.3. 1.4. 1.4.1.
1.4.2. 1.4.3. 1.4.4.
E.l.
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
111
3.3.
E.l.
analsysis
THE PROJECT . . . ..-...-......................=.................
3.2.1. 3.2.2.
CHAPTERE.
Econo;nic
Survey of local
conditions
and site
2.7.1. 2.1.2. 2.1.3.
.....
.................................. Natural constraints ................... Technical and economic constraints Project
planning
.......................................
............................... Objectives of planning ............. Forms of planning and their requirements Planning procedure ................................... Bar chart or GANTT chart ............................. ..................... Time and location chart planning .................... Network or critical path planning Setting
up the site
....................................
113 113 114 115
?15 116 117 118
119 121 124
Construction of access roads ......................... ....................... Constrtiction of site buildings Plant installation ...................................
124 125 125
management . . . . . . . . . . . ..*..........................
125
Site
................................. Management technique Personnel management ................................. Incentive system ..................................... Role of project management ...........................
TOPOGRAPHICALSTUDIES . . . . . ..a...... 2.1.
reconnaissance
Topographical
survey
. . . . . . . . . . . . . . ..-.......-
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..-
Planimetric survey ................................... Levelling ............................................ Composition of a topographic survey team and survey standards ...................................
125 126 130 131
132 132 132 133 134
Page E-3.
Preparation
of
the
ground
plan
3.2.
Preparation
on the
ground
..............................
3.2.1. 3.2.3.
3.2.4. 3.3.
4.2.
134
Main staking out ..................................... ................................... Additional staking ....................................... Staking report ..................................... Displaced stakes Personnel
requirements
and work
135 135 135 135
.................
output
Clearing the the works Stripping
over the area covered . .._.........._...........................
land
by 136
.................................
- suhsoiling
5.1.1. 5.1.2. 5.1.3. 5.2. 5.2.1. 5.2-Z. 5.2.3. 5.2.4.
General
comments
137
Tools
.............
Labour
5.5.
Earth--moving
141 141 141 141 142
. . .._._........................................
142
....................................
organisation methods
144
.......................
and outputs
..................... '.'rench digging and spoil removal .......................... Loading and reworking spoil Spoil haulage ........................................ .................. spreading and compacting Unloading, Bank grading ......................................... Examples
of earthwor'cs
.................................
of
Construction
144 144 146 147 148 149
149
a canal or ditch ..................... of earth dams ...........................
Construction
138 138 138 139
...................................... tools loading earth .............................. ............................... soil haulage ............................ soil compacting
Trenching Tools for Tools for Tools fcr
5.4.
5.6-i. 5.6.2.
and handling
. . . . . . . . . . . . . . . . . . . . . . . . . . ..-.....................
Manpower
5.6.
type
138
.................................. Land classification Bank gradients ....................................... .............................. Bulking - consolidation
5.3.
5.5.1. 5.5.2. 5.5.3. 5.5.4. 5.5.5.
on soil
136 136
FXECUTION OF EARTHWORKS...................................... 5.1.
E.6.
134
GROUND PREPARATION . . . .._............_.-...................... 4.1.
E-5.
.........................
3.1.
3.2.2.
E-4.
134
MARKING AND STAKING OUT THE STRUCTURE .-..............._......
149 151
IMPLEMENTATION OF REAFFORESTATION WORK . . . . . . . . . . . . . . . . . . . . . . .
151
...........................................
151
6.1.
Nur-sery
6.2.
Planting
6.3.
Construction
6.4.
Plantation
6.5.
planting Exampies of a plantation: lines ..............................................
6 -6.
work
Productivity
............................................... of
forest
maintenance
norms
tracks
152
..........................
152
.................................
.....................................
along
153
contour 153 154
-x-
Page E-7.
.._....e
IMPLEMENTATION OF DRAINAGE WORKS .............. 7.1.
Installation
7.2.
Tracing
7.3.
Calculating
7.4.
Trench
7.5.
Trimming
7.6.
b-din
7.7.
Manpower and output
E-8.
E-9.
of a drainage out
total
trench
trench
laying
.....................
network
155
.........................
width
155
...............................
depth
trench
bottom
156 157
.............................
and backfilling
the
in manual
trench
drainage
................ work
............
CONSTRUCTIGN OF MASONRY WORK ................................. of masonry
........................
158 160 160 160
8.1.
Differert
types
8.2.
Dry-stone
masonry
8.3.
Normal
masonry
work
....................................
162
8.4.
Gabion
masonry
work
....................................
163
work
work
155 155
.........................................
digging the
.......
.................................
CARRYING OUT CONCRETE WORK ................................... 9.1.
Characteristics
9.2.
Concrete
9.3.
Shu%tel,ing
9.4.
Steel
9.5.
Installing
of concretes
preparation
...........................
...................................
the
....................................
reinforcement
bars
167
167 167 168
..............................................
reinforcement
160
......................
168
169
APPENDICES I. II.
STANDARD PLANS .....................................................
171
BIBLIOGRAPHY .......................................................
205
INTRODUCTION The soil is one of the-essential elements for plant, animal and human life, It changing eilvironment which, .under normal conditions, is is a complex and constantly the result of an equilibrium between the forces of soil formation and erosion. In the humt;s removed from the soil ia usually reconregions covered with vegeta:ion, The natural development of soil with a covering of vegetation is slow; stituted. that around L5,000-12,000 years are required for the development of it is estimated . 30 cm of soil. Man extracts from the soil the main part of his food production but increasing demographic pressure forces him to extend land culti:ration, intensify production and use techniques that are not always in line with the maintenace of soil Fertility. of man's mishandling, the equilibrium is disturbed, erosion Under the effect whole regions are hard hit by this degradation accelerates and, in mar&y countries, disastroua consequences for the physical and and the fall in soil yield - !;ith economic environment. conservation and related afforestation Soil This is due to the fact that, in the importance. has assumed alarming proportions. There is need ecological balance which, in Of and maintenance the taining increased food prod1otion and, indeed, world.
schemes have assumed increasing developing countries, soil erosion for environmen'al preservation itself, is very necessary for mainvery living conditions of the
such soil conservation schemes hold a Being reiatively more labour-intensive, potential for high labour absorption during the construe tion phase as well as contributing to the development of land infrastructure for increased food production. The relevance lies in the high iabour-intensity, quick wage employment generation for unskilled idle rural labourers and resultant infrastructure development. Soil conservation is the outcome of a balance 'between the satisfaction of It is a national problem in view of its social and current and long-term needs. of which far exceeds the technical and oolitical imolications - the solution . Implementation of a soil conservation 'financial capabilities of the farmer alone. programme, if it is to be successful, must be understood and supported by the populaThis also presupposes technical innvoation and collective awaretion as a whole. ness which will come about only after information and education campaigns. The present document does not claim to replace the very abundant literature on this subject to which the reader should refer should he require a deeper knowledge engineers and senior technicians of the subject. Its more modest aim is to assist It contains: responsible for planning and implementing soil conservation projects. a review of the basic data on different types of erosion and control measures making rjtindard methods for the design and planning of intensive use of unskilled labour, operationlaW supervision. projects and, finally, guidelines for site oranisation, Appendices contain a series of standard plans which, although they may, in many are no substitution for the specific . cases, suffice to define the work in hand, It should be emphasised that the studies that should be carried out for each site. plans given are not necessarily the only possible solution to a given problem and that in all cases they have to be adapted to local conditions, customs an,! traditions s which should always be especially with regard to the maximum use of local resource systematically pursued.
-3-
CHAPTER A
GENERAL PRINCIPLES
THE DIFFERENT
A.l. Soil
degradation
excessive
humidity,
The most which
poor
reshape
the
main
basis
agricultural
of
fertile
away the
fine
The wind
may also
covering
with
(low-lying
Other
rivers
their
forms
of
soil's
chemical
countries,
periods
been
climate salination rendered
is
result
fallowing
which
The soil's
the
degradation salts
for
may also
brought
in
Factors
in
cultivation
Atmospheric
rainfall
In
run-off
that
erosion
are
nature
the
soil
but
this
not
renewed
and fertilising
build
up in
nevertheless
case,
is
the
may be due to of
soil not
in
soil
of fertile
the is
irrigation the
it
In many
regeneration
of hectares
effects
production.
pressures.
of poor
and
resultant
agricultural In
or
structure
with
natural
result
conditions rainfail
the
by irrigation this
of
of
an arid
resulting
land
in
have been
way.
RAINFALL EROSION
erosion i, c the
precipitation
surface
be the
Thousands
A.2. 2.1.
are
The sources
of degradation
demographic
allowed
nutrients
and alkalinisation. unfit
of high
components.
ti GibL.a~~ce and thus
spectacular
forms
the
fertile.
aeration
economy.
These
fertile
excessive
less
is
by carrying
degradation.
to continue
degraded.
which
soil
to topographical
soil
agricultural
may carry
soil
main
degradation
more insidious,
the
same effect
plains,
are
and wind
previously
and due either
of wind,
techniques.
tnem ai
of
alluvial
effect
rainfall
top the
were
defective
region's
that
of
This where
the
the
cause
impossibility
are
as the
reduced.
sufficient.
the
the
depositing which
into
over
including
another
components,
degradation
content
exploitation
is
and varied
or
strip
soil,
the
due to
off
may have
The consequences
for
excessive
totally
regions
soil
soil, farming
are
running
particles,
overflowing
yields
soil
as devastating
and even
the
chemical low
just
have
in
irrigation.
of
water
The wind
may be numerous
on cultivation,
Rain
sand deposits
humidity
over-generous
degradation
away larger
the
or unsuitable
of an unprotected
carry
from
soil
production.
land),
leaching
components
sterile
humidity
of
relief.
particles
Excessive
practice
forms
ground
run-off
rain
irrigation
spectacular
away the
this
may be due to
FORMS OF SOIL DZQRADATION
has considerable of
the
soil,
main
cause
destructive the
slope,
of
rainfall
force. vegetation
erosion Other
which
factors
and human activity.
produces affecting
-4-
Rainfall
2.1.1.
The main and
the
characteristics
Rainfall
striking
the
it
to
leads
The
the
soil
compaction
influence
with
of
Annual
rainfall
2.1.2.
:%1ature of The
readily
important
matter
of
by means
intensity
wash
smallest
of
to
still
difficult
which
refers
to
are
to
particles
The
of
a recording
have
in
in
soil
raindrops
rainfall
intensity;
rain
gauge.
increasing
soil
covered
by a film
rain
an effect
quantities
erosion
of
assess
soil
depends
since
it
humidity,
of
water
run-off.
on soil
loss
water
will
and years
rf
soil.
on the
soil's
depends
nature
on nllmerous
texture,chemical
structure,
the
are
proportion
clays
international
and
system
of
the
different
largest
classifies
soil
and
is
parameters,
composition
a particle
size
range
less
-
silts
with
a particle
size
range
between
-
fine
sands
-
coarse
sands
-
gravels
with
Structure separate The of
with
size
a particle
a particle
refers
to
aggregates
cohesion
Henin's
a particle
of
the
the of
the
and organic-
structure
-
the
mean percentage
of
-
the
fraction
of
dispersed
-
the
fraction
of
coarse
size
stable clay
between
USA, it erosion
than
gravel.
0.02
mm
and 0.2
0.2
and 2.0
2.0
mm
individual
"structural the
The
soil.
mm mm
particles
in
the
soil
and shape.
factors
stability" of
which
can
be determined
by
are:
aggregates, plus
loam,
sand.
Recordings in Madagascar have shown that 1.5 mmlmin are rarely erosive, whereas rainfall The figure of 2 mmjmin is the always erosive. occurs. In Arkansas, (6 per cent),
0.02
these
the
mm and
between
of
or
index",
0.002
greater
arrangement
or
in
as follows:
0.002
range
range
different
"instability
1
range
size
size
than
particles
stones
texture
with
with
size
are
clays
slope
with
intense
-
use
intensity
factors
energy with
the
content. Texture
into
rain,
aggregates.
more
larger
of
important
increases
A soil
also
most
kinetic
increases
have
away
the
amount
soil
susceptibility
is
of
the
the
energy tion
variations
the
Erodibility
kinetic
and will
produce
of
frequency.
precipitation
heavier
most
rainfall
one of
result
measured
rainfall
more
the
of
ar'e
is
and demo1
is
increasing
disaggregate
is
amount
intensity
precipitations
intensity
erosivity
soil;
Rainfall
i.e.
Rainfall
frequency.
erosion.
of
rainfall intensities cut-off
is estimated that on uncovered, occurs as soon as the rainfall
intensities of over point above
of less than 2 mm/min are which erosion
loamy soil with a slight reaches 2.5 mm in 5 minutes.
It
is
expressed
by
stability
Stability
is
together
sand
linked
to
due
in
and
the
equation
+ loam" dispersion "clay aggregates - 0.9 coarse
stable
Structural
the
is
an important
particular
alluvial
complex
of
factor
humic
the
in
and clayey
water
also
plays
structure
nature
a role
in
in
reduced
results
run-off
colloids
The chemical
particles.
absorbant
Disaggregation
to
sands
the
and
of
soil
bf
the
which bases
structural soil
erosion. hold which
are 1
stability.
permeability
and
porosity. -.C'ope
2.1.3.
of
The speed erosion
of
the
With
of
the
nature
-
vegetation
-
precipitation
2.1.4.
increasing
rate
and the
ine
a given
-
is
on soil
increases
run-off amount
with
increasing
slope,
and
soil
speed.
of
particles
carried
away
also
vary
in
relation
in
several
slope.
angle
of
the
soil
of
slope,
erosion
intensity
will
depend
on:
cover intensity
Vegetation This
run-off
witn
flow
length
land
rainfall
increases Run-off
to
the
-
a major
factor
in
controlling
soil
degradation
and
acts
ways:
-
By protecting the soil from the direct impact of water drops. When rain water is intercepted by the plant covering before it reaches the soil, the height of its fall is reduced and, consequently, its kinetic energy and destructive effect are smaller.
-
By intercepting some of the evaporates without increasing
-
By inhibiting ground vegetable matter.
-
By enriching porosity. Roots
soil
and,
the
in
particles.
surface. infiltration.
soil
with
particuiar, Their
Dead
water
roots Organic
effect increase matter
rainwater which then the ground run-off run-off
due
organic
material
the is the
matting even
to
of
greater
porosity
resulting
matting
which
fine if
of from
the
remains volume.
the leaf
of
roots
improves
roots they
on the
soil
the
densely
surface
decomposition
and
and accumulated
structure
increase grow
foliage
and
cohesion close
and
to
promote
improves
of the water
soil
structure. 1 stability;
Calcium and sodium
magnesium ions allow ions cause dispersion
flocculation and structural
and,
consequently, disaggregation.
greater
-6-
The effects Forest Forest
growth
soil
has
the
on the
greatest
2 tr, 3 per
covering
of vegetation.
effect
Cent
may also
type
have
in protecting
soil
OrgaIIiC
material.
a significant
effect
of
from
water
provided
the
erosion.
plant
coverage
dense. Fallowing
involved
increased hoed
also
(forest
Crops
plays
a conserving
fallowing,
have
a less
density
of
crop
role
fallowing,
conservational
bare
on the
Resistance
pasture
type
of
vegetation
fallowing).
effect.
Forage
crops.
depending
offers
better
to erosion
increases
protection
than
with
cereals
or
crops. Orchards
trol
do not
constitute
a sufficiently
dense
vegetation
to effectively
con-
erosion. Research
pastures in
carried
with
relation
out
slopes
of
the
density
to
-
100 per
-
40 to 60 per
-
20 per
2.1.5.
cent
around
20 to 36 per
cent
of vegetation
covered
cent
Lake Aloatra,
Madagascar
have
shown
0.026
covered
covered
soil
the
l),
on the
following
Aristida
topsoil
losses
coverage:
soil
cent
(ref.
t/ha/year
4 +/ha/year
soil
12 t/ha/year
Man Man is
often
at
a prime
the
Abusive applies
factor
how it
of is
2.2.
of erosion.
use of
forests
of
are
water
the
rurl-off. soil
may lead
soil
on very
organic
irrational
to
their
steep
material
use of
the
the
destruction;
slopes,
unsuitable
is
from
lost
soil
the
is
same
crops, soil
and
particles
erosion
impact
of
water
Primary
or
tlsplashl'
which
breaks
and 1.50 increases
The finer
pension.
rainfall
due to
on the
di-aggregation
capacity,
the
by wilich
since
effects
60 cm vertically
These
degradation
replaced.
These raindrop
of
mechanisms
Mechanical
rain
soil
and pastures
clearing
the
The effects
2.2.1.
in
origin
to abusive
ignorance
of
depending
Contains
A grabs is
vary
soil
with
the pores
excess
up the
water
rain are in runs
on the
erosion
soil
cm horizontally.
particles
block
and the
droplets
is
particles
soil
due to
and the the
impact
and may project
The energy
released
dispersed
by the
erosive
by soil
of
force the
them up to particle
intensity. more readily the off
soil
surface
carrying
decreasing away the
fine
"splash" the
soil
particles
effect. absorption in
SUS-
-7-
erosion
"Splash" absorbs
a large
Water
which the
streams.
Gradually,
of the
by modifying small
stability
processes
fields
in
As erosion
erosion
erosive
and transporting
and the
gullies
process
is
allowed
are
of
to
sediment
can cause
great
productive -Chemical Added to
particular in
the
loss,
mineral
salts.
of
there
anastomosing
centimetres
are
erosion
not
it
mm
fertile
this
breaking
in
of 0.2
and most
processes
rills
adequate,
down into
or channels
and wider soil
forming
cultivation
however,
when gully
of
water
land
small
occurs,
to the crops
processes
into
sediment
finally,
the
off.
erosion
The erosion
danger
If
or biological the
its
become gullies
ravines.
may be stripped
dams or,
where
The rills
increased.
Dividing
of
are
is
sea.
and silt
fields
more carried
by
Local
deposi-
up drainage
and
flooding.
erosion
significant
Drainage
cultivated
A rainfall per
slope.
is
the
loss
losses
of
of
soil
and destruction
effects
soil
case
top
land,
small
damage to growing
of uncontrolled 1 capacity.
down the
may reduce
such the
required.
the
the
soil.
lakes,
increasing
The end result
2.2.2.
are
and rivers
channels,
its
erosion;
measures
If
place,
the
a few
practices
in
top
takes
streams
irrigation
of
rill
collective
gullies,
erosion to retain
reduces
extensive tion
gully
the
runs
a danger.
deeper
all
which
up to sand particles strip
enormously
progressively
sufficient
significantly
are
to continue or
no longer
collects
vegetation
in minute
grooves
components
by levelling
run-off
water
small
size.
no longer
powers
become
out
of
and biological
is
of
on a watershed
may progressively
or aggregate
continues,
Where rill
hollow
may be employed
which
soil
a sheet
away fine
of erosion
by a covering energy.
the
forms
streams
Cultivation
soil
mechanical
or
may carry
soil.
kinetic
through
diffuse
these
type
or prevented
raindrop's
filter
is
whicrl
This
layers
the
run-off
and depth
diameter.
of
does not
Initially, width
can be reduced
part
land
water
and up to
10 mm on a soaked
may contain 150 g in
soil
components,
up to 50 g of
the
may carry
fertile
off
case
of bare
5-15
kg of
2 in
calcium
nitrate
land. this
fertiliser
hectare. Integration
2.3.
of
An attempt Wischmeier's
at
rain
water
an integration
erosion study
factors of
rain
water
erosion
factors
is
given
in
formula.
1
To give an example of the proportions that this type of erosion can attain, it with a total surface area of 3.3 million km2, 1.4 milis estimated that in India, lion km2 are subject to significant soil loss and 6,000 million tonnes of soil are lost each year from a surface area of only 800,000 km2 (UNESCO Courrier, May 1980). 2 appear
In India, each year,
it
is i.e.
estimated more than
that 6 million is applied in
tonnes of fertile components the form of fertiliser.
dis-
-8-
Fi g. A-1:
Diagram
of
the
main natural
DECISIVE ! ’ ACIIWE
4
\ FACiOAS
in rUn-Off
erosion
MAIN SURFACE TYPE
RAIN GAUGING LESS INFILTRATION
PARAHEIFRS
I---
factors
WATER NASS
I
OURATION OF FLOW FOOD REQUIREHENTS
FLOW RAIE
VARIABLE PARAMIEAS 6 OECISIVE PARARETERS
\
FOOD AND HEATING RE&JIREHENTS I
SOIL ?ELIEt I
1
FA'IOURAGLE FACTORS
I
1
1
ANIHALS
SLOPE
HAN
1 DEGREE OF
DES'RUCTION OF THE VEGElAllUN BAD SOIL
OESTRUCTION OF THE
SLOPE
#ANAGEHENl
VEGETATION
I
VARIABLE PARAMETERS
8 AESULl CLODS
iARIAl3LE PARAHETERS
t RESISTANCE FACTORS
/~
1 /T
DECISIVE PARAHETERS
ANORjiiR”E
-2___2-)
OflSlACLES
ROOTS
PERCOLATION
SlRUClURE
TEXTURE
~,~soIL
STALKS AN0
T Jrs LEA”f I
PERMEABILITY AND CAPACITY
COHESION
FOLIAGE
I
I
UNDERGROUND
AGAINSI PRECIPIlAlION
\
AGAINSI RUN-OFF
OBSTACLES After
This
formula,
when applied
soil
10~s and determine
that
erosion
does not
Wischmeier's
what
erosion
exceed
formula
to a specific the
is
threshold
methods at which
Deloyeand
makes it
region,
control
H.
should it
H. Rebour
possible
to ensure
dangerous.
as follows:
IA=R(h.LSCP) A is
the
R is
the orecipation
It
soil
loss
in
for
a mean annual
For a given
per
erosivity
can be calculated
Generally,
tonnes
acre'
factor
a rainfall
rainfall
(1 American or "rain
or for
index
is
the
short
ton
over
used.
rainfall:
R = Eg x Im 100 where
Eg = kinetic
energy
Im = maximum intensity 1 1 acre
is
equal
of
the of
rain the
to approximately
in rain
feet/tonne/year; in 30 min in 4,000
m2.
= 0.907
kg);
index". rainfails
inches/hour.
1
to estimate
be implemented
becomes
1953 (ref.
a given
period.
- 9 -
To calculate recording
in
the
which
to establish
kinetic
the
rain
is
is
given
it
rain,
is
necessary
down into
segments
energy
a rainfall
of
to have equal
a hyetogram
intensity
in
order
ratio.
between by the
of
br.r,ken
a duration-intensity
The relationship intensity
energy
kinetic
of
(of
regular
intensity)
an{
formula:
Eu = 916 + 331 Log Ih In which: Eu = unit Ih
kinetic
= intensity
The energy which have
energy
in
feet/ton/year
in mm/h
in segment Eh is equal to Eu multiplied The energy fallen during the segment.
In order to calculate section of the curve
Im, it is necessary in which the largest
K or the resistance
is a dimensionless to erosion. These
"soil of
index" a soil
L.S or the "slope index" the angle and length of C or the "cultivation under well--defined where C = 1 (fig.
is the
index" conditions A.3).
factor values
A.2:
Wischmeier's universal L.S as a function of lo
equation the length
which measures the relative are obtained experimentally.
factor.; A.2).
it
indicates
the
of earth loss of cultivated a continually worked fallow
P or the "water and soil conservation index" conservation is practised field in which soil along the line of maximum slope (fig. A.4). Fig.
of millimetres
to mark cn the recording the 30 min number of millimetres of rain fell.
a dimensionless slope (see fig. is the ratio to that of
by the number is cumulative.
is the ratio to that of
(graph giving and percentage
of earth a cultivated
the values of of the slope
effect land land
loss
on a field
the factor (ref. 23))
* 8
Length
of slope
in metres
of
- 10 -
Fig.
~.3:
coefficient
Crop
values
- C
C
Type of crop In
the United
States
non-hoed
crops
plant
covering,
fallow
and
0.6-0.8
(rice-cereals) green
0.3-0.6
manure
depending
on the
condition,
iocation,
climate
0.3-(1.5)
In Tunisia: bare
earth
- bare
fallow
1
land
orchards
0.90
wheat
0.71
rotation
with
0.40
cereals
0.47
fodder rotation
with
improved
pastures
For mechanised of 1.3-1-a.
Fig.
A.4:
Value
of
Slope
%
l-l2.0 2.1 7,o 7.1-12.0 12.1-18.0 18.1-24.0
0‘01
cultivation,
Erosion
P factor:
0.15-0.23
fodder
reduction
water
these
values
coefficient
and soil
should
of
be subjected
soil
conser vation
conservation
index
to a coefficient
remedies
in %
Contour line cultivation L value to be considered: length of field slope
Rotational field strip cropping value of L to be considered: length of field slope
Terraces the earth in the channel is considered lost Value of L to be considered: distance between channels
the earth in the channel is not considered lost Value of L to be considered: distance betwee.. channels
60 50 60 80 90
30 25 3c! 40 45
60 50 60 80 90
30 25 30 40 45
11 -
A-3. Wind erosion
3.1.
SOIL EROSION BY WIND
factors
The erosive
effect
of wind
varies
The ability
of wind
to move soil
At soil
level,
depending
on the
nature
of
the
vegetation
and
soil.
particle
size.
a few millimetres increases It is
is
that
Medium-size
particles
the
of
surface
the
avalanche
effect.
land
number
Vegetation and reduces The soils particular,
fine
soils
the
offer
is
wind.
is
the
best
during
the
cattle
hooves
wind
dry
tends
Crops of the
soil
laminar
as the
for
distance
to move the
finest
on particle
size.
suspension
mm diameter
"creep"
in
of
the
air
a height from
soil
of
the
soil
particles
ana may form
dust
storms
to break
are
particular,
in
of
wind.
soil
the
plays
pastures.
area
force
of
the
process. texture
a role
regions
of which
has an
the
the
coarse
and semi-arid - part
this
saltation
of
effect
greater
breaks
the
those
along; the
it
also
arid
of
since
humidity
vegetation
grazing
carried
limiting
effect
action
The saltation
increases
are
of
a bouncing
surface.
wind
erosion
level
up the
the
thus
in
saltation.
as they
land,
to the
due to over
called
against
and light
carried
phenomenon
to wind
resistance in
are
along
in motion
exposed
the
increase
soil
texture
danger
Wind erosion by loss
of to
erosion
and the
and,
in
and dry
in which
disappears
The constant
action
totally of
surface
and make it
more susceptible
to
is
encountered
on sandy
areas
absence
whereas
roughness
of wind
fine
soil
sufficiently
cultivation
(ploughing,
dense
techniques
banking)
have
coastal
vegetation. Repeated season
which
tend
maintain
a protective
workto or
effect.
erosion
has a deleterious
structural
of
also
techniques can also cause erosion. soil fragmentation during the dry
of erosion
surface
The effects
leads
wind
climates,
and variou? farming soil and excessive
increase
-
in
The soil's
period
season
required depending
protection of
occurs,
temperate
due to the
3.2.
or
susceptible
dry
is
and
erosion. In
ing
area
sands.
a major
flow
intensity
height.
by a phenomenon
roll
the
Wind erosion there
0.05-5
ground
lowest
on wind
distances.
to
most
of
carried
of particles
the
increases
speed
The amplitude
exposed
speed
varies
are
particles
increases
wind
of
the
zero,
logarithm
wind
considerable
The larger
wind
of
particles
move over
of
the
depends
speed is
wind
the
The effect
The smallest
over
of
estimated
15 km/h.
that
wind
and thereafter
as a function
particles
components, degradation
effect
on the
and fertile and a reduction
soil: components in water
in
particular,
retention
which capacity;
- 12 -
-
by moving the coarser components which build form dunes which can cover and make sterile .. '.'ind
erosion
also
effects
vegetation
Excessive
itself.
humidity
Excessive
humidity
in
the
soil
Water is an essential component have disadvantages due to: reduction rihich
of chemical
prevents
the
reduction
-
its action and which
-
the difficulty
-
reduction
in crop
Excessive
humidity
Excess
leads
for
to degradation
soil
and plant
and bio-chemical
oxidation
-
4.2.
of soil
and certain temperature
of
yield
micro-organism as a result
may range
salts
gradually
build
tions
harmful
to crops.
may occur,
penetrate promoted
!rnsuitable
up in
flow
is not
where the
agriculture soil
in passing
they
soil
sufficient will
to leach
not
be harmful
due to vaporisation
There
to degradation
crop
loss.
the
up of toxic quantity of
soil,
to plant
until
they
i.e. life,
reach
take thess
concentra-
of soil
structure
and reduced soil
permeability.
and by suitable
draining
practices and failure
of its
plant measures
since
labour-intensive
tion,
leads
agricultural
Intensive
1
to total
may lead to the build brings with it a certain
phenomena can be controlled by leaching the water with a high dissolved-salt content.
of
evaporation;
by drainage.
These to evactiate
the
surface
deeply into the soil by the high humidity;
fall
and this
only
deficiency
life;
components
exhaust
oxygen
the phenomenon of alkalinisato salt concentration (Salinisation), calcium ions are repalced by sodium ions in the absorbant soil i.e.
In addition
4.3.
from
quantities
salts
If the water mineral salts. the salts down to lower levels
tion
excessive
of excessive
from a slight
and semi-arid climates, irrigation Each new irrigation flow the soil.
in
fertility.
wet soil;
can be controlled
toxic
but
resulting
on plant roots which can no longer often suffer from parasitic disease of cultivating
and reduced
life
action
In arid salts
and
OTHER FORMS OF SOIL DEGRADATION
A.4.
-
obstacles
Windborne sand particles have effect on grass and crops. The wind increases vaporisation and tends the soil's usable water content more rapidly.
an abrasive ~6 ext;aust
4.1.
up behind various entire regions.
nutrients. for
to apply This
remedying
this
adequate amounts of fertilisers is noted form of soil degradation' do not
come within
the framework
work.
are other
forms
of degradation
such
as sedimentation
or soil
acidifica-
..
13 -
Socio-economic degradation
-1,o.
aspects
of soil
The main effect of soil degradation The harm to agricultural
that result. returning the
land
to its
fertile
is the damage to agricultural activities land may be irreversible, or the cost of
state
may be so high
as to be not
economically
viable. The farmer's expenses
must be sufficient
such as iertilisers,
invest
poor
profits
in soil
seeds,
conservation
This
situation
soils
than
to allow him to live and pay other They must also be sufficient to etc.
fuel,
and improvement.
is of course
more difficult
on largehoidings
with
the As erosion progresses, and less profitable and finishes the deleterious effects finally
to achieve
in smallholdings
with
good soils.
farmer's
work becomes more difficult, more expensive At the regional level, by becoming impossible. undermined the total structure of social and economic.,
life. In order to avoid encourege conservation in work of value
such situations measures which
it becomes necessary, wherever possible, to bring together the largest number Of farmers
to the collectivity.
A.5.
LAND USE
Land employment
5.1.
Depending categories:
on its production
and protection
land
is used for
Protection
land
usually
role
in
the
The balance country's
level
economic
than
land
Production
ma:or
land
characteristics,
between
of
production
of development
classified
the
forest
cr pasture
cultivated
land
and protection
and may change
land
depending
that will
vegetation is
and plays
situated vary
on technical,
a
downhill.
depending social
on the and
conditions.
Although production
protection it land,
land is of less signficance from has a decisive role in maintaining
the economic point of view the country's biological
Land classification
5.2.1.
two large
land.
balance. 5.2.
into
cultivation.
has natural
conservation
is normally
Classification system developed by the Soil Conservation Service of the US Department of Agriculture The classification
is divided
-
capability
units;
-
capability
subclasses;
-
capability
classes;
see fig,
into:
A.3,
crop
coefficient
values.
-
units
The capabilit:r prdouction
and respond
in
group
soils
about
ttle
14
that
-
have
about
same way tc
the
the
same influence
management
on crop
requirements
of
common crops. The subcla; wetness
hazard,
eq 1.group capability and climatic
The capability of
risk
classes
to erosion
having
similar
limitations
(erosion
limitations). describe
and limitations
The simplified
units
progressively,
in
eight
stages,
the
degree
of use.
classification
is
as follows:
Simplified
classification -
Unit
Subclass
Class Land
I
suitable
Land with
1
for annual
cultivation cultivation
I
Land that can be permaulently is treated normally rotated, These are lowlands for which not necessary.
II
Less fertile land with lower yield, often on a slight has already taken place by slope i3 %), where erosion Moderate conreducing the depth of the arable land, servation practices necessary. Land with
intermittent
cultivated and which, when with fertiliser or lime. conservation practices are
cultivation
III
The soil has to be reconstituted a vegetation covering to occur, place only from time to time. land with slopes of IO-16 %.
periodically by allowing and cultivation takes This is the case of eroded
IV
Land where the slope is steeper Is suitable seriously eroded. limited cultivation.
than only
Land
II
requiring
permanent
in class III for occasional
cover
V
Land not suitable for Suitable to erosion. careful exploitation.
VI
Land of the above type but which has poor erosion resistance due to physical properties or topography. can be used for pasture with conservation techniques required from time to time.
VII
III VIII
Exhausted stituted pract:ces.
and more or
ploughing but for permanent
relatively pasture.
resistant Requires
It
Pronounced erosion that can be reconland. by grassing or planting with total conservation
Non-produc.tive
land
Soils tion,
VIII etc.
of class forests,
are suitable Shouid not
only for be cleared.
natural
vegeta-
Fig.
A.5 -
!. ! I! -A-
r.
,‘> _ i :
Land classification to run-pff erosion in tl,e LISA)
Ilt".:~ _.
(J~l.ilI :; .
on the basis of susceptibility (based on a drawing published
ii L!v a III: e d stage
,b_
. . ..r.
--
of
erosion
(Upper
Volta)
Examples
of
advanced
stage
of
erosion
Niger
Upper
Upper
‘~01 ta
Volta
- 17 -
Other
5.2.2.
classification
5.2.2.1.
Classification
by degree
5.2.2.2.
Classification
of
see fig.
is
the
Diagramatic of run-off
A.7:
Apparent erosion
or
Stage I. stability
of
II. Stage of insidious erosion
III. Stage of initial apparent erosion
by s lope
of
in
erosion tropical
(ref.
ll),
Africa
BEEK and BENNEMA :FAO 1972)
a new classification
into
run-off
of
see fig.
(ref.
A.7.
l),
A.8.
developing
Current potential state
land
The classification
5.2.2.3.
Fig.
systems _-
system
countries.
It
technical
effects
incorporates
capability
classification erosion
designed
(ref.
28).
more specifically social
This
for
and economic
factors
classification.
of degrees
of
Soil
characteristics
Types
of
remedy
Insignificant, clear run-off water. No apparent erosion
Fiat or almost flat land or very slight slopes less than 3 % High permeability: 20 cm/hour (cf. 3.2.4, Ch. D) Dense cover of vegetation Good fertility Good soil cohesion Land well supplied with humus
All types of possible No treatments
Slight run-off of turbid water at very low speed during. heavy precipitations No apparent erosion or traces of rills
Slight uniform slopes of less than 3 %, or very intersected slopes Gf 5-8 % Good permeability: 12-15 cm/hour Light covering of vegetation Moderate fertility Relatively good soil cohesion Land with a relatively good humus content
All crops on contour lines Well planned rotation From time to time, bench terraces Reduced grazing density
Uniform slopes of 5-8 %, or intersected slopes of lo-16 % Small collection basins (1 or 2 hectares) Moderate permeability: 8-10 cm/hour Very sligilt cover of vegetation Moderate fertility Poorly coherent soils Land with only slight humus content
Alternating crops on contour lines with % in annual cover crops Bench terraces often necessary Reduced grazing density
Run-off already quite pronounced with moderate precipitation; muddy water flowing at moderate speed Appearance of light patches and stones on surface Shallow gullies appear especially after the soil has been broken UP, but do not hinder machines
Slight fertility
reduction
in
crop
,
- 18 -
Fig.
A.7
Current potential state
(cpncl.) Apparent erosion
or
IV. Stage of intense erosion
Stage V. dangerous erosion
of
VI. Final stage of erosion
effects
of
Soil
characteristics
Types
of
remedy
Heavy run-off of muddy water with moderate and heavy precipitation, speed quite high to very high Increase in the number of patches and stones Deep gullies which begin to impair mechanical cultivation
Uniform slopes of lo16 % or intersected slopes of 20-30 % Watershed of several hectares Low permeability: 2-5 cm/hour No vegetation covering
Alternating permanent grass and cereal cultivation, for example cover crops must dominate in the rotation system Terracing essential Back-sloping terracing necessary on slopes over 15 % Ploughed crops are possible between terraces Low grazing density *
Pronounced run-off at the slightest rainfall Water carries gravel or aggregates moving at high speed in the event of heavy precipitation Deep gullies preventing the movement of heavy machines Land carried away in blocks
Uniform slopes of 2030 % or intersected slopes of 45-65 % Large watershed Very low permeability 0.5-l cm/hour No vegetation cover Mediocre fertility Unstable soils
"Algerian terraces" essential Cover cultivation everywhere, with permanent grass cover on large surfaces Pasture, woods very light grazing density with periodic prohibition
Top soil stripped
Very steep slopes Very large watersheds Virtually zero permeability No vegetation cover Fertility completely lost Unstanic. soJ~c'
Diversion channel above and below to protect cultivated areas Prohibition of grazing Trial tree-planting u:l back-sloping Lerraces
entirely away
Observations 1st
column:
A given area of land may go successively commencing with the stage of described,
through stability.
the
six
stages
2nd column:
There is a constant danger that the features may deteriorate, but they can regress if the treatment given in column 4 is suitably applied. it would be necessary to Where the proposed remedies prove inadequate, immediately apply the remedies of the next, more serious Stage.
3rd column:
This is merely in combination;
4th
there is listed a nubmer of treatments by order For each category, the choice should be made depending on the stage to of effectiveness; Obviously, general remedies (workwhich the erosion has progressed. Various etc.) should be applied at all stages. fertiliser, ing. the erosion In general, stages may coexist in a single plot of land. starts at the lowest part (watershed effect) and moves progressively upwards.
column:
a list of different features, it is not necessary however,
some of which must exist that all be present.
- 19 -
Fig.
A.8:
Classificaticn (in tropi Reference
Slope %
Various
3-12
Crops nating grass
of land Africa)
crops alterwith cover
on the
basis
of
slope
1 Possible methods
Land use
o-3
:dl
cultivation
Crops
to be avoided
Protective measures
Mechanlsed tion
cultiva-
-
Mechanised tion
cultiva-
Precautions to be taken for bush-type culture on bare soil
Absorption or diversion network Contour cultivatjon
12-25
Crops grassland woodland
Manual cultivation Animal-drawn machines
Bush-type crops on bare soil
Anti-erosion networks Terraces
25
Pasture forestland
Manual
All
Anti-erosion ditches
cultivation
- 21 -
CHAPTER B
EROSION
B.l.
PROTECTiON
CONSERVATION
TECrlNIQdES
OF PROTECTED
LAND
Forests .
Role of the conservation Depending
increasing
on the
open forests,
-
light
-
tropical
forest
The role
of
forest
the
formations
forest
the
the
organic
rich
flows,
increasing
ground-water
forests,
conservation
protects
the
mechanisms
is
against
water
soil
roots)
porosity
which
of the
protect
the
and permeability.
due to:
soil
impact
thus
structure;
soil
against
This
organic
run-off matter
is
substances. against
run-off,
their
regions, 1 level.
A forest
forests
duration
it
may help also
play
an important
and reducing
peak flows,
reserve
role which
in evening limit
out
the
to
reconstitute
to its
and a recreation
protect
influenc the
role
e on the
relative
since
they
region's
humidity
of
help
to lower
Plant
climate. the
in some
air;
precipitation.
addition
Land conservation necessary
have a corrective
to increase
increases in
Finally, logical
forests
may have a significant
transpiration
drained
of
effects.
In marshy
1
may be made by order
and disaggregation
(leaves,
structure,
action
soil
effect
matter
in nutrient
pernicious
in wt.ich
splash
In their
regions
a distinction
formations.
the forest
and improve
water
zone,
or deciduous
vegetation
reducing
(b)
climatic
cover:
-
(a)
forest in so mechanisms
is this
protective area
role,
for
on continuous
cover
against
During the nineteenth by a vast programme
it
where
it
has a role
as a bio-
man.
based
or supplement
a forest
the is
vegetation attack
non-existent
cover.
It
of man and animals
is
therefore
or to
or inadequate.
the Lande region of Gascony in France century, of reafforestaticn using maritime pines.
was
the
-
The main are
not
that
objective
22
of afforestation
incompatible
but
the
side
-
may be production
of
afforestation
The two
or protection.
dealt
with
in
this
publication
is
of protection. Main forest afforestation
1.1.2.
Choice
1.1.2.1. These should
species
are
used
of species
selected
on the
be made to give
basis
preference
The varieties
requirements.
in
of
to
used
the
over-all
types
for
of
soil
However,
objectives.
trees
that
conservation
attempts
can also
meet production
may have
the
following
objectives. -
conservation
-
reccvery
-
improvement
-
stabilisation
of of
soil
land
selected
be suitable
-
offer
of the
The choice objective
of
of
the
coastal
soil:
sand,
continental
sand,
the
operation; conditions:
difficulties.
Review
used
of moving
environmental
no cultivation
1.1.2.2.
degradation;
should:
objectives for
erosion;
ground;
and protection
The variety
-
run-off
has undergone
of marshy etc.
meet the
soil
that
windscreen,
-
against
in
of the main afforestation
species
tree
varieties (ref. 13)
to be used
afforestation
depends
programme
on the
which
climatic
conditions
may be either
timber
and the
production
main
or
conservation. The selected
soil
condition
or
intended
for
are
suited
well
testing
The main
humidity
the
level
in
certain
the
and,
susceptibilities
planting
should
shrubs.
rilthough it
provides
rnc roachmen
be given
new varities
depending Wherever
to
local
prove
on the
a project
is
varities
which
necessary,
prior
out.
varieties
that
playing
has a patchy
zone.
should
preference
situation
be carried
have
can be used
a predominant
are
categorised
grass
forestry construction
cover
and there
production materials
below
on the
basis
of
the
role.
Steppe regions with rainfall between 200 and 500 mm(Sahelien and subdesert
This since
may also
conservation, to
factors (a)
the
soil
should
climatic
varieties
is
zone) are
only it
small,
relatively is
and firewood
few bushes
of vital
economic
and helps
in
and
importance
controlling
desert
t .
Plantation
techi.iques
counter
the
competition
carried
out
to concentrate
should for
water
be designed from
and to ensure
natural
to exploit
natural
vegetation.
infiltration
of water.
conditions
Earthworks
and should
be
- 23 -
The main varieties -
Acacias
used are:
(mimosoideae)
Numerous varieties
are widely
encountered
in dry
and very
dry
zones
They comprise numerous subspecies and varieties and Australia. have very specific ecological requirements and are well adapted conditions
which
they
in Africa
which often to the severe
encounter.
They include: -
Acacia
laeta:
sandy -
this
and rocky
Acacia
has very
soils
albida:
or to clay
this
is
resistance
good
a tree
to drought,
is
suitable
for
subsoils. without
spines,
the
trunk
of which
may
grow up to 1 m in diameter in good soil. It provides firewood and may be fed to animals. forage seeds, and the fruit This variety is par-. titularly useful for soil conservation in view of its deep rcots and the micro-climate vicinity -
-
provided
Acacia dunes;
cyanophylla: this variety it is used together with
Acacia
raddiana:
this
from Mauritania tion -
by the vegetation
of the driest
Acacia
it
produces
in the
is
a large
acacia It
is
found
in
a variety
the most arid
used
for
is
a small It
spiny
tree
which
is a good variety of arid zones.
grows
the
regions
reafforesta-
in very
dry regions
it
on sandy,
which
Prosopis juiiflora (mimosaceae): this is a small spiny is used by cartwrights and for the production of posts. planted
stabilising
of regions. this
Senegal:
firewood; -
that
is used in particular for tamarisk for wind breaks.
to the Sudan.
soils and on clay subsoils. results in the reafforestation -
cover
of crops.
gives
stoney
excellent
tree;
the wood It is an excellent stabiliser for sand.
is an excellent
Genus euphorbia Euphorbia balsamifera: this is a shrub of 2-5 m in size from the very dry regions of the south Sahara. It propogates easily and is widely used for stabilising sands in arid regions. (b)
Dry-climate
Sainfall
is between
The grass again
the
Savannah
cover
limiting
500 and 1,000
is more dense factor.
than
The species
mm with
7 to 8 months
in the preceding selected
must
of dry
case but be suitable
season.
water for
is once these
conditions. ---_1 The main ap~~:les -
Azidarachia areas
,ndica
of India
used are: in the dry this is a tree which is widespread It provides ve1.y Sudano-Sahe lian climate zones.
(meliaceae):
and in the
- 24 -
it
good firewood, source
requires it
of water;
is
deep topsoil
a light, poorly
suited
with
a relatively
impermeable
to clay,
close
soils
subject
to
flooding. -
Anacardium -
occidentale
Dalbergia
sissoo it
tree; adapted
to
since
is
it
is
poles
and for
Acacia
variety
Euphorba
-
Acacia
-
Terminalia
-
Acacia
albida.
-
Acacia
Senegal.
-
Prosopis
a moderate-size,
and for
soils
but
and vigorously
is
for
used
in
out
the
is
must be well
throws
used
It
firewood.
they
It
soils.
misshapen and
control
new shoots
It
of windbreaks.
drained
erosion
production
well
and suckers.
of
firewood,
can be planted
only
soil. is
grows
well
widespread in
does well a shrub
turicali:
in
heavy
soils
on a dry used
for
Senegal
and in
which
the
Sudan. to
subject
are
The
flooding;
the
ground.
hedges
1 i nes.
and in
mearnsii. tomentosa.
juliflora.
Semi-humid
The rainfall
-
to clay
construction
this
variety
-
(c)
the
healthy
sdstringens
and poor
suited
is
and stakes
(caesalphinicaea):
scorpioides,
pubescens
poles
deep rooting
siamea
rich,
for
stoney
not
Cassia in
-
used
sandy,
it
deep:
-
is
this
(papilionaceae):
tropical is
between
The principal
species
Teak (tectona
grandis):
supply
Savannah
and should
1,000 used
and 1,300
3 to 6 consecutive
dry
months.
are:
this
be well
mm with
requires
deep,
fertile
is
an excellert
It
drained.
soil
with
an adequate
wood for
water
shipbuilding
and cabinetmaking. -
Gmelina
this
arborea:
reafforestation and the
young
Propagation needs
for
deep
are
which
curtains,
very
hardy
The wood is
easy.
alluvial
a species
protective
plants is
is
soil
and is
is
suited
lines
of
and cattle used
for
will general
susceptible
to
i ndividual etc.
trees not
The tree
graze
on them. The tree
joinery.
to asphyxia
from
stagnant
water. -
Cassia
siamea.
Genus eucalyptus: numerous tests .-. +:o semi-humid tropical climates. suitable
formed.
for
forests
prOteCtiVf?
?'hey provide
clsed to build
lines
excellent of
trees
have
been
Numerous since
they
general and shelters.
carried
out
on their
adaptability
species
are
available.
They
grow purpose
rapidly,
are
robust
wood and firewood
The species
used
are
and well and can be
include:
- 25 -
tereticornis
Eucalyptus
with
the
exception
Eucalyptus
micro-corys
Eucalyptus
robusta It
is
urophylla,
E:-lcalyptus
camaldulensis.
Eucalyptus
deglupta.
are
suitable
for
calcarota.
-
Callitris
glauca.
-
Chlorophora
Casuarinil
loams,
soils.
and healthy
soils.
salty
coastal
marshland
of waterlogged
on heavy
ground.
work. etc.,
of
groundwater
is
this
used
numerous
The wood is also
is
tree
but
is
which
is
and
and the
used for
a source
a remarkable It
as a windbreak.
low-altitude
level
a iarge
conditions
of
resin.
suitable
joinery.
(filao): sandy,
varied are
soils. and it
this
also
in very
The species
and light
(iroko):
and is
grow
land.
does not
It
tolerate
tree is
for
widely
requires
stagnant
dune used
for
a relatively surface
water.
Bamboos -
Gxyienanthera for
-
and in
also
used
Cd’, Tropical In view
of
those
these
in pulp
which
climates,
large
has good
resistance
soils;
it
does not
like
clayey,
number
of
species
the for
that
can be grown,
on a large
scale
Cmelina
arborea:
PlanWd
on a large
scale
Planted
on a large
scale
Acrocarpus Cassia
fraxinifalius
siamea
suitable
and paper-
and salty
soils;
it
it
is
possible
to
qualitative and quantitative point of view. soil conservation is not usually a requirement.
Planted
falcata
is
pulp
Savannah
grandis:
Albizia
for
and papermaking.
are best from afforestation
adorata:
used
compact
Tectona Cedrella
to drought, is
maintenance. this
and humid the
this
and ferruginous
land
Bambusa vulgaris: is
select
abyssinica
superficial
dry,
making
In
genus
and external
reafforestation higher
this
woodwork,
equiselifolia
stabilisation
less
reafforestation
mediocre
excelsa
cabinetmaking
moist
and sandy
good soil.
the
in
purpose
Callitris
SOilS
and superficial
on loamy,
afforestation
-
for
and dry
alluvial
etc.
species
for
and general
rich
in more or
for
Eucalyptus
lumber
-
grows
salyna.
majority
soils
requires
Eucalyptus
a good choice
-
acid
useful
the
relatively
preferentially
grandis,
Genus pinaceae: are
of
Euchlyptus
soils.
-
for
- 26 -
Araucaria
In mountain
eunninghamii:
Chlorophora
excelsa
Chlorophora
regia
Eucalyptus
camaldulensis
Chlorophora
rostrata
Eucalyptus
tereticornis
Eucalyptus
umbellata
Eucalyptus
citriodora
Eucalyptus
cloeziana
Eucalyptus
deglupta
Eucalyptus
saligna:
More difficult and soil
Eucalyptus
grandi.s:
Very similar same species
Eucalyptus
pilularis:
Planted
on a large
scale
Eucalyptus
propinqua:
Planted
on a large
scale
Eucalyptus
paniculata:
Planted
on a large
scale
Pinus
merkusii
Pinus
kesiya
Pinus
elliottii:
Pinus
insularis
Pinus
taeda
Pinus
caribaea
var.
Pinus
caribaea
bahamensis
Pinus
oocarpa:
of
preceding
view
tree,
in madagascar
of if
rainfall
not
the
at medium
At low altitudes At medium altitudes altitudes
Pinus
aptula:
At high
altitudes
Temperate
specific
point
caribaea
At high
is
the
the
successful
pseudostrobus:
There
climates
a large
(Europe)
number
of
species
used
and these
should
sycamore,
bean
be matched
to the
objectives.
They
include
tall
trees
nettle
the
following:
(horse
tree,
elm,
intermediate -
chestnut, plane,
or filler
oak, poplar,
trees
deciduous
(service
hornbeam,
maple,
mollntain
-
to
Pinus
(e)
-
from
Has proved altitude
Pinus oocarpa, var. ochoterranaF:
-
climates
tree, beech,
maple, lime
for
tree.
ash,
wild
tree);
cooses;
judas
tree,
walnut,
elm,
alder,
birch,
horse
chestnut,
false
acacia,
plum,
Willow,
laurel,
etc.);
ash);
-
evergreen
shrubs
for
filling
(arbutus, out
holm-oak, the
lower
holly parts
of windbreaks
and wooded
strips:
cherry.
- 27 -
-
-
deciduous
(hawthorn,
tamarisk,
blackthorn,
evergreens
conifers
for
(laurel,
and thuya
for
evergreen
wi_ndbreaks
Japanese
cedar,
SeqUOia,
-
Lambert
cypress,
pines.
Preparing
dogwood,
syringa,
elder,
thorn,
cotoneaster,
privet,
purslane);
larch
a reafforestation
objectives
of
when choosing
on poor for
soils;
windbreaks
on the
sea coast;
plan
the
plan
"ne species
have most
been
established,
suitable
are
rainfall
is
the
related
main
to
factors
the
to
climate
and
soil. As far
as
annual
number
choice
of
rain
species
dates
(superficial
of
study
is
year
soil,
a predominant
a sufficient
is
also
and also
guide
necessary the
factor.
in
The
determining
the
to make allowance
regularity
of
for
rainfall,
so as to
hazards,
may be necessary
to concentrate
can also
be used
rainwater
to
limit
run-off
vaporisation
mulch).
survey
not
It
techniques
the
as a physical
not
relevant
Suitable
of
possible,
the
soil
auger
is
concerned
samples
and where
should
be taken
a complete
to
determine
any
factors. The potential
rooting soil,
the
measures
working
limiting
is
rain
and the
zone,
points.
pedological
the
of
throughout
In an arid
As far
concerned,
to be propagated.
planting
to certain
is
climate
of millimetres
distribution
specify
for
may be the a high
level
The presence of water
and thus
Certain
root
development
proximity
of
of ground
water.
of
an upper
reduces
species
will
can be used
as pines,
is
a rocky
layer
substrata,
only
to recolonise
of
(e.g.
vaporisation grow
an essential
is in
compacted
sand)
which
a limiting
layers
of
of
Obstacles clay,
limits
factor
a deep layer
thin
factor.
topsoil
layers
capillary
in
light
dense
to
arid
movement
climates. other,
topsoil; where
of
the
such
underlying
rock
fissured. The soil
nature
of
the
preparation
method a will
arable
portion.
The chemical of
rose,
hedgerows:
-
consider
guelder
rose);
thyme,
cypress
Once the
is
bush
-
3 -1.3.
the
bladder-senna,
species
chemical
often
(presence requirements
be a valuable
soil
content of is guide
of
the
soil
also
will
calcium,
acidity,
often
inadequate,
to selection.
vary
also
depending
on the
thickness
be a determining
salinity). and the
Knowledge results
of
and
factor
in
of
species'
local
the
the
experiments
choice may
- 28 -
Ground
1.1.4.
preparation Methods
1.1.4.1. These vary
considerably
the species twography, economic conditions. In certain of
proper
The main clearance,
-
preparation
-
staking-out,
-
preparation
-
measures
-
erosion
with
introduction
is
of
service
of
planting
can also
1.1.4.2.
local
is
(terraces,
socio-
a prerequisite
embankments,
contour
out
by hand
are:
holes, run-off
water,
to use manual
deep ploughing be stripped
the type planting;
-
labour
-
the ground l's not wet ground).
for
vegetation plentiful
this
labour;
which
it
is
by mechanical
stripping
are used,
-
On grass-covered
measures
vegetation,
B.2.
can be carried
possibie
methods
is
anti-erosion
section
existing
to be used and the
is
techniques
under
the
soil,
paths,
Vegetation methods
rf
of
work.
always or
of
to accumulate
control
subsoiling
Manual
that
designed
not
Vegetation
be described
type
how it
Anti-erosion
operations
-
It
the
reafforestation. will
on the
to be planted,
cases,
etc.)
ditches,
and depend
is
necessary
for
example
the
to use powerful
means or even by the
case
machines.
use of chemicals.
by manual
in
particular,
cover
requires
when: only
slight
modification
stripping
(very
prior
to
and cheap; suitable
sites,
for
soil
meachnical
preparation
in
certain
slopes,
cases,
very
be unnecessary.
In other -
cases, the vegetation may be removed: --.------.---.--. -----.------in narrow strips 1.5 m wide along either here will be picks and hoes;
may,
steep
the
contour
or by removing vegetation in a radius of This will be done with picks and shovels. --._.-_. -- -._. -_..- ..-._ .-__-.._-.__--.---
50-70
On brush-covered
will
Forest-covered clearing forests.
operations
sites, sites are
soil do not
usually
preparation usually intended
present to replace
cm around
be highly a soil
The tools
lines. the
labour
protection
ex?sting
forests
planting
used holes.
intensive. problem
and
by productive
- 29 -
Preparing absorption
1.1.4.3. These
methods
used
in
zones
order
increase the water allow the roots to (60 x 60 x 60 cm).
storage capacity of take, deep ploughing
the or
With
of
holes,
rainwater
the
technique (see
and Other
direct
water
planting
to:
on pre-existing soil the
vegetation;
by undercutting the use of large planting
these
techniques
soil to holes
are
not
intensive. Another
earth
digging
of
in
-
exception
action
water
eliminate
the
destructive
arid
improve
-
labour
the
are
the ground to and retention
it planting
called
Appendix,
collects
Standard
around
ridges
laid
towards
large
the
the
out
in
planting
"steppe"
method
Plan
1).
planting
No.
used
The water
on sloping is
land
retained
fashion or
collector
are
used gullies
to
collect can
collect
by a ridge
(‘ r I k-3 tl’J>ays along .vatt’r in t~he terraces;
be built
the
1::.zI!it kin 3n npiSroxirilatcly c <.ri : 3 c:I‘ i rr‘cCulari+ i ie- .J. >
in
on the
the
location
basis
of
of
collector
drains,
paths,
are
touched
they
etc.
mind:
crests ilonstant
or
ridges
so that
they
spacing
between
a crop
not strip
by
by q’corrccting”
the
- 59 -
Fig.
Terrace
B.lO:
lengths
Direction United
and horizontal
slOpeS
(ref.
1) )
of flow:
States
I
0,O.s % 122 m
, '
'
0 122m
,I
heavy rainfall areas Commonly adopted lengths: 0.16 % , 0.25 % , 0.33 % total 400 ’ 122 m ! I 122m 122 m on very good absorbant soils 0.08 % I, 0.16 % 1, 0.25 % I total 488
’
0
,
for low-rainfall climates 0.08 % , 0.16 %
152m
’
152m
’
total
I
152m
This rule can be applied,
with precautiun,
m
m
456
m
in TROPICALAFRICA
Zaire Heavy soils and rainfall 0.00 % , 0.17 % , 0.33 % , 0.5 % I I I 180 270 360
0.04 %
,I 90
0.08 %
, 0.33 % ,I 0.16 % ,I 0.25 % I 1 120 Permeabl~4~oila, low-inT ensity raiz EL 0,ll , 0.33 % , 0.16 % , 0.25 % i I I I 120 240 360 480
0 0
-1 480
formula
1
formula
2
formula
3
, 0.08 % , 0.16 % I I 150 300 450
@
0.33 % is an optimum WESTAFRICA (frcn L:
Fournier)
490-550
UPPERVOLTA: L:
200
Virtually
ALGERIA:
m, slopes: m,
slope:
0.01-0.02-0.3
uniform
%
0.2 % (ditches)
uniform slope 0.5 % and 0.3 %, dry zone
Longitudinal slope 0.5 %, length 400 m TUNISIA: MADAGASCAR: Contour channels and terraces 0.5 % - advisable: Fig.
B.11:
Terrace
Determination as a function
length
for Nichols' of slope standards of ground slope and the length
Sandy ground Maximum slope per thousand a ground slope of:
for
0.2-0.3
%
terraces of the terrace
Clayey ground Maximum slope per thousand a ground slope of:
5%
10 %
15 %
5%
10 %
15 %
m
0
0
0
0
0
0
m
0.2
0.4
0.6
0.8
1.0
1.2
120-210
m
0.6
1.0
1.2
1.6
2.0
2.2
210-300
m
1.0
1.4
2.0
2.4
2.8
3.2
300-390
m
1.2
2.0
2.6
3.2
3.8
4.0
390480
m
1.6
2.4
3.2
4.0
-
0- 30 30-120
for
- 60 -
Bench
2.4.
terraces1
Bench
This
forms. which off
terraces process
was too
for
wate,,
of
saturation
of
There
are
a series
to recover
of
for
They will
flat
or
nearly
cuitivation
reduce
flat
land
or completely
plat-
on slopes eliminate
run-
infiltration. requires
upper
soil
two main
homogeneous, layer
of
deep
relatively
layers
types
terraces
constructed:
into
possible
an impermeable
the
land
utilisation.
construction
The presence
sloping
makes it
steep
and promote Their
convert
near
and cause
at
land
the
a single
permeable
surface
slips
depending
terrace,
constructed
and sufficiently is
which
on the
likely
soils.
to cause
may be catastrophic.
way in
go and terraces
which
they
are
constructive
pro-
gressivcly. 2.4.1.
Terraces
constructed
at
solution
usually
entails
retaining
walls.
It
soil
proved
This have
is
used
a single
go
massive
only
ineffective.
earthworks
when other
Terraces
and the
procedures
of
this
construction
for
type
are
of
enhancing
and conserving
justifiable
only
on good
soil. The main
types
-
earthwork lip;
-
terraces
-
stepped
terraces
-
irrigation channel
at
-
of
terraces with
terraces termites
terraces
are
(see
Standard
in which
the
bank
is
grassed
dry
stcnework
on slopes
Stepped slight
stakes
less
terraces
the
top
by a small
earth
than with
which
and wattle,
depends
are
on the
exceptional
channel
at
the
top
inadvisable
Terrace
slope.
cases,
in
1.50
countries
height
They
m.
snd a drainage
are
where
is
usually
usually
20 %. dry-stone
walls
and grassed-banked
terraces
will
resist
run-off. In ileavy
sequently at
of
at
12):
walls;
terraces which have an irrigation the base with a slight back slope;
The _width of a bench terrace equal to or less than 1 m and, in built
protected
No.
banks;
with
made with abound.
Plan
the
slope
the base
of
draining Fig.
volume
B.12
rainfall
regions,
terraces
are
the
next
the
water
shows
of earthwork 1
the
built
higher
run-off
with
a slight
to a collector
required
relation
Bench terraces have been used in the Far East and South America. areas of high population where there
the
slope
with
terrace
Con-
construction. a drainage
may itself
channel have
a slight
drain.
cross-section in
back
The whole
terrace.
a typical
may degrade
of CLo the
a terrace natural
built
at
one go and the
the
Mediterranean, in mountainous land.
slope.
since ancient times around They are used, in particular, is a shortage of agricultural
- 61 -
Fig. ! ~----.--
Terrace
-- B-12: ..._.
____
built _..
.__
at ~. ..___~
one -~.-I-
go
(Burundi) .-
.__.
--~--
.-
.~
_. ----.-,
Construction at one
Terraces
of a terrace go (Lesothoj
at one go (Lesotho)
- 62 -
Terraces
Typical
in dry
cross-section
stones
(Gard,
of a bench
France)
terrace
63 -
Fig.
8.13:
Guide 50 design with 1 m vertical
Slope of land Width of bench available for cultivation Total width of bench terrace No. of benches per 100 m of slope Maximum depth of cut Area of benches available for cultivation per ha Slope area of riser per ha of benches Volume of cut per ha of benches 2.4.2.
-Terraces
and construction interval
of bench
terraces
5
%
25
m
18.50
8.50
5.17
3.50
2.50
1.83
1.36
m
20.00
10.00
6.67
5.00
4.00
3.33
2.86
m
5 0.47
10 0.45
15 0.42
20 0.40
25 0.37
96
0.925
30
3s
0.35
0.32
0.850
0.775
0.700
0.625
0.550
0,475
m2
919
1 838
2 758
3 667
4 596
5 515
6 434
m3
1 175
1 135
1 077
1 02c
963
903
847'
constructed
progressively
These are constructed in the same soil snd climatic conditions as those desprrvic,usly but since tneir progressive construct!on makes use of agricultural they are much less labour intensive and, consequently, the costs are techniques.
cribed
lower. Construction
is carried
by placing obstacles future riser.
out: horizontally
or on a slight
slope
at the point
of a
In the farming that is carried out on the strips marked out in this way, soil is progressively moved from uphill to downhill by continuous downhill ploughing or pickaxing. The land accumulates behind these obstacles and progressively increases in heig;It to form a terrace with a slope which is sU?ficiently slight not to erode. Terraces obtained in this way are not usually horizontal but have slight downhill slope. Two types filters (a)
of natural and complete
Filters. part of the too severe vegetation The filters
obstacles solid
These break
can be used:
obstacles.
the erosive
soil carried in it. and can be controlled cover, etc.).
force of the running water and hold back a. They are effective when the erosion Is not by farming
techniques
(ridge
may be mads of:
-
piles
of stones
-
contour
-
lines
-
contour
-
rows of fruit
or crop
bunds protected of dense rigid
residues; by stabilising
grass;
hedges; trees
or vines.
plants
(ados);
cropping,
dense
- 64 -
(b)
Complete
solid
stabilising in
the
plants
and which
are
result
earth
Drainage
2.5.
progressively
either
or banks
bunds
or
initially
converted
into
of
ridges,
earth
such
on which
as those
to constitute horizontal
trees
described
defence
bench
or
networks
terraces
as a
to prevent
rill
slippage.
works of control
The construction gully
are
intended
paragraph,
Characteristics the role of
2.5.1.
are planted,
preceding of
These
obstacles.
gully erosion works
of waterways
and
for
rain
run-off
is
intended
and
erosion. As the
watershed
and deepen (from
as the
0.20-2.00
flow
and water
m in
Channels cross-section
this,
natural
of
speed
develop
the
water
vegetation
run-off
and then
depth),
and gullies
the
the
increases,
collects
gullies
(with
into
establishes
rills
a depth
erosion and the
anastomise
they
form
greater
which
an equilibrium
itself
which
Subsequently
increase.
by regressive
course
into
than
tends
channels 2 m).
to stabilise
cross-section;
after
cross-sectional
state
is
retained.
Regressive Regressive result
in
erosion
all
the
cross-section necessary
soil
is
Even when the modified. in start
the
likely flow
rate
to develop
concentrating
water
installation
of
not
to failure.
destined Effort
general
plan
construction
if
the
methods.
this
of
in
these
drainage
may finally
away before
the
this
form
cultivation
of
surface
soil,
reached,
the of
of pasture
erosion;
at
it
is
erosion.
conditions
cropping
equilibrium
this
erosion
the
watershed
result
in
the
water
point
is are
an increase courses
cross-section. channels natural
natural
networks
channel
the the
a watershed
has been
and the
diversion
flow
diversion
to control for
again
a new equilibrium
Consequently
erosion.
of
forests
and renewal
of
stripped
cross-section
to start
in
to conserve
progression
of
downhill
being
order
equilibrium
The construction of
In
Destruction
run-off
moving
of a watershed
reached.
to prevent
nevertheless
gradually
erosion
waterways
if
run-off
must
one wishes
erosion over
terraces)
and this
waterways
and gully of
(ditches,
be arranged
to ensure
require the
results
whole
that
the
also
has the
in
renewed
prior these
to the efforts
development
watershed,
effect
using
are
of a suitable
- 65 -
The two basic (a)
run-off
(b)
the nature section).
data
flow
and shape
tion
of
the
run-off
Run-off
2.5.2.1.
for
the
development
beds
for
draining
In
the
of
peak run-off
case of
peak
C = the
run-off
catchment
basins
with
are:
water
(drainage
cross-
surface
The concentration
(see
a duration area
of
time
This
area
rational
less
method
than
200 ha,
given
by the
concentration
time
determinaequation:
C I A
in m3/s coefficient
for
slope.
this
a surface
can be made by the
flow
I = rainfall
average
plan
rates
rate
Q = the
A = the
a drainage
conditions
Q = 0.00275 where
of
rate;
Determining
2.5.2.
essential
is
fig.
equal
to the
,the basin
depends
given
B.15)
in
ha.
on the
by the
basin's
total
length
of
the
basin
and the
formula:
t
ITc
= 0.018($
o'77
I where
T
c
= the
concentration
L = the maximum water S = the
slope,
The rainfall determined duration return
Fig.
(or to
their
ratio
of
the
a period
larger
ouration
are
shown
Rainfall
Climate
patterns
of
for
figure in
Africa
Mean annual rainfall (mm)
equal
small
selects
500
108
Sudano-Sahelian
600-l
300
114
T = return
500-3 duration
000
the
time
be made between
rainfall
intensity
and a return intensity
Intensity-duration
200-l
COO
must
concentration
the
is return
of duration
values
in
relation
and Madagascar
Mediterranean
1 000-3
the
below.
of
T = 10 y
Madagascar
to
Rainfall B.14
length.
constructions,
Rain
Guinean-equatorial
to
A choice
constructions. in
fall
time
one usually
10 years
for
in
ratios.
period), to
in netres
difference
intensity/duration equal
minutes
distance
for
50 years
B.14:
flow
intensity
recurrence
duration
equal to
from
in
time
66-120 120
characteristics
30 min T=50y
Rain T=lOy
of
in mm/h 60 min T=50y
60 150
75
-
90 42
108
-
- 66 -
Peak run-off conservation completely
case
of
possible
where
Fig.
leaving
out
of consideration
any soil
the concentration time or reduce run-off have been instal!ed, run-off may be
for
Topography
it
is
is
formula
- Table
Forests: . flat, slope 0.5 % . undulating, slope 5-10 % . hills, slope lo-30 %
necessary
to use the with
and vegetation
greater
than
200 ha,
it
to use analytical Reference
out.
hydrology should
be
textbooks.
possible basins
area
has been carried
hydrology it
a surface
methodology.
survey
catchment
Rational
B.15:
with
rational
no hydrometric
In West Africa, suitable
basins
peak run-off,
to specialised
'made here
is
catchment
to use the
In determining methods
be determined
halted.
In the not
should
measures which may increase Where absorption networks
coefficients.
is
rates
ORSTOM de RODIER-ALJ?rRAY method
a surface
area
of up to 200 km2 (ref.
which
31).
of C values
Soil
texture
Very
sandy
Laamy clay
Compact
0.10 0.25 0.30
0.30 0.35 0.50
0.40 0.50 0.60
0.10 0.16 0.22
0.30 0.36 0.42
0.40 0.55 0.60
0.30 0.42 0.52
0.50 0.60 0.72
0.60 0.70 0.82
30 96 impermeable surface 0.40 0.50
50 96 impermeable
70 96 impermeable
0.55 0.60
0.65 0.80
loam
clay
Prairies: . flat . undulating . hills Cultivated: . flat . undulating . hills Urban zones: . flat . undulating
2.5.2.2.
Drainage
The simplest channel
way cross-sections
and most widely
cross-sections
is
the
used method
of
MANNING-STRICKLER
calculating formula
flows as follows:
in which: Q is
the
flow
rate
S the
cross-sectional
R the
hydraulic
where
in cubic area
metres of
the
radius
p = the perimeter
in m
per
second
drainage
way in m2
and drainage
- 67 -
i the
longitudinal
K is
the
These Fig.
slope
coefficient
values
are
K values
B.16:
of
for
the
shown in in
the
the
water
course
surface
figure
texture
of
the
drainage
way wall.
B.16.
MANNING-STRICKLER
formula K
Characteristics Very
smooth
Sand/cement mortar rendering, sheet metal without planks,
walls:
Smooth mortar Planks quarry
Smooth walls:
. . . . . . . . . . . . . . . . . . ..s...........
rendering
without tiles
very smooth; planed protruding welds . . . . . . . . . . .
careful joints, ordinary ..*.......*..............a.................
85
rendering, 80
Smooth concrete; concrete channels with numerous joints ................................................. Ordinary Irregular roughly
Rough walls: Very
rough
Very with
walls:
extremely
masonry;
regular
earthwork
earthwork, rough or old built masonry ..,.....,.....
irregular rock beds
Earthwork
in
condition;
70
concrete, old or ...................
60
rivers
regular
the
velocity
in
the
channel
of water
course
is
equal
to
the
rivers ..,...
with
Completely abandoned earthworks, torrents large blocks . . . . . . . . . . ..**...............*............. The water
75
.........
earthwork with grass; . . *..,.....e.......................
poor
100-90
pebble
beds
50 ..
40
carrying 20-15
ratio
of
the
flow
rate
to
cross-section:
For a given
type
MANNING-STRICKLER
formula on the
basis
-
the
flow
-
the
drainage-way
-
the slope to be given to cross-section are known. In erosion
water
velocity.
channels.
rate,
makes it of
cross-section
protection Figure
B.17
channel
the
gives
the
K value
the
flow
where
the
main parameter the
has been
determined)
the
to calculate:
a known drainage-way where
the
work,
(where
possible
permissible
rate flow
cross-section and slope rate
and slope; are
and drainage-way
to be controlled threshold
known;
velocities
is
the in
drainagethese
- 68 -
Fig.
Permissible
B.17:
Original
Fine,
surface
materials
non-colloidal
sand
Sandy, Loamy
3
Volcanic
velocities
in unlined
Water transporting colloidal alluvium
Water transporting coarse alluvium: sand, gravel, pebbles
0.45
0.75
0.45 0.60
colloidal
mud
0.60
0.90
0.60
alluvium
0.60
1.05
0.60
loam
0.75
1.05
0.67
0.75
1.05
0.60
0.75
1.50
1.12
1.12
1.50
0.90
1.12
1.50
1.50
1.12
1.50
1.50
1.20
1.65
1.50
1.20
1.80
1.95
1.50
1.65
1.95
1.80
1.80
1.50
very
colloidal
Alluvial
colloidal
Mixture
of colloidal gravel
clay
and pebbles; mud mud and pebbles
and non-colloidal
Pebbles
and stones
Schists
and volcanic
Table
of permissible
Types
of vegetation
crusts
muds or plates
velocities
in
grassed
channels
Permissible Clays
Bermuda
grass
Kentucky
blue
- Cynodon grass
Blue gramma grass gracilis Buchloe d?-tyloides
dactylon
- Poa pratensis
velocities
and loams
(m/s) Sandy
soils
Good vegetation
Moderate vegetation
Good vegetation
Moderate vegetation
2.40
1.59
1.50
0.99
1.65
1.11
1.20
0.81
1.65
1.11
1.20
0.81
1.65
1.11
1.20
0.81
0.75
0.51
0.45
0.45
- Boutelous
- Medicago The means of
sativa reducing
drainage
water
velocity
-
Reduce the surface smoothness the roughness of the walls of cover.
-
Reduce the hydraulic radius R by increasing this may be done using by preference, for channels which are large and shallow.
-
Reduce course.
the
m/s)
Clear water without debris
0.75
Mixture of loams non-colloidal
Alfalfa
(in
0.52
gravel
Coarse
channels
loam
ash
Compact,
drainage
colloidal
Muddy, colloidal Ordinary compact Fine
water
longitudinal
slope
are:
characteristic K. This may be done by increasing the water course, e.g. by means of a vegetation
by placing
the figure for the water perimeter; waterways of equal cross-section, weirs
transversely
along
the
water
-
- 69 -
types
Main
2.5.3.
These
are
a larger
may lead
which
of
the
to an increase soil
waterways
if
by giving
erosion
constructions
the
characteristics
resultant
These
are
watershed
to protect
roads,
They are
similar
th-m
do not
inter-
waterways.
This
erosion. advisable
to
make them suitable
One may increase
crop
into
the
protection
zones
against
a waterway.
Ilaths,
to the
natural
renewed is
which
improve for
these
carrying
permissible
water
or by installing
anti-
or retention
to protect
tiracks,
conservation
sections.
protection
desi,gned
into
it
bed a grass
at critical
and divert
it
undertaken,
erosion.
When soil
to make constructions
and cause
is
water-course
Diversion, trenches
2.5.3.2.
flow rate
natural the
run-off.
and concentrate
work
without
velocity
run-off
in
collect
may be necessary
conservation
their
away the water
naturally
it
undertaken, part
Before
the
waterways
waterways
are being
cept
constructi.on
Natural
2.5.3.1.
works
of
run-off
They
also
from
upper
include
reaches
ditches
of
designed
etc.
ditches,
tiers,
and terraces
St-own in
Standard
Plan
No. 9. 2.5.3.3. These the
water
are
Grassed
channels
usually
resectioned
velocity
does not
They are
slightly
-
the
bank
slope
-
the
total
-
the
channel
1s very is
waterways the
very
small
No.
which
i3)
have
been
grassed
to ensure
that
value.
a very
being
depending
Plan
threshold
and have slight,
varies
depth
Standard
exceed
convex
width
(cf.
flattened
trapezcidal
cross-section:
4/1-6/l;
on the
flow
and varies
rate; depending
on the
critical
velocity
and slope. Grassing natural
grassing
When the allowed is
the
bunds
requires
channel to grow.
American as shown
careful
is
not
sufficient.
is
very
large,
When the "flood-way" in
sowing
the
diagram
climatic
The grass
be carefully
a natural
transverse in
and favourable
which
must
vegetation slope
is
of
very
the bed width
conditions
shrubs
slight, is
when
supervised. and bushes
another
restricted
can be
system
used
by two parallel
below.
Parallel
bvnds Natural
"Flood-way"
land
- 70 -
2.6.
Bank, channel
and gully
prOteCtiOn
Bank cave-ins, meander formation and gullying may reduce the area of cropped Control Concave gully banks are undercut by water and gradually retreat. land. measures include the protection of the bank by natural vegetation or by various obstacles or by displacing the cutting power of the current towards the centre of The techniques employed vary considerably depending on the the water course. force of the water, the extent of the phenomenon and local resources. 2.6.1.
Stabilising
banks with
vegetation
The most simple approach is to allow natural fire and other it. against the ravages of cattle,
vegetation deleterious
t,o grow by protecting elements.
Protection can be provided by fencing off the zone on each side of the gully. If the banks are too steep, The fenced zone should be 3-8 m wider than the gully. slope - a minimum of l/l earth-moving work may be necessary to provide a shallower or better still l/2, on which vegetation can obtain a footing. The most resistant and least demanding plants are what are generally called "weeds". They help followed by shrubs and bushes.
These will appear the first. to prepare the soil and are
Where humus loss is high, the process of vegetation development promoted by covering the soil with branches, straw and leaves.
can be
When natural. vegetation does not. suffice to cover the banks with sufficiently dense growth, a planting programme may be called for, using trees, bushes, creepers, being given to local species. brambles, etc., with preference Grassing over thr bdnks may ensure good protection. However, this requires well prepared seed and a relatively fertile soil. A variety such as Bermuda grass (cynodon dactylon) which flourishes under difficult conditions and stabilises the soil well, Inay be used. Use may also be made of trees such as willows and poplars in wet soil, false acacias in dry soil and privet, xiid blackberry and plum, elder, poplars, acacias, etc. A number of grassing techniques may be used; seed broad-casting; sowing or plants of selected species in furrows on t,he upper slopes (‘i/2); turves, placed in holes. Where possible, use should be made of seeds or plants taken from close by. Precautions should be taken to protect recently sown area against water eroslon. Wire-link fencing of 1 x 3 cm mesh will catch floating debris and ensure protection in this way. 2.6.2.
t?-otection 2.6.2.1.
of banks by construction -_I_-
works
Summary protection
The methcds used vary considerably and depend mainly Examples are sncwn in Standard Plans Nos. 14, 15 and 16.
on local
resources.
-
These measures
may include,
and reeds
out
-
alia:
-
branches
-
anchoring
-
made up of tree trunks “jacks” or “parrots” base by stones and retained by a chain;
-
pallisades
stakes
laid
inter
71
intertwined
steel
by stakes;
wire; splayed
out,
anchored
at their
fillin
Protecting and wattling
staking '2 6.2.2.
with
banks and anchored
made from wood and wattling.
Pebble
L.
on the
Stonework
prctection
wi t I1 this technique, the bank is 1s iajd out at. random on the bank.
a low bank by with pebble filling
(Standard
Plan
reprofiled
No. 1’7)
to a slope
of 273 or
l/2
and stone
The mean Jiameter of the stones should be calculated to ensure that they (Izba formula 1. The stone facing may be cannot be aarried away by t6.e current s.ij-1 .‘i? m d3ep and should be at l-east 1 .5 times the mean diameter of the stones ::r:et! . iGn e n t ii e b An k has recently been filled or where the soil is crumbly, a iiiter layer of gravel should be placed between the bank and the stonework. This 15-20 cm thick. layer 5 l-i5 u 1.A b P ‘~~.-Concrete- ;.c
+t=L-, Einh
water
-, :
Level
Stonework
Filter
-*;Yank protection
by stonework
pf1
.. I@-7
- 72 -
the
a footing at low ater, l- 1.50 m deep and l-2
If the base of the bank is accessible stonework base in a trapezoidal trench
is installed at m wide at the base.
The advantage of the stonework is that it can be laid at random. It immedi-. ately combats any undermining which takes place at the base and thus ensures however, frequent refilling is required at least during the excellent protection; first year. 2.6.2.3.
Bank protection
Slope
with
fascines
protection
and stonework
with
fascines
Fascines are used to produce boxes which are then filled with rocks. The fasrines which are iaid out along the contour lines are held in place by stakes made of freshly cut wocd which start off the shrub growth on the bank (see Standard Plan No. 16). -Steel
wire Retaining
stakes
Pebbles Bed lined
with
interlaced
reeds
' Bank lining
2.6.2.4.
Bank protection
using
gabions
(see
Standard
Gabions are wire mesh packages filled with stone Chapter E). They provide excellent bank protection, mould to the shape of the bed as and when undercutting When the fill behind the gabions is protection by a screen of reeds, rushes,
Plan
No. 17)
and linked together in particular since occurs.
it is advisable crumbly, etc., or a gravel filter.
to provide
(see they
- 73 -.
Bank protection
2.6.2.5.
by masonry work
This type of protection is seldom used for crop land since it is much more In addition, it is much less flexible expensive than random stonework or gabions. than the latter and more liable to undercutting. Where the water carries pebbles of over 0.10 m in size, the masonry work should be made up of blocks approximately 0.60 m in depth and the joints should filled with bituminous material.
be
Bank protection by groins (see Standard Plans Nos. 18, 19)
2.6.2.6.
Groins are constructions, anchored to the bank, designed force of the water towards the centre of the water course.
to divert
the erosive
the height of the groin is restricted to the section of water in In gullies, which alluvial drift occurs. The top of the groin rises in steps to the anchoring The groin is directed downstream at an angle of 10-50,’ to thee point on the bank. direction of flow. The length of the groins should not be more than to ensure that the water flow is not hindered.
li3
or l/4
of the bed width
The Standard The groins may be made of a variety of materials. and 19 give some examples of the most commonly used types of groin. -
groins
-
stone rubble
-
gabion groins;
-
masonry work groins;
-
groins
made from logs or fascines;
with
groins; a concrete
superstructure.
The gabion groins are simple in design but nevertheless extremely In addition, their construction requires larger ‘quantities of unskilled 2.7. 2.7-l.
Plans Nos. lb These include:
Correcting
the slope of water
effective. labour.
courses
Role of constructions
These transverse constructions are intended to reduce the water energy regressive erosion. steeply sloping water courses and to control
in
The principle behind these constructions is to produce waterfalls by creating obstacles to the solid materials transported and to reduce the longitudinal slope between each fall and at the same time the water velocity. A distinction may be made between provisional constructions which are intended and permanent constructions. to allow the growth of stabilising vegetation, 2.7.2.
Type of work 2.7.2.1.
Stabilisation
by vegetation
The direct stabilisation of the longitudinal profile by means of VegetatiOn It can be carried is a system used in the US for small or medium-sized gullies. out as follows:
(a)
The shrubs are planted By shrub barriers planted across the flow line. there may be a row of stakes 30 cm close together in rows and, in addition, Tree barriers reduce the water flow velocity and allow loam to downstream. accumulate behind the dams.
(b)
By planting grass turves across the flow line This is an expensive head of small gullies. soil does not make direct grassing possible.
where erosion starts at the process which can be used when The flow rates must be low.
Small temporary dams (see Standard Plans Nos. 20 and 21)
2.7.2.2.
'These are intended the growth of vegetation
to reduce the water upstream.
retain
velocity,
fine
soil
and promote
These works should: --
have a height
-
should be spaced relatively close a minimum (virtually zero slope);
-
be anchored
-
be supplemented by overflow collectors water during the period of use.
--
of 30-45 cm;
at an adequate
depth
to each other
to reduce
.the water
speed to ,-
in the base and banks of the gully; of adequate
capacity
to evacuate
flood
A very wide variety of materials are used for the construction of these small steel wire, rubble. In temporary construction.?., the materials dams: earth, piles, need not be as resistant as in permanent constructions and the construction need Damage caused by heavy flows of water can he reoairsd cdsily not be so precise. at law ,,ost. The ma&n types
(a)
of small
temporary
dams are:
Darth dams
A simple low-height (30-45 cm) earth dam is built across the g1.Y::: to maintain A transverse overflow gully earth and moisture at the bottom of the water course. It should be grassed rover to is laid out laterally to evacuate flood water. provide protection against erosion. These are suitable for small flow rates. (b)
Branch weirs
Weirs made of branches small floK rates. gully
and they
are adequate
for
In the case of small gullies (2-3 m wide), straw is packed at the base of the and held in place by branches fixed LU the banks with piles. It
filled
are easy and cheap to build
is also possible to use a series with packed straw.
For larger
gullies,
the arrangement
of pi !es laid
out across
shown in Standard
the gully
Plan No.
21
and
can be
used. The water should flow over the cer.tr e of the weir which is kept lower than the sides to ensure that the water joes not 1'1:~ *round the outside and over the banks.
- -75 -
Transverse cross-section
Pile (cj
and straw
weir
Wire mesh weirs
Wire mesh may be used instead
of branches
to retain
the packed
straw
for
the
weir. (dj
Dry-s tone
weirs
These are used for small and medium gullies in adequate quantities. are available
on slight
slopes
anti when materials
life lcnger than that of the other These constructions usually have a service They are also more flexible and can be more readily constructions mentioned above. that may occur below the weir. adapted to ciiarges in the land by filling up hollows
Example The most soild wire
Where the mesh.
stones
are those
of a dry-stone
made from stone
are more irregular
slabs
or rounded,
weir placed they
edge to edge. may be held
Dry-s+one weirs are usually less than 60 cm in height, but, under In such cases it is essential circumstances, may be as high as 1.00 m. The downstream footing that the f:sti.ng downstream is well protected. equal to at least 1.5 times the fall of Irater.
in place
by
exceptional to ensure should be
76
The overflow be lo-20 cm below can be calculated This threshold.
lip should be located in the centre of the water course and should The width of the overflow lip the maximum height of the weir. for flow over a solid from the maximum flow rate using the formula rectangular or trapezoidal shape. lip may have a dished,
Witn rectangular overflow lip
(e)
_Cphion weirs
for dry-stone weirs when the stone available The?r can be a good substitute Gabion check dams have good resistance to water flow on site 1s of poor quality. and have the same flexibility as dry stonework. superstructure Footings of gabions can be combined with a dry -stone dams to form a base so that the height of the fall can be increased. Small
2.7.2.3.
permanent
Structures of this type are built than those mentioned above and in view should be taken .in their construction.
longitudinal
from materials of their higher
The factors
used are into
entering
(1)
the size
12)
the stability
(3)
infiltration fissures is
structures this is
have a slope the deciding
slope is too steep, the number of structures will be excessive and, secondary check dams can be installed between the main structures, the spacing.
The main materials
It
cross-section
which are more resistant cost, special precautions
The principle is to ensure that the bays between the on which the water wil.i not build up an erosive velocity; factor in spacing the structures.
--
small
weirs
These are intended to permanently stabilise the of a gully when vegetation growth is not adequate.
When the in this case, thus increasing
in
of the
dry
the
stone,
masonry,
calculation
gabions
and design
and concrete.
of such structures
are:
spillway;
of the structure;
of water downstream.
therefore
-
the peak flows
-
the nature structure.
below
necessary
the
foundation
which
to have data
to be evacuated
of the
structure
for
leaks
and
on:
throughout land
may create
the
a depth
structure's
life;
of at least
the
height
of the
- 77 -
If there be constructed
is an impermeable on this.
in other cases, trickles of water. Plan.
layer
in the subsoil,
the dam foundations
sufficiently deep trenches should Examples of this type of structure
be constructed to divert are shown in the Standard
In this type of dam, the flow occurs over the crest or trapezoidal spillways. of dished, curved, rectangular (a)
Spill
structures
(sills,
These are intended to halt event of a natural ledge.
guide
of the structure
Small earthwork
by means
channels)
regressive
erosion
in a channel
or gully
these structures may be temporary In the case of small channels, In larger gullies or channels, they will dry stonework or branches. masonry or concrete. with a chute, made from gabions, (b)
should
in tht
and made from be structures
dams
Establishment of water reservoirs behind small earthwork ?,ams can help in controlling gully erosion by halting water courses near to their point of origin. These are merely small dams with a height of no more than 3 m and a reservoir The design of larger dams is beyond capacity of several thousand cubic mebres. the scope of this document and reference should be made to specialised manuals. The operating principle of these structures is not erosion protection creation of a temporary or permanent water reservoir for use in irrigation, watering of cattle or fire fighting. The construction following data:
of small
dams requires
consideration
to be taken
but the the
of the
---
rainfall
patterns;
-
vegetation the nature of the feeder zones: surface, soils to determine run-off coefficients and discharge
-
the size
-
the characteristics (drill samples).
of solid
flow which
may fill
of the land
for
the retention
cover, nature volumes;
of the
basilIs;
the dam foundations:
depth,
permeability
---
The dam should he located In a nsck of the valley downstream from a hollow The ratio between the reservoir capacity order to minimise the dam dimensions. and the dam volume should be at least 3. The dam comprise;
a barrier,
a s.pLllway
and intake
In the case of an earthworks dam approximately construction specifications are as follows:
and discharge
3 m high,
structures.
the most common
in
-
-
slope
of upstream
bank:
-
slope
sf downstream
-
height
of dam crest
-
height
of the dam crest
-
crest
-
stripping of earth all the topsoil;
70
-
-
l/2-1/3;
---
--
bank:
l/2; --v--e-
above highest
--.p____
water
________
0.30 m; (freeboard): ----0.80 m; water level:
level
above the normal
--
1.20 m minimum;
width:
over the foundation
to a depth
of 0.20-0.30
m to remove
---.building of a trench 1.50 m wide along the dam axis down to the impermeable This trench will be filled with compacted impermeable earth; substratum. -------_ -/pill of impermeable clay earth containing no more than 30-40 per cent clay. The fill is laid out in thin layers of 15 cm thick and compacted; -a-the upstream wall of the dam is protected against wave impact by grassing or, a lining of gravel or dry stonework. if this is not possible, --
The size of the spillway should be calculated to evacuate floods of ten-year This may account for a major part of the total dam cost. The most intervals. simple are natural grassed spillways which must be sufficiently large, shallow Where construction and of gentle slope to evacuate flood water at moderate speed. the cross-section usually employed is trapezoidal with work requires excavation, a slope of I/4. Where adequate grassing cannot be obtained or the discharge to be evacuated is too large, it will be necessary to construct an artificial spillway in Such constructions may' not be justifiable for gabions, masonry or concrete. small dams. A drain channel is provided for exploitation made of a concrete tube held in place by concrete undermining.
of the water and this cbllars and protected
is usually against
The sluice pipe is used to evacuate small quantities of excess water without it being necessary for them to flow over the main spillway. It is similar in design to the drain channel. 2.7.3.
river
Principles dimensions -
of calculating
Given below are a few simple structures (weirs, dams). 2.7.3.1.
Calculating
Two cases should "dry".
structure formulae
for
spillway
discharge
be considered
depending
calculating
on whether
the dimensions
the sill
is
"wet"
of small
or
-
79
-
Dry sill
(a) It
is
assumed that
The flow
is
the sill
calculated
is
by the
dry
when:
following
general
formula:
IQ E m J;;;.H3'".Ll in which: Q = m = H = L q
the spillway flow in m3/s the coefficient depending on the shape of the the hejght in m from the crest of the spiilway length of spillway in metres. the
In practice, -
profiled
-
thin wall sill water spill):
-
thick water (b)
is
following
spillway
sill:
q
0.46;
wall
is
less
than
sill (the thickness m = 0.38. spill):
of the
sill
is greater
the
thickness
or equal
of the
to that
of
the
Wet sill
+ 0.2
is
applied
-g)
3 d-
to the preceding
= : = =
Length
2.7.3.2.
is
possible
The length
of the stilling to use the
of the
stilling
This
formula.
coefficient
;
coefficient for dry sill total height of water upstream from the sill the height of the sill the difference in level between the upstream the spillway H = height of the head of water on the spiilway.
It
sill
m:
of the
ml c m (1.05 m D S Z
m
are used for
(thickness m = 0.40;
A reduction coefficient calculated as follows:
where
values
spillway
and downstream
edges
basin
Rehbok, basin
Schoklitsh
and MCD formulae.
must be one or two times
the
height
of the
chute. 2.7.3.X.
It is classification
Face slopes for earthwork dam possible
to empirically height) (slope =baSe-
of
a small adopt
the slope
values
given
by Terzaghi's
- 80 -
Types
Upstream
of soil
Bomogeneous soil of wide-ranging particle sizes Homogeneous coarse silt Homogeneous silty clay Sand and gravel with clay core 2.7.3.4.
Protection against under the dam
2/T 113 215 113 water
Lane's rule can be used to check a danger of leakage. LV
+ Lh 3
slope
Downstream l/2
512 l/2 215
seepage that
seepage
under
the dam does not
present
m.h
In Lv Lh h
which: = the length of the vertical path = the length of the horizontal path = the difference in head between the upstream and downstream the dam the values for which are given below: m : Lane's coefficient, Type of foundation
Value
Very fine sand Fine sand Medium sand Coarse sand Fine gravel Medium gravel Coarse gravel Gravel and sand Medium clay Compact clay Hard clay
8.5 7.0 6.0 5.0 4.0 3.5 3.0 2.5 2.0
Gully
correction
slope
of m
1.8
1 .lj
structures
in
Cape Verde
sides
of
- 81 -
8.3.
WIND EROSION PROTECTION TECHNIQUES
Dune stabilisation Dunes are large sandy areas which can be moved by the wind when they are not When moved by the wind, these dunes can cover agristabilised by vegetation. block traffic routes, damage housing and cultural zones, render them sterile, result in the abandonment of entire regions. when carried by the wind at soil level, forms dunes when confronted with branches, hedges. These move in the direction of the dominant various obstacles: wind and may take on a typical crescentic shape with their tips pointing downwind with a gentle slope facing towards the wind and a much steeper slope facing away from the wind. There are two major categories -
Maritime dunes - are found sandy coasts with regular
-
Continental destruction
of dune:
maritime
dunes and continental
to some degree or other throughout winds blowing in from the sea.
dulies form in arid by cattle grazing.
regions
Conventional techniques -- for maritime dunes
and are often
the world
the result
dunes. on low
of vegetation
stabilising -
The most widely used technique was developed in Europe in the nineteenth century and was used successfully to reafforest the Gascogny Landes in France with pinus pinaster. The technique comprises three main phases: -
the creation
-
stabilisation
-
reafforestation of the stabilised is highly labour intensive. (a)
of an artificial
"coastal
of the dunes behind
Creation
of the coastal
strip";
the coastal dunes.
strip;
This
dune stabilisation
technique
strip
The objective is to reduce the quantities of sand carried and deposited by the wind by creating a slope which would form an obstacle to the progression of sand particles. The first above the high wooden stakes wooden stakes or sheet piling; cases.
step in establishing the coastal bar is to lay out along the beach water mark, a wattling between 0.75 and 1.00 m high made out of Where sunk into the sand and intertwined with close branches. it is also possible to use sheets of fibro-cement are not available, however, this is expensive and can be envisaged only in special
When the mound of sand that has accumulated behind the wattling has reached a height of 0.50-O-75 m a second wattle barrier is placed on top of the first and is continued until an equilibrium profile has been obtained, i.e. until the This may be reached within a sand grains can no longer pass over the obstacle. few years with a slope of 30-140 per cent and a height of s;;::zi:rtcly !C m.
- 82 -
When the dominant wind is not perpendicular to the beach, groins constructed in the same way are run out from the main wattle fence intended to halt the movement If a single coastal bar is not sufficient, a number can of sand along the barrier. be built parallel to each other. (b)
Dune stabilisation
This is intended to create conditions which are favourable This may be carried out with hardy perennial reafforestation. fences or by covering the soil with branches. Cover plants must ensure gooc soil They can be sown to burial by sand. of plants should be resistant to both be carried away by the wind and it is or protect the seeds by covering them cuttings often gives the best results. Some of arenaria in pescaprae in tenusissima,
for subsequent plants, wattle
coverage, have rapid growth and be resistant rows The first or propagated by cuttings. Seeds may the wind and wind-borne sea salt. advisable to sow during the least windy season Propagation by with straw and branches.
the species that have been used with success are marram grass (ammophila a member of the convolvulaceae family, ipomea Europe and North America), Madagascar and, in the North Cameroon, stylosanthes gracilis, melinis digitaria unifloris, cynodon dactylon, pennisetum clandestinum.
Rows of small wattle windbreaks made of cut branches, bamboo, palm leaves, These small windcover is inadequate. reeds, etc., are used when the vegetative Depending breaks of 0.5-2 m high are laid out in a network of 2-40 m in dimension. on the situation, these windbreaks can also be made up of plants such as saccharum as in Tunisia. aegyptiacum, Another process which can be combined with sand with dead branches or other plant debris. (c)
the preceding
one,
is
to cover
the
Reafforestation
The reafforestation of stabilised dunes is carried out by means of nursery The planting techniques are the same as those described in grown plants. The species used should be resistant to the effects of wind and section 8.1. salt and one cannot expect trees to grow suitably in a strip 200 m wide from the a network 1 x 1 m on the wind The plants should be close together: coastal bar. exposed side and 2 x 2 m on the sheltered side. In an arid compete closely
climate, grasses which have been planted with the young plants fcr water.
In certain very favourable climates tures, it may be possible to plant trees preparation. 3.1.2.
Techniques continental
for the stabilisation dunes
with long rainy directly without
to stabilise
dunes will
periods and hig:l temperaany other method of
of
The principles of stabilisation may be the same as those used for maritime dunes but the climatic conditions in arid zones do not always make it possible use them; this is the case in the Sahara, for example.
to
-
The procedures preventive together -
fascines
-
straw covering
-
planting
3.1.3.
that with
83
-
can be used to reduce soil pasture and track control.
(palm leaves
exposure to the wind are mainly The other procedures used are:
in the Sahara);
and grassing;
of windbreaks.
Rune stabilisation by a coating bituminous products
0:‘
This is a modern technique which has been used for afforestation Kuwait, India, Pakistan and, recently, in Libya and Tunisia.
in the US,
A bituminous emulsion is spread over the sand surface and penetrates to a depth When the emulsion dries it forms a crust which provides complete protecof 2-3 cm. The emulsion is spread mechanically: a bulldozer-drawn tion against the wind. It seems that. In Libya, each vehicle covered 4 ha per day. tank and a spray gun. eucalyptus) if the product the substance has toxic effects on certain trees (acacia, If it is applied before planting, planting work seriously is applied after planting. damages the protective layer and reduces its effects. This technique planting procedures. 3.2. 3.2.1.
requires
only
small
amounts of labour,
except
for
conventional
crop land protection Windbreaks
The objective of these is to reduce wind speed to less than 18-25 km/h at which The windbreaks are composed of trees and level the wind loses its erosive effect. shrubs. The distance protected is proportional is blowing perpendicular to the windbreak, of up to 20 times the windbreak height.
to the windbreak height. the wind speed is reduced
Wide windbreaks are not necessarily more effective The best results are obtained when the windbreak height as its width.
When the wind over a distance
than narrow windbreaks. is approximately the same
windbreaks reduce vaporisation. By reducing wind speed and increasing humidity, They may create a Dense windbreaks are more effective from this point of view. favourable environment for afforestation in a semi-arid zone. An example of a dense windbreak used in the US uses a number of different species in order to create a dense foliage over the total height of the windbreak. The central zone is made up of Shrubs are planted densely on the windward side. tall trees and the intermediate zones contain trees which are somewhat less tall. The whole has a triangular cross-section which forms a dense vegetation barrier over its total height. 3.2.2.
Other
These are cropping techniques resources and employ little labour.
which are carried Examples are:
out with
normal
farming
3se of cover
-
leaving
-
parallel-strip
-
tillage which maintains too t'ine a tilth;
-
green manuring.
3.3.
Pasture
crops
in rotation
-
crop residues
or in fallow
in place
land;
as long as possible
after
harvesting;
cropping; the soil
in clods,
by avoiding
tools
which
produce
prote5iion
This is a problem which is encountered particularly in extensive semi-arid Gcats and sheep are the wind's best helpers regions such as the Sahelian regions. in preparing land for wind erosion. Control
is mainly
by limited
grazing
and ba.lning
certain
zones.
-
85
-
CHAPTER C
REHABILITATION TECHNIQUES FOR WATERLOGGED SOILS
c.1.
AIMS OF DRAINAGE
The aim of drainage is to evacuate water in excess of vegetation and soil Certain soils have a natural drainage system others do not; requirements. these latter require the installation of an artificial drainage system. Drainage creates in the soil the conditions required for good plant development It improves the soil's physical and promotes soil aeration and root penetration. qualities and makes it possible to reclaim zones which were previously considered unsuitable for cultivation. In irrigated zones, drainage is linked to leaching techniques to prevent accumulation of toxic salts in the soil and also to prevent gullying and soil erosion. Drainage techniques are suitable the good of the community.
c-2. 2.1.
for
labout-intensive
work in activities
for
DIFFERENT TYPES OF DRAINAGE
Open ditches
They are suitable for a wide These are the most simple and most widely used. range of flow rates with very slight or zero slopes provided they are of adequate cross- section. Tney are most effective from the drainage point of view since they intercept Their construction and maintenance are both ground water and surface run-off. highly labour-intensive when no machines are evailaole. Their main disadvantages are their take up on crop land and the hindrance animals and men. Where the drainage between ditches, the land loss and the will be given to underground drainage. low density networks and when they are
size in view of the large area that they they cause to the movement of machines and requirement entail= only short distances hindrance become excessive and preference Open ditches are therefore used mainly for also required to evacuate surface water.
Channels are a type of small open ditch or gully designed to evacuate surface water. on pasture land or when the agri-.Channel networks are usual y installed The cultural value of t!ie land does not justify the installation of underdrains.
- 86 -
channels are usually 40-50 cm deep, O-C.20 m wide at the They can be dug by hand or by machine. at the surface. they require relatively frequent maintenance. effective,
base and around 1 m wide If they are to remain
to m 0 to 0.20 Channel Farming techniques can achieve wide and 0.50 m high are constructed a ditch at the base of the slope to 2.2. buried
drain
Beds 8-30 m the same objectives as channels. or furrows and ridges cut down the slope with collect the water.
Underdrains These are collectors in the soil.
made of drainpipes or They can be interconnected
a drainage ditch or into surface water directly.
a natural
other piping material, which are between each other and run into They cannot be used to evacuate
collector.
This type of drainage is expensive and is suitable only for soils with a It does however have the advantage of requiring minimum high commercial yield. maintenance and to have a long service life if it is correctly installed. Another advantage is that the land over the drain is free for cultivation. A very wide range of materials are used for under-drain construction. Certain are traditional materials and can be of interest in regions where modern drainage materials are difficult to obtain or expensive. The main 2.2.1.
types
Fascine
of underdrains
are:
drains
A trench is fascines leaving trench backfill.
dug to the required dimensions, a space for water drainage.
the bottom The fascines
is filled with are covered with
Backfill /
Fascine 2.2.2.
Stone A cavity
slab is
drain
drains produced
using
stone
slabs
placed
at
the
bottom
of a trench.
the
- 87 -
Drains
2.2.3.
with
stone
backfill
These drains are made with round stones They clog up easily. the gaps between them.
so that
the water
can run off
through
Wooden box drains
2.2.4.
They are made using a wooden These are suitable for soft and marshy land. They are used only box structure with an internal dimension of 7 cm or more. rarely. Peat drains
2.2.5.
These are used in peaty
soils
in which
the peat
itself
is used to form the
drain. 2.2.6.
Earthenware
piping
drains
These have been used since the beginning of the nineteenth century. They comprise fired clay pipes between 5 and 15 cm in diameter and usually 30 cm in length. have flat ends and consequently they may be moved out of alignment Also, they usually To overcome this disadvantage, if the earth settles. interlocking drain pipes have Fired clay pipes are manufactured in brickworks been produced in the Netherlands. They should be of very good quality if breakage is to be in the same way as tiles. avoided during laying and if they are not to crumble under the effect of water. All defective drains should be eliminated before laying. 2.2.7. similar
Concrete
drainpipes
These are used where fired dimensions.
clay
pipes
are difficult
to produce.
They are of
Concrete drainpipes ar e manufactured using special machinery and drainpipe quality depends on the method of manufacture and the quality of the aggregates used. These aggregates should be permeable to snsu-e good drainpipe porosity; however, the pores are rapidly blocked by fine soil particles in the water. In the concrete is attacked by sulphates in the water. acid and peaty soils, 2.2.8.
Bituminous
fibre
drainpipes
These drainpipes are made of fibre impregnated with bitumen and moulded under They are pressure. Holes or slots are made in the pipe to allow water to enter. lighter than clay or concrete pipes and are more resistant. 2.2.9. tural
Plastic
drainpipes
The use of plastic drainpipes underdrainage work.
is becoming widespread
in all
types
of agricul-
They are made of rigid or flexible non-plasticised polyvinylchloride (PVC). There are slots at regular intervals in the pipe walls to allow the passage of' water. The diameters used are between 30 mm and 100 mm. The characteristics of rigjd PVC drainpipes are shown in fig. C.l.
- 88 -
C.l:
-Chara,,:.‘ristics .._-_
Perforated
PVC drainpipe _---
Fig.
of r;gid
PVC drainpipes --_
Exterior diameter in mm Weight in kg Wall thickness in mm
32
40
50
63
0.110
0.138
0.195
0.273
0.8
0.8
0.9
1 .o
Rigid PVC drainpipes are produced in 6 m ?engths and, in special cases, The pipes have slits of 35-40 mm long and 0.5-O-8 mm wide perpendicular 9 m lengths. The of 20-50 mm depending on the type of s'oil. to the pipes' axes and at intervals The drainpipes are joined together by a sleeve. slits are staggered.
Slit:
Rigid
length 40 mm width 0.5 mm
PVC drainpipe
Flexible PVC drainpipes are supplied in ZOO-250 m lengths on a drum and are The pipe itself is corrugated, which ensures intended for mechanical laying. The main characteristics greater resistance to crushing and improved flexibility. are as follows: 0.7-1.0 mm Wall thickness: Connection by T's, sleeves, etc. 1.5 mm diameter Perforations - circular: 1 x 1.5 - 3 mm No. of perforations/m of drain: 600-700 Surface area of perforations/m of drain:
or rectangular
lo-25
cm'.
These drainpipes are easily blocked by loam and roots; they are also vulnerable to clogging by ferric hydroxide. During storage before laying they should be protected from sun and weather which causes ageing of the plastic and a deterioration of the mechanical characteristics. 2.3.
Mole drainage
Mole drainage is used in plastic and low permeability soils. The technique consists in digging a drain in the soil, without any external support whatever, using a ripper blade fitted with a "mole" - a pointed cylindrical metal tool - which digs a circular drain 0.05-0.12 m in diameter at a depth of 0.60-0.80 m. These mole holes act as drains but must be closely spaced. They require very special conditions: the soi: must be sufficiently plastic, the clay content should
-
89
-
not exceed 30-35 per cent and at the moment they are dug the water content should not be greater than the plasticity limit (ATTERBERG's Plasticity Index). The aggregates should have excellent stability (stability index lower than 1). Th%erequirements
for
mole drainage
are: --
-
a drain
length
of less
than
-
a slope
between 0.2 and 5 per cent.
Mole drainage costs very (from three to ten years). 2.4.
80 m between two outlets;
little
but it
-has a relatively
short
service
life
-Subsoiling
Subsoiling is used to mechanically break which reduce water penetration into the soil.
up hard pans or ploughing
compaction
Subsoili;lg rapidly changes hydrodynamic characteristics, in particular soil's hydraulic conductivity and makes it suitable for underdraining. It root penetration. loosens and aerates the soil which promotes better
c-3.
3.1.
the also
DETERMINING THE CHARACTERISTICS OF A DRAINACE NETWORK
Water movement in a drained-- soil Water movement in soil
It is presumed that is not drained naturally.
is shown diagramatically
the soil
is permeable,
in fig. isotropic
C-2.
and the deep water
Between two rows of drainpipes, the deep water table is convex in shape, height of the table being at its maximum halfway between the two rows. A drop of water which infiltrates the soil's surface, into the non-saturated soil under the effect of gravity. table, it is no longer subject only to gravity and it will the drain. Fig. C.2 shows diagramatically their distance from the drain.
the route
taken
table the
first descends vertically When it reaches the water flow in the direction of
by water
streams
(iepending
on
-
Fig.
C-2:
Water movement in drained --Input
*.-.
90
-
soil
(Precipitation
or irrigation)
._.
Permeable laye
Impermeable layer
-
The water drop 1 which falls directly gravity and descends vertically until
-
Water drop 2 reaches drain after travelling
---
-
above the drain is subject it reaches the drain.
only
to
the water a short
table clrse to the drain and finally reaches the distant: in the saturated soil. -. travelled in the water table increases. For water drops 3 and 4, the distance Following predominantly vertica:L movement in the upper part of the water the liquid-flows curve towards the drain and may finally reach it via table, an upward movement. -----Water drop 5 lands the furthest from the drain and its route first descends it then moves and ther curves when the impermeable layer is reached; horizontally and the final section ascends towards the drain. On the other side of the yy' axis, the situation is symmetrical. _-_--_--
When the depth of the permeable layer is small in relationship to the distance in the segment of soil above the between the drains, the flow diagram shows tnat, below the drain level the movement movement is predominantly vertical; drain level, The flow diagram differs depending on the depth of is predominantly horizontal. the impermeable layer; if this is at the drain level or only slightly below it, If the of the drain will predominate. horizontal movemen; in the direction of vertical movement will be impermeable layar is at greater depth, the proportion greater The shape of the water table surface between two drains varies depending and the permeability and thickon the input rate, the distance between the drains, ness of the permeable layer. When the input rate is zero, the water table surface will tend towards the It may also descend below drain horizontal to reach an equilibrium at drain depth. If the shape of the water table surface is level as a res,Jlt of capillary losses. it will tend to come closer to the soil's surface the more the distance more convex, betweeli the drains is increased or if the thickness or permeability of the draining layer is liecreased
-
The shape dependent Fig.
the the the the
of
water
the
table
91 -
surface
oetween
two drains
is,
therefore,
upon: input rate q layer depth of the permeable of the drained permeability distance between the drains
D; layer
K;
L.
C.3.
The optimum level of the water table (p-h) is the basic. datum in drainage problems and it is dependent on crop requirements. The other data are input rate flow rate" or "characteristic q, the depth D and the permeability K of the drained layer. The interval 3.2. 3.2.1.
between
Determination
of
Causes
wetness
of
the
basic
drains
is
determined
on the
(a)
(b)
Cc) (d)
(e)
causes
of soil
of
these
parameters.
data
Before trying to solve a problem of soil waterlogging, mine the causes of the wetr.ess. These causes may differ should be adapted to each :ase. The main
basis
wetness
it is necessary to deterand ;.he control measures
are:
basins above the zone in question. water from catchment it is necessary to intercept this run-off water and divert or man-made collectors (cf. Chapter B); ~-------river water overflowing into an allub.ial plain. In such a case, it is necessary to protect the zone by embankments or to dig drainage ditches to evacuate the flood water in a minimum time compatible with the type of crop; inflow of run-off In such a case, it into rlatural
a high underground conditions;
water
table
due to specific
topographical
or geological
--. a high level of rainfall producing excessive rise in the ground water level In an or the development of saturated horizons in low permeability soils. arid zone, the high level of irrigation required for soil leaching may drainage techniques In this case, conventional produce the same effects. are used; inadequate capacity of such a case, increasing the problem.
natural collectors. the size of the
This collector
may trap the water and, in may be sufficient to solve
1
- 92 -
Optimal
3.2.2.
water
table
level
The ability of the top layer of plants and for good agricultural slose to the surface of the soil, which is adequate
too low capillary
may also have water supply
of
soil to dry out is essential for gaod rooting If the water table is permanently too yield. good rooting will not be possible. a water table
an unfavourable during the dry
effect season.
since
it
will
not
provide
s rooting water table varies depending on the plant In a light soil, the water table may be hi gher than
The optimal depth of the depth and the soil texture. a heavy soil in which capillary
supply
is
in
greater.
In the case of leguminous crops for which the roots do not penetrate deeply, (30-60 cm) to ensure the water table should be relatively close to the soil surface This is also the case for grasslands. optimum yield. Cereals
require
Fruit species.
trees
a water
require
Permissible
3.2.3.
table
a lower
:;ubmersion
Crop submersion
between water
60 and
table
of
80 cm below
the
soil's
surface.
m or more depending
l-l.50
on the
time
covers:
-
partial
submersion
which
-
total plant
submersion stalks.
when the
Total
submersion
may cause
Crop damage caused
affects
the
plant's
root
water
level
rises
above
greater
by submersion
damage than depends
system; soil
level
partial
and affects
the
submersion.
on: -.---.----
-
submersion
-
the
point
-
the
type
7-15
time; at
which
of
plant
submersion being
occurs
days loss.
Fruit siderably
trees are highly depending on the
In project
retards
planning,
growth
cycle;
development.
Submersion
of
times of l-2 months prior to the vegetative submersion for 15 days may reduce yield by
produce is very sensitive in a reduced yield which
are particularly Maximum loss
plant's
--
Grassland may withstand submersion During the vegetative period, 30-50 per cent.
period.
Cereals formation. submersion.
the
grown.
In general, submersion of l-3 days may result in total crop
Market garden mersion may result
in
to will
submersion and even one day's subvary depending on the species.
sensitive to submersion curing flowering and grain may be as high as 20 per cent following a three-day
sensitive species.
to submersion
one may use the
following
although
permissible
the
results
submersion
vary
con-
times:
-
The figure Fig.
below
Effects of the
C-4:
93
some figures
gives
-
for
of submersion on yields optimum harvest)
the
effect
(maximum
of
loss
submersion
in
on yield:
percentage --
Submersion
time
3 days
7 days
15 days
Grassland Autumn cereals Spring cereals Maize Perennial fodder Potatoes Sugar beet
20 20 20 10 50
50 100
IO
20 50 40 80 40 100 50
Sunflower
10
40
-
3.2.4.
Type
of soil
Permeabiliuy is significant parameter porosity on texture, A number of these are: -
the
of
-
the
the ability of water to drain down into for calculating a drainage network. and organic-matter content.
formulae
relate
permeabi .lity
100
100 100 100
the Soil
It soil. permeability
is
a depend
The mos t important
to soil
texture.
are
same diameter
SCHLITCHTER formula
soil
particles
the
D;
the
value
HAZEN formula
I Km/s D,O is of the
the soil
diameter which permits made up of particles
Use of however, it
the will
formulae will ensure not give a sufficiently
tion
100
- permeabix-
This applies when all the R is related to the porosity;
of
100
Direct
measurements
of
permeability
This can be done in a laboratory The most simple soil in situ. called the "auger-hole method";
= 0.01
Dfo 1
cent
passage of 10 per less than DlO. the
correct accurate is
using whole and reliable the principle
by weight
order of magnitude of result for practical
preferable
to
the
samples or by the method is that of is as follows:
use of
of
the
por-
the results; purposes.
formulae.
direct measurement on ERNST which is also
- 94
A hole layer
is
made in
or a depth
the
soil
with
-
a 4-5
cm auger
down as far
as the
impermeable
of 2 m.
As much water
as possible
to reduce the ground water water rises in the hole is
is
removed
level by at measured at
from
least 5-10
the
hole
40 cm. s intervals.
by means of a ladle The speed
at which
so as
the
ground
Where: H is the depth of the hole under the ground water level in cm S the depth of the impermeable layer below the bottom of the hole in cm r the diameter of the hole in cm' of the water Y the mean distance between ground water leve 1 and the level Y over a period of time T K the hydraulic conductivity in m/day. The hydraulic (a)
K=(
(b)
K-
Fig.
C.5:
H+20
conductivity 4 000 r2 r ) (2 - Y w
3 600 r2 (H + 10 r) (2 - Y R
ERNST's
is '1 Y) 'At
X
calculated if
gif
S>
S
as follows: l/2
q
H
0 or if
S (
l/2
H
Y)
method Measuri .n stick
Depth
Water-bearing
Impermeable
3.2.5.
__ Intrinsic This
flow
rate of --.-.-.-
indicator
land
land
network
IS the flow that the drainage relation to a unit of the land's surface mined by the following equation:
network area.
must collec+, The intrinsic
and evacuate flow rate
in is deter-
-
where
sible time 3.3-
95 -
qc = the intrinsic flow re;e in llsiha of evaporation (a dimensionless e = the coefficient i = critical rainfall intensity in mm/h. The critical rainfall submersion time for T depend on agricultural
is the rainfall a recurrent time and eccnomic
-theage Network
3.3.1.
number
lower
for
a time 6 corresponding The values for time T. factors.
than
1)
to the permis63 and recurrence
network design
The design and layout of the drainage network depend primarily on topographical The first task is to locate the thalweg (middle line of a river) and the factors. The main collector drains should be located along Che thalweg. crest lines. Minor drains should empty into the main collector drains withcut ever crossing a crest line. The minor slope, slight drains Fig.
drains
should
be laid
out
at
angles
i.e. more or less parallel to the contour lines. (less than 0.003), they may be laid out parallel angles to the ploughing are also p 1 aced n: right
to the lines of greatest Where the slope is very to the slope. The minor direction (see fig. c.6).
c.6
The collectors main collectors the secondary
are
always
are situated thalwegs.
in
laid the
out along the main thalwegs
The layout of drains and collector!drain and should therefore be adapted terrain, layouts are shown in fig. C-7.
tne
right
line of greatest and the secondary
combinations may vary to each specific case.
The slope. collectors in
depending on Some typical
- 96 -
Fig.
C.7:
Layout
of a drainage
network
Intermediate
Transverse
drainage Run-off
Intermediate
collectors
water
~~zzJ$E+~~
Collector 5elt drains (protection against external run-off water)
3.3.2.
Drain
Drainage land
of
variable
Draining
of waterlogged
permeability
pocket
depth
The depth 2nd spacing of drains are two closely linked parameters. As d .ain 2"5r !I is increased, spacing between drains may also be increased. In homogeneous land, deep drainage has a certain number of advantages over superficial drainage since:
- 97 -
-
the
-
drains number
-
drains them.
table
is
lowered
giving
further,
may be more widely spaced, and drainage cost; Iare in this way protected
hand, deep drains season.
On the other in the dry
table
the
water
the
permeable
soil
not to put the drain of the two layers. the
into
overlies the
results
in
against
root
irvasion
tend
to cause
study
a very
impermeable
a too
should
impermeable layer
but
If the impermeable land lies above a permeable drain as deeply as possible in the subsoil.
For practical A depth of 0.60-0.80 as deep drainage. On very
drain purposes, m is considered
depth
varies
small;
aeration;
a reduction which
rapid
of
be carried
locate
subsoil,
between 0.70 a depth of over
water
to determine
is at
to clog
the
out
it it
drain
tends
fall
subsoil, to
in
preferable
the
one should
borderline try
to locate
m and 1.50 m. 1.20 m is considered
land, the drain depth will depend on drainage slope It may be necessary to have the drain shallow at the and the depth of the outlet. start and deeper as it approaches the outlet to ensure a sufficient slope for the water to drain away effectively. 3.3.3.
Drain 3.3.3.1.
put:
slightly
soil
which
a pedological In heterogeneous land, most suitable drain depth. If
better
spacing Selection
A distinction the permanent A large
sloping
number
for the permanent Europe and anywhere In irrigated drain water input regime formulae.
of methods
of
calculation
should be made between two regimes regime and the transitory regime.
of drain
of
water
formulae have been developed for calculating These presuppose constant input. regime. They else
where
rain
is
of
long
duration
zones and in regions of high intensity is not constant and it is therefore
and low
input
drain
and out-
spacing
may be used intensity.
in
and short duration rainfall, necessary to use transitory
Calculating the spacing between drains is easier for the permanent regime than use of the permanent regime formulae is often moreover, for the transitory regime; especially when precise knowledge about justifiable even in the transitory regime, food conditions and hydrological constants is not available.
- 98 -
3.3.3.2.
(aj
Calculating drain spacing the permanent regime
in
The HOOGHOUDTformula
Drain
spacing
is
given
by the
I
L2
fcllowing
formula:
= 8 K2 d h + 4 K, h2 9
4
I
where-: L
= q = K2 z K1 = h d
the spacing between drains in m the intrinsic flow rate in m/days or m3/m2 of the drained zone the hydraulic conductivity of the layer below the drain in m/day the hydraulic conductivity of the layer situated above the drain in m/day = the height of the water table above the drain level halfway between the two drains (in m) = the depth of the equivalent layer. A value which is a function of spacing between the drains L, the drain radius r and the depth D of the impermeable layer be;ow the drain (see Fig. c-8).
Use of this formula layers is at drain level, carried out by successive L is already known. Fig.
C-8:
Values
of d in
presupposes that the boundary between the two permeable which is not always checked. The calculation is approximations, with d not being known accurately until
the
HOOGHOUDT formula
D 049 --0.49 0.49 149 0.10 0.m aho,
D
UmQ%--
a71 0.60 0.63 a69 0.71 a73 074 (171 a75 a75 a76 a.79 1.~067 (~7s am on 0.89 a91 0.91 4x94 au a9d a96 1.n am au 049 I.(1D I.03 1.0s 1.12 1.1) I.14 I.14 I.15
l.n 2¶0 1.75
N
I.01 I.YJ I.41 I.11 I.34 I.59 I.U I.? 1.u I.63 I.43 I.67 IN 1.71 IJO I.73 I.11 1.n 1.11 1.n 1.M
Q7I (LPI I.14 I.9
the the
I.5 1.49 I.99 1.m 1.n I.1 1.91 I.97 202 2a 215 229
I.57 I.U I.Y 1.10 I.69 1.76 I.91 I.94 l.W In I.Y 1.99 i.5l I.% 203 211 1.97 20) 216 227 201 119 2% 213 211 2% 2SJ 241 217 211 244 254 222 2s7 251 2u 231 250 263 m 2Y 2% 27129s 241 2b5 2M 100 2U2792922ln224 234 291 1.01 3.24
149 224 ZJI
I.72 196 202 211 229 242 234 zm 2.71 2.17 ID1 I.15 24J
191 1.U 2% 1.U
I QPI a97 a.* 099 Q99 Q'H 2 1.n l.u, 1.11 I.90 I.92 I.94 1 aA9 249 296.2722w a.11
c 7 I 9 10 12.9 II 17.3 m
a U
la 24) 2% I.64 274 I
>.I 4.14 cu 4.57 4.74 SDl
4.n 4.u 4.95 s.23 I.47 J.R
6'10 a2 I.44 6rn 643 7.M
497 xs7 ait 6.63 70) 1.Q
3.1s %,I LU 7.00 733 1.a
a.84 9.64 3.m 6n7.n Ia4 5.30 644 n.ao 9.47 660 LY 9.97 11.1
-
(b)
99 -
The ERNST formula
The general
equation
is
as follows:
where: = the height of the water table above the level of the between the two drains in m flow rate in m/day q = the intrinsic = the thickness of the saturated layer above the drain DV of the thickness multiplied KD = K, D, + K2 D2 = the product permeability of the various layers in m2/day
h
the D2 D, = the q
thickness mean flow
Ln Do/ n K u = thickness DO calculated U
the
= wettened
Depending layers of
q
of the section
Rr = radial of
the
layer
perimeter
of
on the different
lower layer in m of the upper layer
with
resistance
which
is
a function
for
the
radial
the
which
drains
in
m by the
permeability of
halfway
K, drain
resistance
position
has been
drain.
position of the permeabilities,
drain the
in relation to the boundaries between formulae to be used are as follows:
2 h=B~+$+,n$ Kl
Homogeneous soil
Do < $ L
Drain at the boundarv of two lavers different Permeability Kl& K2 9L2 (KlDl + K2D2) + & K14K2 2 DV h=~+$&+&&r+ h=R
KS >) K2 + Hooghoudt formula
Ln "
Drain in the upper layer h
q
Dv 9L2 9L gf?i- + B(KIDI + ~2~2) + rrK1 In $
of
Calculating the transitory
3.3.3.3.
-
100
drain spacing regime
in
-
GLOVER-DUMM formula
(ai
- t/j ht
= ho x 1.16
e
if
$
<
0.80
0
j
=
VL2 10 KD
D
= Do + ho + ht 4
L2= ~71.16
2)
where: J
V hO
ht t
= reservoir coefficient = the effective porosity = the the = the q
load load time
above
the above the expressed
The effective porosity permeability expressed in
(b)
This as follows:
BOUSSINESQ formula applies
when the
(in in
days) per cent
drain at drain at in days. V is
given
times times
t t
approximately
by the
square
permeable
layer
root
of
the
cm
(1903) drain
is
located
on the
and is
expressed
- 101 -
Drain
3.3.4.
diameter
The choice and the amount Drain drain
and length
of drain of water
diameter
increased
with
is
diameter and iength to be evacuated. usually
drain
constant
length,
The flow rate drained multiplied by the intrinsic
is
i.e.
Where the
length to be drained Large diameter urains
inildequate. length may be longer
than
for
a function
over
the
the
surface
equal to the flow rate. Q = S.qc
is
= L.E.
length
whole area
product
of
flow
flow
in
this
surface
area
drained
becomes too may therefore
small
rate
and the
to be drained
large, drain capacity becomes be used; in this cast the drain but the cost is also higher. drains,
diameter
in
drains
are
to select the type that can be used.)
between
and collectors
drain
Collectors
5 and 8 cm. depending
of
on gradient
diameter. Calculation
3.3.5.
the
plot
.qc
The commonly used diameters of underdrains however may have diameters up to 30 cm. C-9 shows
the
drained.
the
(The simplest and the most widely used method is and its diameter and then calculate the maximum length
Fig. and drain
of
of
collectors
drains
The flow rate in collectors which feed into them.
(see
Collector diameter Fig. C.9).
Fig.
C-9:
Flow
rate
is
equal
may be variable
in
drainage
to
the
sum of
as a function
collectors
(in
the
of
l/s)
13.z: II -rt 1.55,5..c 8.: !I Il.05,I1.1 I.1 ;I .:1.03,1b.! ‘.I b':11.55,1..1 1.I I':1L,,.lO : .4 I! ::‘.o-‘zo.l I.! .:.I al ‘.I ‘.I ‘.( ,.! ,,! .J .I 1.1 1. 8.: 1.: .( I.( I.. .I 1.1 ‘.I #.I 1.1 I.! ‘.I1.5 I.( ‘.! I,! !,I 0.
1.X '.U :.U
.5. 1.0: 1.0: !.I!
).?I !.li i.l 1.5' I..! 1.1: i.O! L.?! l.OI i:;: l.il
! 0.25 0.’
dn
I Ii 1c lb 116,1 1‘ it 111 zz I 11 z lb rI z* 011 ,,*': 1 ,I I 11i!bl : II 5’11 Ill4 !‘U 4% 5hl I 35 +I I to z 6: I G, 0I bb II4z 5 ‘I I .5 ,I:, b bb5p L is O-Z& : r(5 I :1 bl¶Uz SE
I. a 1 1.5 1 1.s I I. s L 1.5 t.5 :5 I* 1.5 I 1.s ,
5 cz
1.
flow
flow
rate
rates
in
the
and gradient
minor
- 103 -
CHAPTER D
METHODOLOGY FOR SETTING UP A SOIL CONSERVATION PROJECT
D.1. 1.1.
PRELIMINARY
STUDIES
Aims
Setting up a soil conservation project comes within the framework of an over-all strategy which involves numerous disciplines and follows a logical process in decision making. The first phase of the process is the analysis of the situation from the physical, human and economic point of view. This should provide the necessary factors for deciding on the value of tne project, its limitations and advantages and the economic fundamentals from which it is possible to evaluate the significance of any measures that might be envisaged. Preliminary studies are the first stage to help in aimed at defining the aims of coherent and well-founded to be employed in achieving these aims. 1.2.
Situation This
analysis
analysis
will
cover
successively:
tics of picture data in
the soil degradation and the impact The analysis should in the region. order to arrive at a first estimation
1.2-I.
The physical 1.2.1.1.
Data
the physical and hydraulic characterisof this degradation on the socio-economic comprise a review of al.1 the available of
the
measures
that
might
be envisaged
context_ collection
The data may be obtai..;ed The type of the services. supply this information are (a)
the decision-making process development, and the means
follcwing basic data
consultation with the relevant national to be collected and the services that may
as follows:
Cartography -
The most widely used scale is I/200,000 or I/IOO,OOO. maps. -topographic Certain regions may be covered by maps using a scale of I/50,000 or I/20,000 In the case of numerous countries (North Africa, West Africa, Madagascar, maps may be obtained in France from the National Geographic InStAtUte etc.), (Institut geographique national);
-
Fig.
D-1:
Over-all
flow
chart
for
104 -
drawing
1 Preliminary
up a soil
studies
conservation
1
Possible
Aims
Analysis of basic data
Hypothesis of improvements
Land
I
studies
project
Economic
Project
meatures
Choice of improvements
components
-
-
-
aerial photographs. on black and white satellite information
105
-
Many countries panchromatic
have
film
at
been covered
a scale
of approximately
These
photographs (LANDSAT pictures). at the regional level.
by aerial
photograph: l/50,0005
may provide
interesting
(b 1 -Geology Geological maps at a scale 1/1,000,000, usually available from the national geological ties, etc. (c)
or
I/500,000
services
I/200,000. (BRGM in
These are France), universi-
Pedolx
General
pedological maps, where they exist, often have a small scale (1/1,000,000). For cer'ain projects, pedological maps may be available with and they can be obtained from geological or agricultural services. larger scales, (d)
Climatology
Usually, all daily precipitation.
countries
have
a precipitation
Climatologicai stations make more detailed intensity, temperature, evaporation, hygrometry, These data can be obtained tural departments. (e)
from
meteorological
observation
data
network
collection
wind
speed
services,
which
covering
measures
rainfall
and direction, airports
etc. and agricul-
Vegetation
Data about the type and distributicn of natural vegetation and the density main species that can be used for afforestation purposes can be obtained from cultural, water, forest and animal breeding services. (f)
Hydrology
Characteristics Type of hydrometric 1.2.1.2.
and agri-
Data
of the hydrographic observations carried
network out.
and the
hydrological
regime.
analysis
During the pre1iminar.y to determine the magnitude incidence end intensity cf Soils may be classified type of erosion to which damage caused.
study, utilisation degrad ;tion of soil the : actors behind
of the data should make it phenomena by highlighting the degradation.
according to their erodibility they are sloject and the incidence
while specifying and intensity
possible the
the of the
-
- 106 -
1.2.2 :
The socio-economi_c_ 1.2.2.1.
Data
The main data -.. (a)
context
collection to be collected
deal
with:
population in the zone in demography: number of working people, trends;
type of farming (Family, industrial, (type, yield, costs), agricultural
(b)
farming: production
(c)
soil utilisation: urban zones;
(d) (e)
animal
agriculture,
policy,
1.2.2.2.
development
which
should sectors
plans,
may be damaged or disrupted
permanent assets such as land, the infrastructure tion networks),
-
seasonal depending (flooding,
-
economic activity of communication make cultivated
Probable growth trend
1.3.1.
areas
breeding,
Forest,
current
legislative
be made of agricultural which might be affected
-
1.3.
etc.), income;
population, farmed, industrial
or
measures.
Data analysis
An over-all review order to specify all items
animal
agricultural
breeding;
agricultural
in
question,
activity by soil
and soil utilisation' degradation.
may be classified
agricultural infrastructure of economic activity
under
three
headings:
(buildings, (roads, etc.);
irriga-
assets such as crops which may be damaged to different degrees on the intensity and period of occurrence of the phenomenon crop destruction, etc.); uhich may be perturbed, due for example to the destruction water run-off or by wind-borne materials which may routes, land sterile or seriously compromise a region's industry.
economic growth rates should be estimated in order in the value of these assets over coming Years.
Assessing
the
extent
of
possible
data
about
to determine
the
measures
Damage assessment 1.3.1.1.
Collecting
Damage that may occur in classified into two categories:
the
damage
absence
of soi 1 conservation
measures
may be
(a)
the main one being the loss of land capital under the same Capital losses, heading as other infrastructural assets such as farm buildings, irrigation In estimating capital losses, it is possible to use as a bas iS networks, etc. These should be re-evaluated estimates of damage that occurred in the past. to bring them in line with current monetary conditions.
(b)
Production losses which may result From reduced soil fertility, flooding, Production loss may be a deposition of wind or river-borne sterile soil. variable phenomenon related to the intensity of the destructed phenomena, the main ones being, precipitation intensity in the case of rain erosion and wind In this case, the updated cost of annual force in the case of wind erosion. damage should be used for calculation.
Mean annual
1.3.1.2. The methods and related
that
to available
damage
may be used
for
determining
mean annual
damage are
numerous
statistics:
where a number of values exist calculated from the arithmetical
for
annual mean of
damage, the damage data;
mean damage should
be
when only a single value for annual damage is available and the incidence of that damage is proportional to this damage is not known, it may be hypothesised With a knowledge of the the intensity of the phenomena which cause it. relationship between the phenomenon behind the damage and the incidence of it is possible to deduce the cost of damage for various this phenomenon, assess the mean annual damage cost; incidences and From this where a number of damage incidence combinations to draw a "damage incidence distribution curve" Mean annual
damage is Future
1.3.1.3.
the
area
bounded
are available, it (see fig. D-2).
by the
co-ordinate
1.3.2.
damage
damage will vary depending on the forecast economic The calculation for mean annual damage should therefore economic growth rate.
Envisaged
possible
axes.
Future region. Forecast
is
growth rate For the be weighted by the
investment
prices is the sum of envisaged investThe amount of future damage at current be higher where the planned improvements are ment. The sum invested may, however, expec!.ed to result in an increase in the value of agricultural land which, after The level of land value increase have higher crop yield. conservation work, will may be assessed from the amount of increased revenue, at current prices, indexed by the economic growth rate for this type of income. Fig.
D-2:
Dama;
Incidence
curve ,
Damage curve
Incidence occurrence
of
phenomenon
Damage costs
-
-
DRAFT PROJECT
D.2. 2.1.
108
Aims
Once the draft study has made it possible to assess the the draft servation project and the envisageable investment, the means to be employed to achieve the set aims.
value
project
of a soil should
condefine
The draft project should define the various possible improvements From both the to permit decision making as to which project technical and economic point of view, These objectives are often contained in an will best meet the final objectives. for the development of a catchment basin. They over-all land improvement policy may be economic, social, political, ecological, etc. 2.2.
Analysis
of
basic
data
This analysis should cover all the data relevant to the establishment of the The basic data collected should usually be supplemented by field draft project. studies and surveys and then subjected to detailed analysis so as to form the basis for assessing possible improvements. The analytical methods that can be used are outside the framework of this book. We will, therefore, consider only the main data required in analysing a soil conservation project. Climatology: -
monthly
-
exceptional daily annual precipitation;
-
rainfall rainfal,
Morphology -
relief;
-
gradient
-
erosion basin.
and annual
precipitation
studies duration of
the
precipitation:
and statistical
statistical
analysis
with
and determination of relationships for various probabilities.
catchment
analysis; of maximum
between
rainfall
and
basin:
characteristics: forms:
mean values
classes
eroclibility
of
slope;
classification
of various
sectors
of
the
Hydrology: -
surface
area
of catchment
-
estimation
-
determination
of
flow
rates
from
man-made
-
determination
of
flow
rates
from
collectors.
of run-off
basins
- boundaries
of
sub-basins;
coefficients; structures;
Pedology: -
general
reconnoitring
-
auger soil the scale
samples with of the project
of
terrain; sample (usually
density depending one sample per
on land variations 5-10 ha);
and
- 109 -
-
collection of soil samples ties and permeability;
-
determination
-
evaluation
and mapping
for
analysis
of crop
of
physical
suitability
and chemical
proper-
categories;
of earthworks.
Topography: -
drawing up of plans suitable for the direct surveying or by photogrammetry;
-
survey of land cross-sections
-
types
-
crop
-
yields;
-
animal
(l/10,000
profiles along the main emissaries for the main features.
.. animal
Agriculture
project
with
to
l/20,000)
preparation
by of
husbandry:
of crop; rotation;
type
a*nsity,
of grazing,
use of passage
routes.
Socio-economics:
2.3.
-
industrial
-
agricultural
-
market
Hypothesis
structures; income;
and rentable
value
of land.
of improvements
G&en the basic data have been assessed, the project leader may present one or more hypotheses for improvements that are both technically and Financially acceptable giving justification for the principle behind the project and the main technical arrangements. This
hypo.
sis
for
improvements
should
be accompanied
by the
following
docu-
ments: -
location plan at a scale of l/20,000 or l/10,000 locate the siting of the main structures;
-
the main technical and:
-
arrangements
-
characteristic
-
cross-section
-
layout
-
emissary
improvements,
-
standard
plans
-
spacing
-
layout
-
requirements
over-all improved
flow a.4
together
and type of
forest
assessment hectare.
for
the
relevant
it
is
possible
standard
plans,
rates, spacing
of defence
of main and secondary
for
with
From which
and drainage
networks,
collectors,
the main structures, of plants, roads, and location
of improvement
of nurseries, costs
with
etc.; an indication
of cost
per
to
- 110 -
2.4.
Economic
analysis
For each draft in current account, 2.4.1.
project prices,
The expenditures
it is necessary For each of the
preliminary investment: tion compensation, etc.;
-
maintenance
valid 2.4.2.
and expenditure measures.
include:
-
studies,
and operating
These expenditures economic footing.
to draw up an income planned conservation
cost
of improvements,
land
purchases,
evic-
expenses.
should
be discounted
so that
they
can be compared
on a
Income covers:
-
the main component in a soii capital appreciation, the anticipated additional discounted income;
-
As a result of the protection measures, damage will be reduction of damage. totally eliminated in the reduced For a given phenomenon recurrence time, i.e. In the damage incidence distribution curve case of small recurrent periods. 0.3, this will be seen as a reduction in damage costs For shown in fig. By comparing this curve with the damage curve as It given recurrence time. the reduction in the mean annual damage is the was prior to the improvements, These curves may have a different shape area between the two curves. and their comparison is essential For depending on the type of improvement, For example, we have selecting between different types of improvement. The curve shown in fig. D.3 two types of curve that followed improvements. Curve Cl shows damage distribution incidence Following afforestation work. to an absorption network in an area where there are C2 applies, for example, embankments may be broken with damage which rainfalls, heavy, low-incidence would be greater than the initial damage.
Fig.
D.3:
Damage incidence
distribution
conservation
project
cost
-
Damage Co before measures
-
Damage C, after measures
defence defence
Income R = Co - C, Mean annual
Incidence
1
being
return
-
Balance
2.4.3. Ihe viability
-
sheet
balance
sheet
of income
and selection The main
criteria
used
it
possible
to
define
are
is
viable
rate, profit profitability
the if
difference there
is
which is is zero. rate
between a profit
incorn at
and expenditure.
current
prices.
the value of the actualisation If the improvement is financed should not be greater than the
rate for by a loan
rate.
-
The relative receipts. projects.
-
Cost
which is equal to the quotient gain at discounted prices, This makes it possible to choose between various independent
benefit
Selection
2.5.
makes
are:
which
Internal profitability which the discounted the internal loan, interest
and expenditure
criteria.
Discounted profit, The improvements
-
111 -
of
ratio. of
improvements
The draft projects make it possible to define the alternative improvements intended to achieve a stipulated objective and which are technically and however, They also provide the factors for making a choice; economically feasible. this will not always be guided by the economic factor alone but may also take into account other criteria, e.g. social, political, etc.
D.3. 3.1.
Objectives -
Once the draft project has the project itself improvement, for the implementation. The project and drawings. 3.2. 3.2.1.
-
/
THE PROJECT
Field
covers
additional
permitted the selection of a possible type covers the drawing up of all the necessary
field
studies
and the
preparation
of
of items
documents
studies
Topographic preparation intervals
-
longitudinal of l/2,000
-
cross-sections
of
work of plans at a scale of 112,000 or l/5,000 with contour lines at 0.25 III for slight gradients and up to 0.5-I m for steeper gradients
plofiles of natural water outlets and main collectors for the horizontals and II100 or If50 for the verticals; of outlets
and all
salient
points
at a scale
of
at a scale
l/100
or
l/50.
- 112 -
3.2.2.
Survey
borings-
The technique them will
vary
and depth
depending
For plantation
on the
work,
it
is
difficulty of digging planting depth every 10 ha or so. For cut-and-fill
and the sampl e borings type of work envisaged.
of
analyses
neces sary to determine by carrying out holes,
earthwc-k,
trenching
soil
to
type,
a sample
difficulty
should
be carried
humidity
boring
of
recessnry to determine soil type and in works, it i Soil analyses are carried out on samples taken with an permeability. depth greater than the maximum drain depth tind at a rate of one sample it is also necessary to dig a trench every 50 ha to make a descriptive
3.3.
Project These
They 3.3.1.
a descriptior
of
the
m in
particular auger every soil
at a 10 ha; survey.
to dig one or more trenches height of the finished F+-uc-
project
and assessment
of
expenditure.
comprise: Written
documents:
(a)
an explanatory memorandum describing cal arrangements;
(b)
a descriptive out and the
(c)
specifications
Cd)
an analysis
(e)
a quantity
3.3.2.
and the 1.00
documents comprise
the
project
principle
and
estimate which enumerates and describes the origin, quality and preparation of materials; for
the
work
and breakdown estimate
which
map at
a scale
to
of
be carried
out
work
by a commercial
a location
!g)
a map of
(h)
a longitudinal
(i)
drawings
the
of
defence
network
profile the
of
structures
of
the
expenses
for
each
item
l/20,000; at
the at
main
a scale
of
l/2,000;
collectors
and the
a suitable
scale
emissaries; (l/20
or
l/50).
techni-
to be carried firm;
Drawings:
(f)
the
prices;
calculates
on
be assessed.
For drainage
For the construction of small dams, it is necessary along the axis of the structure to a depth equal to the ture in order to determine soil types and permeability.
out
of
work;
CHAPTER E
PROJECT IMPLEMENTATION'
This priority
skilled
conservation work sites in which chapter describes the operation of soil is given to labour-intenstive procedures using untrained manpower, little a large number of simple tools and few machines. labour,
E-1. 1.1.
Survey of local conditions site reconnaissance
Before opening tion to survey the decide on the work Natural
1.1.1.
GENERAL SITE
ORGANISATION
and
the site manager should make a prior visit to the locaa site, techaical and economic constraints so that he can major natural, procedures and conditions.
constraints
The main constraint is climate which may make it necessary to halt work at the either because of frost which prevents masonry site for some period during the year, and concreting work being carried out or due to excessive heat which may inconveniThe rainy season may also prevent certain types ence workers and reduce output. of work being carried out or be an impediment to haulage or materials supplies. Water flow should be investigated before work is carried out on water courses. PPvine or gully rectification and dam construction should be carried out at the lowest water level or the work may be severely damaged or even totally destroyed Nevertheless, if the during the construction period by the arrival of flood water. work cannot be carried out at any other period or if the flood calendar is not additional protection such as the installation of coffer dams sufficiently regular, tr,is type of additional protecHowever, with water diversions, should be planned. Economic optimalisation should be sought between the tion is ustially expensive. 1
This chapter covers only the general principles of site organisation and Soil conservation work does not, in fact, necessitate any project implementation. types of work are applicable special organisation and the guidelines for other Reference should be made to Training Course No. III without any major adaptation. which has been produced as part of "Project design, implementation and evaluation", the Inter-regional Project for Planning and Administration of Special Public Works Projects.
- 114 -
cost
of additional For building. tion of
is the
not
protection and the danger of the structure being destroyed during the small structures described in this document, additional protec-
ususally
structure
necessary
being
destroyed
The sanitary conditions in particularly important for the Information should be obtained safety and control measures can the hygiene of epidemic disease, particular attention. 1.1.2.
Technical
and economic
and would during
be too
expensive
in
relation
to
the
danger
building.
the region are another natural constraint, and are setisfactory progress of labour-intensive wrrks. about the risk of any epidemic so that the necessary Since water is a major vector be taken on site. of the water being used should be the subject of
constraints
During the site reconnaissance? note should Site access should be assured. taken 3n the condition of existing roads and tracks, their distance from the constructlon site ,nd any need for the construction of new access routes.
be
be established by examining the potential of Supplies of materials should the quality of the materials they supply, delivery capabilities existing quarries, Employment can be increased when use is made of local materials which and prices. are available clcse by and can be exploited without great difficulty using rudimentary techniques.
At the project design stage, it is essential have suitable are available in adequate quantity, cessed at a rate which meets site requirements. for materials exploitation, processing and haulage a decision is taken on reliance on local materials.
to ensure that characteristics
these materials and can be prothe manpower required
In addition, should be assessed
carefully
before
In this way, a reinforced concrete weir would require large quantities of sand, gravel and cement and wculd ideally be constructed using capital-intensive methods. In such a case, it would its replacement by a stonework weir might be envisaged. be necessary to ensure that the necessary quantity of quarry stones was available, that the stone would be of sufficient hardness and that the haulage distances would not be excessive. If these requirements were not met,'the advantage to be drawn from using these materials would be eliminated by the high cost of vehicles for t-,h e I r transport. price
Frr non-quarry factors should
materials such be examined.
as wood,
fuel,
cement
and steel,
the
supply
and
Supplies of equipment. It is necessary to assess the number of tools and machines required on the site: .onditions for the pu-chase of new equipment, local Supplies of new resources and the condition of available second-hand material. equipment may take a long time in arriving and it is advisable to make allowance for this when plans are prepared. The possibility of manufacturing certain simple tools and having equipment maintained and repaired by local craftsmen should be considered. If local resources are inadequate, plans may be made to train local craftsmen or equip the site with Its own resources (small workshop, etc.j.
-
Local
manpower
and supervisory
-
local
availability
of
unskilled
-
local
availability
rf
skilled
-
availability
-
working
-
cash wages
of
in
-
should
be selected
taking
into
account:
workers;
workers:
working
and payment
walkers
workers
supervisory
conditions:
115
hours,
such
as blacksmiths,
foremen, social
topography
structure,
public
masons, technicians,
etc.; etc.;
holidays;
kind.
Consideration should also be given to seasonal variations which may be very and be a major constraint for work which requires continuous marked in certain cases, in river bank pl'otection work, which is normally carried For example, progression. a marked the time factor may be of particular importance; out during the dry season, seasonal shortage of labour may make it necessary to change the type of protection work or the haulage technique (use of haulage vehicles in operations for which they Completion of the work in stages or segments might be a are particularly viable). possible compromise where there is a temporary labour shortage. The lack of skilled workers may also be a deciding factor in the design of the A gabion or stonework retaining wall would require lesr skilled workers structure. On the other hand, it would be necessary to than a reinforced concrete structure. Consequently use much larger quantities of materials to achieve the same strength. the structure will probably take longer to build and its commissioning will be delayed. 1.2. 1 .2.1.
-Project
planning
Objectives
of
planning
Operational planning is an essential management tool which will make it possible to pursue a strategy or tactic, to keep control of the numerous factors that may The objectives of affect final cost, and ensure thr best use of available labour. work preparation and organisation, planning are those stipulated by task sequencing, These entail the drafting of various documents, and work control and follow-up. the type and precision of which are directly related to the type of work being managed. With these documents it should be possible to have a precise idea of the abstract factors in a site, to highlight interdependence between various activities and pick out those operations which demand the project manager's greatest attention rainy season, in relation to the numerous constraints that have been foreseen: religious holidays, harvesting, etc. Depending on the size and complexity of the project, it may be necessary to operations and basic tasks, the repetition of break down the site into activities, Planning is which over a given cycle calls for specific attention and analysis. therefore a task for a technician with a thorough experience of building sites, men, working methods, the various presentation techniques and with a good mind for analysis and review. It is a task for a specialist.
-
Forms of
1.2.2.
It
will
of which planning
-
116
planning
and their
requirements
be necessary
to select
between
existing planning procedures, all In deciding the suitability of the three factors should be taken into
various
have certain advantages and weaknesses. procedure for the project in qUeStiOn,
consideration: The criterion affecting the choice of presentation system Project complexity. The majority of works involved in a is that of the complexity of the works. relatively simple and the interdependence betsoil conservation programme are ween the various tasks or operations is direct and relatively uncomplicated. Experience has shown that a choice of one of the following three types of presentation would meet the requirements of nearly all programmes:
(a)
(b)
-
bar chart
-
time
-
network
or
and location or
Exploitation skill of the
(c)
GANTT chart
planning;
chart
critical
planning;
path
planning. The programming technique will depend on the It will therefore differ depending on whether the staff responsible for charge of the project,
of the workers
document. using it.
the user is the engineer in the works programme accounting,
supervisor
Type of works.
This
-
work
covering
-
linear
work
-
work
carried
-
labour
-
material
-
plant
-
general
-
repetitive
-
general
-
financing
will
also
affect
a large
area
(reafforestation,
(ravine
The factors which programming technique:
or the
correction,
out
at a given
are
being
choice
erosion point
planned
the
of
of
programming
dune control
(small
may,
foreman.
stabilisation,etc.);
ditches,
dam, weir, course,
technique:
also
etc.);
etc.). have
an effect
on the
requirements; and tool rotation
supplies;
and maintenance;
works
organisation;
cycles
of
progress
basic
tasks
and supervision
schedule,
f of
the
project;
etc.
Clarity and ease of interpretation are prime requirements in planning and an effort should be made to present information simply, by giving a self-explanatory and precise picture of the problem being analysed. The highlighting of interthis makes it dependence between various operations is a fundamental requirement; possible It
to pick
out
critical
tasks
which
should
be given
major
be noted that planning is merely a hypothesis, for scheduling the various tasks in a project. fore be possible to correct it and, if necessary, modify or adapt change of work plan.
realistic
attention.
should also possible,
although the mOSt It must thereit
flexibly
to any
117
1.2.3.
-Planning
procedure
All planning commences with the basic technical data:
ing -
assessment
-
volumes
-
probable tions,
-
of
available
labour
and quantities
for
performance in particular;
-
special
site
-
various
constraints
-
allocation
-
labour,
-
availability
for
in
each each
various
the
(rainy
items
project
of
in formation
and calculat-
zone;
task;
basic
task
storage,
requirements:
of
collecting
season,
in
water,
view
of
access
harvesting,
specific
road,
religious
climatic
condi-
etc.; holidays,
etc.);
funds;
equipment, of
tool
requirements;
equipment,
tools,
etc.
The various tasks involved in the completion of the project are then placed in Any form of depiction can be used: a logical sequence. arrows, rectangles, bars, out in parallel etc.; then one adds to the list those tasks which can be carried and the ordering tasks (ordering of supplies, rotation of vehicles, requests for topographic studies, for example). In this way, one obtains an initial picture which highlights the task sequencing. The diagram will be supplemented with information on the basic times for each activity, the labour and mechanical A resource.; to be employed and all the constraints which can be seen so far. number of diagrams are drawn up in this way in order to identify the most economic programming. The sequencing of operations is the most delicate part maximum attention. Once these studies have been done, the presented in the most suitable form.
of planning and requires work's programme can be
In the following paragraphs we will examine in sequence the planning of a single construction site using the three most commonly used methods (bar charting, time and location charting and critical path planning). The example in question embankment combined with the general organisation of a site of 8 km of protective an irrigation Fig.
E-1:
channel Cross-section
(see
fig.
E-1).
of channel
and embankment Grassing
Stone
facing
bank
is
- 118 -
The list
of
the
main
operations
is
Direction
of advance
Install site Strip vegetation Excavation Stone
-
8km
Gang No.
Gang size
Duration (weeks)
2
200
12
facing
This lists of zero duration comprehension.
The type
The ordering operations, tasks. have been omitted place ctinstraints, to the ordering of stones, cement,
the main operational but nevertheless These may related
Bar chart
on the
as follows:
of
which are to facilitate etc.
or GANTT chart chart
proposed
by GANTT is easily One lists, producing it.
read and requires on the left-hand
little side
skill of the
part of the person the various operations to be carried out in usually from top to bottom, their logical order of execution and on the horizontal scale the time schedule against each operation, are drawn rectangles, Horizontally, to a convenient scale. )ropcrtional in length to the time the operation will take. or lines,
2C workers
0
100 wor!tcrs
JJnskilled I.abour requirements
- 119 -
To the lower indicating labour, made by joining gang movements
section tool,
of the planning equipment, etc,
up the various during operation
chart it is requirements.
operations by arrows of the site.
The major disadvantage of this type relationships that exist between It is also difficult complex projects. relationships
of
the
tasks
are
(linked
GANTT chart)
to show
of diagram is that it does not show the different tasks, especially in the case to supervise project progress since the
various of spatial
possible to add a diagram Improvements can also be
not
shown.
this type of diagrammatic presentation is very useful and is Nevertheless, summarising detailed scheduling usually used for planning simple construction sites, and for displaying to a large number of that has been analysed by other methods, and in particular the workers themselves, the results of these analyses. people, 1 .2.5.
Time and location
chart
planning
However, it can be used This is an extension of the GANTT-type bar chart. bank protection works, iinear soil only for linear and narrow sites such as: conservation work-, forest tracks, embankments; or for tall and narrow structures: retaining walls, weirs, small dams, which entail successive repetition of the same activities. The basis for drawing merely plotting on a chart and an X co-ordinate (the
up a time and location chart points against Y co-ordinates chainage of the project).
is
very simple and entails (time in a convenient scale)
A Y
Time (weeks)
I
0 0
1
2
3
.-x.
4 km
project
chainage
>
Using this technique, points A and B are defined in both time and space. Point A is therefore located at the 2 km chainage at the start >f the third The line week; point B is at the 4 km chainage at the start of the fifth week. joining A and B therefore represents a two-week task being carried out between the 2 km and 4 km chainages of the project (an erosion control ditch, for example). The direction of advance of this task is of course defined as going from left to of the fourth right. If a check is made on the advance of the work at the start week, it will be necessary to ensure that the 3 km chainage (point M on the chart) One can therefore see the value of has been reached as foreseen in the diagram. since one can detect at an early date this method in site supervision and control, any
delay
or anomaly
and rapidly
make the
necessary
organisational
changes.
-
It is construction
120
-
section of the work under possible to add to the chart a longitudinal on which are marked the main features which may act as constraints: This
river to be crossed, cemetery, etc. X axis above or below the chart.
diagram
should
be drawn
parallel
to
the
Any isolated
point on the chart will show a task of 0 duration at the specific This will be an order task (for example, ordering the supply point of the site. of steel, cement, etc. to the site). A vertical line represents a task being carried out at one specific point of the site (construction of a weir, for example), and the duration of the task will be shown by the distance covered by this line on Two parallel lines indicate operations carried out the selected Lime scale. simultaneously b;r two teams at different locations: Day No.
16
Day No.
10 __ I
0
1
2
3
Tall and slender projects are shown using the ease in reading the planning chart, the time scale and the height of the structure on the Y co-ordinate Fig.
4
I
5
6
7 km
same principle; is
however, for shown on the X co-ordinate as is shown in fig. E.3.
E-3.
-
5m 4
6 VI ti H’
Cabi
. !: -.--
-I
:t's logic &hart; the required resources are not yet taken into consideration. The second step is to deploy these resources (manpower, time, materials) between the various operations so as to optimalise production time and costs. When the
network
has been completed,
the
t'critical" activities identified so that particular attention can be paid to them during the work. It is usually advisable to present the results in the chart which is more easily read and used by the workers themselves. Developing a network diagram requires important of which are given below:
the
use
of
special
should be the course of form
terms,
of a bar the
most
-
a chart
Network or graph: usually orientated. lines,
122
-
comprising
peaks
joined Requires
beginning or end of an activity. Event: is shown by a circle in which are indicated: the earliest and latest finish dates.
the
Earliest
Task or activity: actual time required sequence. Logical which
The event
chronological
number,
a strategic the network main linkage
number
time
this
is
a sequence
of
interdependent
is
an event commence.
at
tasks,
the
order
several activities finish or from which It is may initiate a number of operations. In the case of large, complex projects, the work. more or less extensive charts starting from these
stage in the course of can be broken down into points.
Earliest
event
time:
starting
from
the
initial of
event at time the successive
on a single
zero, the tasks are
event,
this
event
a backward path is Latest event time-: final event and taking successively the
If a number of of the shortest
paths path.
Free float: event time.
is
Dummy activity: dependence and linking zero duration. Network construction
converge the
on a given
difference
made over the network starting from duration of each of the basic tasks. this event will be given the time event,
between
this is a broken line two events in different
construction method site comprising the
(practical following
the
latest
event
time
and the
example): activities:
i.e.
a weir
foundation
Immediately job
preceding
Job
Duration (days)
A B
Set-up site Marking out Construct shuttering Prepare steel reinforcement Excavation Install shattering Install steel reinforcement
2
Commencement. of
1 2
A A A
2
B
2
Place
2
C-E D-F Conclusion
concrete
earliest
joining two events showing an interA dummy activity is sequences.
No.
G H
of
which A node
sequence of the arrows is traced and the durations added together. When a number of paths coincide will be given the time of the longest path.
C D E F
and
be changed.
this Node: several activities
the
curved
Latest event time J5?c the length of which is independent of the shown by a line, This line ends in an arrow which shows task to complete it. event
sequence:
cannot
cr
no resources.
event's
Event <-
by straight
4
1
of
site
site
of
- 123 -
This which Fig.
list
forms
of the
jobs
links
will in
be classified the
network
by order (see
fig.
of
sequence
in
the
table
below
E-5):
E.5. stage
Stage-2
1
/
Stage
3 --/
Stage
4
~~
Stage
5
Stsge
6
f
Install steel reinforcement
shuttering
----A Set-up
-c
Pour
concrete H-
\ sit 1e
Prepare
steel
reinforcement
=I==
I
will
The network will then be added the earliest
The I'floats" for critical path ( -H)
be laid out using the symbols described and latest times for each event.
each event (latest event time minus will be the one which passes through
above
to which
earliest event time). the events with a zero
float
In this way it will be seen that job D can suffer a four-day delay (8-4) without any repercussion on the final completion of the project. On the other hand, any delay in the completion of job C will have repercussions on the final completion date. It will be seen resources but indicate D have been completed.
that jobs 4/5 respectively
and 617 are "dummy" activities. that jobs F and G cannot start
They require no until jobs C and
- 124
-
path method for the The same principle is used below to show the critical The stage classificaconstruction of the 8 km embankment and irrigation channel. that for this type of site, It will be noted, however, tion method will be used. They are as follows: certain constraints have to be introduced. -
job
B starts
one week after
the
start
-
job
C starts
two weeks after
-
job
D starts
two
weeks after
the
-
job
E starts
after
completion
of
-
job
F starts
after
completion
of' job
the
of
start
job
of
start
B and
Stage
the
tasks
1
Stage
Fig.
1.3. 1.3.1.
Diagram
E.6:
Setting
C
C
ing in each job and that part which
by distinguish of the others
2
Stage
3
C (2 days) B
Stage
4
C (2 days) B D
Stage
5
F E
development
up the
Construction
job
by stage:
A (2 days) B
A (1 day)
B
D.
Allowance can be made for these constraints that part which must be carried out independently has to be carried out simultaneously to others. Scheduling
job
of
jobs
A
site of access
roads
When access to the site is difficult, an access road will be necessary for supplying the site with equipment and materials. The works supervisor should ensure, dcring the course oi' the work, that the necessary signs are in position protect the road construction workers and to avoid accidents.
to
-
Construction
1.3.2.
of
site
125 -
buildings
accommodation for the The buildings (offices, sheds, etc.) should be located at a relative mess room, workers, the access road to avoid noise and dust. The workshop avoid
expensive
and store
Plant Plant
possible;
be built
Site
1.4.
(a)
as possible
to
the
site
to
a dry
place
for
storing
the
cement.
be stored
plant
and fuel
from which away
dust and direct sunlight is not muddy or sandy.
it-: the
shade
from
stores
shou'.,l
be kept
on the
site
accommodation clean
to avoid
and the fire
technique
Site
supplies
Good site
planning
necessary equipment the work of a gang always an increase
depends
especially
and materials. Delays in supplies the whole site; and his may affect in costs.
being
well
supplied
with
a stock of the most common spare parts At the same time, and this should be managed to ensure security of supplies. Quantity
the
may make it necessary to halt the consequence of this is
From the opening of the site, the works supervisor should have a schedule This should be kept supply requirements for the various stages of the work. date as the work advances and steps should be taken in advance to ensure that suppliers are able to meet deadlines and supply the necessary quantities.
(b)
if
management
Mana ement
1.4.1.
in
should be stored where it is protected preference should be given to an area
a : ;-und
The hazards.
as close
installation
Fuel reserves should storage area.
plant
be built
and
transport.
A shed should 1.3.3.
should
works supervisor and distance from the site
should
of up to
be established
measurements
It is necessary to measure the work actually completed !and the quantities of In materials used and to compare this with the estimates made p!?ior to the work. the case of earthworks, these estimates are based mainly on measurements of surface areas and lengths intended to calculate the volumes involved. in
Quantity measurement also covers cost calculation: fuel consumed, These
estimations
may be entrusted
estimation transport
of all distances,
to a quantity
the other etc. surveyor.
factors
involved
- 126 -
(c)
Productivity
This
involves
individual
improvement improving
gangs
being
To achieve
gang
the
foreman
capabilities
the
workers'
-
the
gangs
-
the
best
workers
or the
best
-
the
most
suitable
tools
are
-
the
workers'
Daily
should
ensure
and competence
-
(d)
and organising
the
various
tasks
to avoid
idle.
this,
are
output
that: are
used
to
the
best
effect;
homogeneous;
welfare
Works progress progress
is
kept, Fig.
E.5.
are
encouraged
(incentives,
bonuses,
etc.);
used;
looked
after
(housing,
food,
etc.).
reports
reports
The planning should the site supervisor
gangs
should
be drawn
up and signed
if the be updated each week; should be informed immediately.
by the
planned
foreman.
tempo
has
not
been
m Excavation volume 8 000 __ 6 000 __
7 1.4.2.
Personnel (a)
I 14
I 21
Time
in
> days
management-
Recruitment
of workers
Special labour-intensive public works programmes require special personnel management which are matched to the specific social objectjves of these programmes Voluntary worker participation can be obtained only by suitable prior preparation, and make use of public information and which may be of an administrative nature, awareness campaigns. When the project exceeds a certain level of workers and time, it is necessary the volunteers themto organise a volunteer recruitment and handling programme; selves should be classified by specific criteria to the jobs they will be expected On recruitment, each to carry out taki.;g into account their special abilities. worker should receive an individual work card which may be based on the model shown below.
-
Fig.
127 -
~.8.
Work card Group
(E)
Name ................................. ...................................... Sex ..................... Age ........ ................................. Place of residence .................................. No. of dependants Profession ......................................... Qualifications No.
r
L
Photo
I
.....................................
.....................
issued
on ................
RECTO
Work periods End
Work details Date
Project
I Post
25.2
SEGOU reafforestation
17
No.
Checked Signature
II Date 12.4.
checked Signature
VERSO A weekly attendance bearing only his family special capabilities), worked for calculating this tally of the site, himself.
E.9) should be drawn up for each worker, name and address (with, where necessary, any checking off the number of hours and days Depending on the size pay (or related benefits in kind). foreman or works supervisor will be kept by a tallyman,
sheet (fig. name, given designed for
-
Fig.
128
-
E-9.
Site
............................................. Work attendance
Name ._.................................... Category ............................... Gang . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . Week
From From From From From From
..... ..... ..... .,... ..... .....
Worker's
to to to to to to
Personnel card No.
Wages/h
No. of rations per day
applied
The regulations
(lilt*ar;lsl?
Hours
Days
Cash
Kind
payroll
regulations
The provisions legislatior:.
-
Wage
Work done
designation
Weekly
working
Week's total
Work supervisor's initials
Worker Name
-
19..
..... ..... ..... ..... ..... .....
-
Site
Sun.
sat.
Fri.
Thurs.
signature
1 Registration No.
(b)
sheet
. . . . . . . . . . ..--------.-----..---.-...Hourly wage . . . . . . . . . . ..-_............. Month . . . . . . . . . . . . . . . . . . . . . ..--..
Wed.
Tues.
Mon.
. . . . . . . . . . . . ..-..---.--..
NO.
should
should
specify:
working
week;
iicu~~s; of
tile
be in
line
with
loca
customs
and current
Remarks
-
-
method
of
-
possible
payment; sanctions
(for
absence,
Regulations
may be established
(c)
remuneration
Worker
The level
129 -
of
remuneration
late in
should
arrival,
consultation
etc.). with
workers'
representatives.
be set
by the competent authorities Since these are community work. remuneration may be lower than
into account the specific nature of the ment programmes carried out by volunteers, minimum legal wage or paid in the form of
benefits
in
taking developthe
kind.
Payment should be carried out at regular intervals on a daily or weekly basis. The works supervsior should ensure that the necessary funds are available in order In the case of payment in kind (food rations, for to avoid delays in payment. care should be taken not to diverge from local tastes which might be a example), source
for (d)
discontent. Transport
To the extent when the however, to organise on the work (e)
their site
Worker
On small aimed primarily
and quartering efforts should be made to recruit manpower locally; possible, site is at a distance from the workers' homes, it is advisable or if necessary their quartering transport to the workplace, lodging, food and adequate sanitary facilities. by providing training
sites at
and on short-term work, worker training may be rudimentary the correct handling of the relevant tools.
and
In the case of larger and long-term sites, this training should be backed up by training aimed at providing workers with the knowledge necessary for them to take over responsibility for the correct operation and maintenance of the completed retraining of local craftsproject (introduction to modern agricultural techniques, and writing, etc.). men, reading (f)
Human relations,
conflicts
The works supervisor should ensure that volunteers are fully informed of the purpose of the work entrusted taking also be divided up into gangs, where necessary or community structures. the in special public works programmes, ticn usually leads to collective self-discipline. heterogeneous social groups (different ethnic period under artificial conditions may result The works supervisor of the project. To this and that a good community sanctioned accordingly.
should assert end, he must spirit exists
receive a warm welcome and Volunteers should to them. into account existing social
involvement of However, origins) living in conflicts.
the population the coexistence together
for
in
quesof
a limited
his authority and ensure correct progress ensure that the site regulations are observed Any infraction should be on the site.
-
(g)
they
Health,
safety
and working
130 -
conditions
Suitable working conditions will be laid will have an effect on work productivity
Sanitary distance from Safety
facilities should be related the workers' homes.
and health
requirements
should
to
down by practice and continuity. the
size
be applied.
of
and legislation;
the For
it is cuttings, trenches and ditches, banks which are higher than 1.20 m;
-
for excavations, stability of any
-
for work carried out in water, it is necessary to ensure and harmless and avoid risks of drowning and cave-ins.
site
and
the
example: necessary
Every isolated site employing more than ten workers should medical kit for first aid which may be carried out by a volunteer prior training or by the works supervisor himself.
that
to
the
ensure
water
1.4.3.
Incentive In
employing more than to provide a small 250 workers.
clean
have an emergency who has received
In the case of work sites employing more than 50 workers, there should nurse or health worker who can provide first aid and treat common diseases (malaria, headaches, dysentery). In the case of sites 12 months, it is necessary permanent nurse for every
is
the
be a
500 workers or work lasting more than mobile dispensary with a bed and a
system
all
firms employing workers, incentives are desirable to encourage better results. Recompense is therefore given for good results obtained either individually or by the gang as a whole. Praise or rewards may be made and additional holidays given. However, such procedures may prove unsuccessful especially in the case of It will therefore often be necessary to turn to: short-term work. -
the
-
piecework (a)
flnish-and-go
system,
payment.
The finish-and-go
system
This system is particularly attractive to workers, such as small farmers, agricultural workers, etc., who see the special public works programme as a supplement to their main job - agriculture. The interest for them is to finish their woric early and return home so that they can possibly spend the rest of the day on this main job. The system also suits agricultural workers who are not usually accustomed to regular working hours. It
is possible to determine a task which lasts for several days, although this is not usually desirable, nor always permitted by legislation. There is a danger that this practice may lead to five daily attendance cards being given for three days' actual work and this is clearly open to abuse. Usually, preference is given to daily tasks; since the result is extra work for skilled workers, the tasks are essentially simple ones, such as for example, digging a certain length of trench of uniform cross-section.
-
(b)
Piecework
131 -
systems
Where local legislation permits, piecework systems offer numerous advantages, in particular where a standard wage rate is fixed for each task and the worker (or gang) receives a fixed amount for each unit of work carried out. The advantages and disadvantages of these systems are as follows: Advantages
Disadvantages
the worker is able to earn more than the normal daily wage in return for higher output;
in attempting to achieve higher the worker may neglect quality safety;
his output will be higher since his wage depends directly on the effort he puts into his work;
if the rates are too low, the incentive to work hard may be lost, or the worker may work too hard to the detriment of his health;
these systems promote discipline and require vision;
individual less super-
the worker himself attempts to improve the efficiency of his working method;
output, and
differences in earnings between harder workers and less hard workers may sometimes cause resentment; these systems are more complex to apply than a daily wage or a finish-and-go system.
when, ir.stead of an individual, it is a gang which is doing piecework, the gang will organise itself to ensure maximum effectiveness and the most active members will encourage the others to work harder; in certain cases, where the situation allows, the workers will be able to stipulate their own working hours. 1.4.4.
Role of
project
management
The project management The main tasks are: -
work programming;
-
work implementation;
-
supervision
is
responsible
for
the
correct
implementation
of planning.
and control.
Work programming requires an over-all long-term view of the project and should Carrying out the work requires be the responsibility of the project manager. daily supervision which will be the responsibility of the works supervisor. Responsibilities -
of
project
manager
programming budgeting and budget control forecasting recruitment of assistants training - research public relations selection of main items of equipment wage negotiations project control
Responsibilities -
of works
supervisor
implementation of work quality and productivity control recruitment and payment of workers purchasing of materials discipline transport and organisation of manpower supervision of equipment and plant maintenance of buildings and roads
-
TOPOGRAPHICAL STUDIES
E.2. Topographical projects on hilly
'132 -
studies may prove necessary in numerous ground or which cover a large area.
cases,
It is diffjdult, within the framework of this document, methodology and the type of topographical studies that should projects within a characteristics of the soil conservation We will therefore not do programme may vary considerably. general principles for topographical studies and invite the numerous specialised documents in this :ield. 2.1.
Topographical A survey
(a)
the
(b)
survey
which
survey
in
picks
out
the
altitude
which
the
various
natural
to
refer
features
of
these
natural
to
of
features
carried
out
by the
measurement
of
the
the
is
distances
and angles.
measurements
-
the
-
the measuring rod in wood or metal of 4-5 m in length fitted level for checking horizontals and a plumb line for measuring distances on slopes greater than 2 or 3 per cent;
-
a folding
I Angie
chain
surveyor’s
2-m rule
(20 m in
for
length);
measuring
the
details
of
the
with a spirit horizontal
structure.
measurements the most commonly used being goniometers, plates one of which is graduated to permit
1
reader
survey
The planime%ric survey is The instruments required are:
I
to specify precise be foreseen since the special public works more than indicate certain
or a structure;
Planimetric
Distance
for
comprises:
the levelling measured.
2.1.1.
particular
survey
planimetric
terrain
in
-
surveyor's each other;
squares
-
optical
-
a type of goniograph plane table, relative position of a number of
-
compasses azimuths.
square
which
for
locating replaces
points the
the theodolite; the measurement
and features
surveyor's with which points;
these comprise of angles;
at an angle
of
45 '
two to
square; it
is
possible
to
measure
the
I
I
with
which
it
is
possible
to measure
differences
between
magnetic
2.1.2.
Levelling Two procedures
-
direct
-
indirect Direct
are
levelling
usually for
levelling levelling
horizontal for
is
used: sites;
inclined
carried
sites. out
using
a level
and a levelling
staff.
Since the level can be used only for horizontal sights, it is to carry out a series of levelling sights. steeply sloping ground, in fig. E-10. called change-point levelling, is il lustrated Fig.
necessary on This procedure,
E.lO.
the difference in level between two points is calculated In indirect levelling, by measuring the angle formed between a straight line linking these two points and This method requires the the horizontal, and the distance between the two points. use of theodolites or clinometers. The latter are particularly well suited to rapid reconnaissance l/l,OOOth. The indirect Fig.
E.11.
surveys
leveling
and allow
method
gradients
is
to be measured
illustrated
in
fig.
with
E.ll
a precision
below.
of around
-
2.1.3.
Composition and survey
of a topographic standards
The composition and difficulties -
topographic
-
one or two staff
-
two chain
-
two labourers,
is
the
terrain.
-
team
survey team will vary A basio team will usually
depending comprise:
on the
different
surveying
slope
surveyor; men;
men; to
The density scales
survey
of a topographic of
134
of
carry
levelling
the
levelling
points
stakes.
generally
accepted
for
as follows: Surveying l/10
No. of
scale
points
per
ha
1
000th
l/5
000th
2
l/2
000th
6-10
l/l
000th
15-30
l/500
levelling
th
20-100
E.3.
MARKING AND STAKING OUT THE STRUCTURE
Marking out a structure consists in indicating the axes and the external dimensions on the ground. This is done by means of stakes which should be precisely The marking out operations should located in relation to fixed reference points. be carried out in the presence of the project manager and the works supervisor. 3.1.
Preparation
of
the
ground
plan
The structure should be depicted by a ground plan and by elevations sections. The ground plan is drawn up by indicating on a tracing paper axes and the measurement of angles and altitude. 3.2.
Preparation
on the
and the main
ground
The transverse or longitudinal axis of the structure should be indicated by two fixed reference points which would be either boundary stones set in concrete or concrete boundary posts in which a nail is set in the upper part to act as a reference point. The number and altitude of the reference point should be marked on the boundary stone. The fixed
reference
points should be located outside work and should be sufficiently visible not to be damaged work. They should remain in place throughout the duration co-ordinates and altitude are usually incorporated in the of the area.
the external limits of the during the course of the of the work and their general levelling survey
-
Main
3.2.1.
staking
This
is
-
for
works
-
for
earthworks:
the
location
Staking
used
out
define:
engineering the of is
level
of
the
route,
the
axes;
the
longitudinal
profile,
the
curves,
cross-sections.
carried
out using hard-wood, square or circular cross-section the stakes should be driven home with a In loose soil, land, they should be cemented into holes made with a jumper
The stake heads should be painted to ensure that they are stake should be numbered and referred in plan and altitude
reference
above
construction: axis
the
stakes, 50 cm in length. on rocky sledgehammer; bar. each
-
out to
of
135
clearly to the
visible, fixed
and
points.
The stake head should be set at the exact measurement of the if this is not more than 30 cm higher or lower, or an exact
future number
ground of decimals
or below. Additional
3.2.2.
staking .
This is carried out from the main stakes and indicates the boundaries of These stakes are not levelled such as the edges of trenches or banks. works, they should be painted in a different colour to that of the main stakes. Staking
3.2.3.
the and
report
This document should be drawn up in should indicate the number of the profiles, reference points.
the
presence of the and the position
works supervisor and altitude of
who the
Example: No. of
Part of structure
stakes
Position
of
stakes Slopes and sections
Alignments and curves
Distance between stakes
I 3.2.4.
Displaced Before
the
Height of earthworks
Comments
I stakes work
is
started,
the
main
stakes
which
covered by the works should be displaced at a constant of the structure. This displaced staking should also axis stakes as shown in fig. E.12 below:
are
located
within
the
area
distance outside the boundary be levelled in relation to the
-
Fig.
136 -
E.12.
L-
Axis
Personnel
3.3.
requirements
The personnel
and work
required
for
the
output
marking
the basic topographical survey team as listed team should have an output of 4-6 km per day. Material
required
-
a level
for
-
a goniometer
-
two levelling
-
a surveyor's
-
stakes;
-
cement,
-
paint
marking
determining for
out
Clearing covered
should
comprise,
be provided by ground, such a
as a minimum:
altitudes;
the
marking
out
chain
water
marking
(or
steel
proper;
for the
tape);
the
installation
of
the
main
fixed
reference
points;
stakes.
E.4. 4.1.
work
out will On normal
above.
staffs;
sand, for
for
anti staking
the land over by the works
the
GROUND PREPARATION
area
In soil conservation projects, land clearance will be limited to preparing areas of work such as channels, embankments and earth dams with a supplementary for the movement of workers and plant. Land clearing consists in progress of the works or might
eliminating any vegetation lead to their deterioration.
For manual work, the tools used will vary considerably country. The main types are the machette, hatchet, axe, saw, scythe, sickle and hand winch. Output norms are related primarily to the density of types may be classified into various prolips. For manual gories can be distinguished as shtiwn in fig. E-13.
which
would
depending hoe,
fork,
hinder
the margin
the
on the pick,
the vegetation. clearing work,
pruning
Land five
cate-
-
Fig.
137 -
E.13.
Category
Characteristics
higher than sparse shrubs
Manual output
Observations
Between 200 and 300 m2 per day/man
Output depends on climate and site organisation
--
Grass Savannah
No vegetation 1 m; a few
Shrub Savannah
Scattered bushes; thorny vegetation; land covered with perennial grasses; numerous shrubs
between 100 and 200 m2 per day/man
An alternative a chain pulled two tractors
Wooded Savannah
Semi-arid tropical dense vegetation; brush; numerous thickly wooded; large trees
Between 50 and 100 m2 per day/man
Tree stumps and trunks and brush are left in place; they are burnt on site 3 weeks after having been felled
Forest
Hard and soft wood; large diameter trees forming a vault
Unusual work within the framework of soil conservation
Six men and a winch 10 trees fell about animal haulage day; might be envisaged
regions; thorny shrubs; some
;
projects
4.2.
in
Stripping
is to use between
can per
'
- subsoiling
The stripping areas which are
operation entails to be filled.
the removal of Normal trenching
topsoil methods
over a depth are used.
of
20-30
Subsoiling is a deep scarification (up to 60 cm) intended to increase soil permeability or break up a hard pan. It is used in arid zones to prepare the prior to reafforestation work. It requires powerful mechanical plant (tractors 35-70 hp for subsoiling to a depth of 60 cm).
area
Instead of subsoiling the to be covered with ridges
soil may also be loosened with a pick in which trees are to be planted.
The following productivity data for light stripping in the Philippines. The soil is loosened by a plough and the stumps removed by hand.
-
Soil
Non-cohesive soil; fields of and burnt, and in which there roots per square metre
Method
Four successive ploughings; ing roots by three passes handpicking
with
axe
under
and subsoiling were before being shovelled
cm
soil of
the
collected clear
sugar cane which have been cut remains two or three stumps or followed by removal of the remaina bamboo scraper and three times
-
2 ploughs,
Gang composition:
-
2 labourers
1 scraper,
165 m2 per
Over-all:
Productivity
138
hour
handpicking
per gang
Per operation: first ploughing: subsequent II bamboo scraper: handpicking:
r
General comments and handling
EXECUTION OF EARTHWORKS type
Land classification
5.1.1.
The type
of
-
the
working
-
the
choice
-
output
cuts
on soil
land method
determine: to
be used;
of equipment
to be used;
consequently,
and,
Soil type and fills.
will
the
has a considerable A distinction
-
loose
soil
-
rocky
soils
which
Loose
soils
may b,e classified
Light
which
Heavy
soil
Very
heavy
soil
Rocky
ground
Very 5.1.2.
topsoil,
hard
rock
without
and the
previous
shape
to be given
to
loosening;
topsoil, sand,
as follows: dry
sand,
fine
gravel
firm soil mixed with sand, wet sand, compact compact clayey fine gravel, large gravel, peat
Firm soil mixed with stones, clay gravel, clay, marl, broken rubble
soil,
Wet clay, compact marl, brittle slate, faulted
rubble, soft quarry decomposed rock
Soft
Hard rock
earthworks.
effect on trenches may be made between:
may be classified
rock
of
may be loosened.
Moist clayey
soil
cost
may be excavated
Dry
soils
Ordinary
Soft
plough plough scraper
q
E.5. 5.1.
250 m2 per hour per 490 m2 per hour per 490 2 per hour per 250 m2 per labourer
:
limestone,
consistent limestone,
compact
clay,
large stone,
as follows: chalk,
sandstone,
Granite
and gneiss,
hard
Granite
and compact
gneiss,
compact
slate,
congolomerates
limestone quartzite,
syenite,
basalt
Bank gradients
The slope of a bank should always be less than the angle of repose that would It is defined by the be formed in a bank abandoned to the action of weathering. base and i the angle of the ratio H tgi where H is the height of the bank, B its B bank to the horizontal. q
Fig.
E.14.
Banks cut ground
Type of soil
Dry Hard rock Soft or fractured rock Rock debris, scree, pebbles Subsoil mixed with stones and topsoil Clayey soil, clay, marl Gravel, non-clayey coarse sand Non-clayey fine sand Bulking
5.1.3.
Soil, three
are -
in
land
natural
Banks Filled
Waterlogged
land
cut in banks
dumped soil
Dry land
Waterlogged
5/l
5/I
l/l
l/l
312
312
l/l
l/l
l/l
4/s
Ill
415
I/l
l/2
213
l/2
415
II3
2/3
l/3
213
l/2
213
l/3
l/2
l/3
II2
l/3
- consolidation
when extracted, types:
the coefficient been extracted:
increases
of
initial
of
persistent
in
bulking
volume.
F which
This
is
is
measured
called
bulking.
when the
There
soil
has just
F = K+ -
the
coefficient
land
bulking
F' wnich
is
measured
after
consolidation:
-
-
the coefficient of soil which of newly
Fig.
of consolidation has consolidated
extracted
140 -
which is completely
the decrease in relation
in the apparent volume to the initial volume
soil:
E.16.
Walked soil before consolidation
Soil
Fig.
Values
E.17:
Type
of
coefficients
of
bulking
after
and consolidation
Coefficient consolidation
of soil j ffiz;y';"
~rsistant
I F
I F 10-15
%
l-l.5
x
8-l.?
%
15-20
'$I
1.5-2
%
12-15
%
'-Heavy soil mixed with sand Clayey soil Clay Marl Very compact clay and marl Scree Hard core tine)
20-25
%
2-4
%
15-17
%
25-30
%
4-6
%
17-19
%
30-35
%
6-7
$
19-21
%
35-40
%
7-8
%
21-23
%
40-65
%
8-15
%
23-30
%
30-40
%
8-15
%
17-18
%
40-65
%
25-40
%
IO-IS
%
out
sand
Knowledge earthworks.
bulked vo=
of
coefficients
To produce a fill volume (before v 1 + F.
of
with a final consolidation)
bulking
and consolidation
is
important
volume V', it is necessary to of V VI and excavate an in l+T q
of
soi
T
Gravel
Topsoil,
consolidation
in
carrying
place a provisional situ volume of
Tools
5.2.
The tools mechanical
used
manual
earth
moving
are
either
hand
tools
or
portable
tools. Trenching
5.2.1.
for
The main
tools
manual
tools
are:
This is made of steel and has a point at one end and a blade The pickaxe. the wooden shaft is about 1 m in length. at the other; The point blunts rapidly when used in hard soil; it can be repaired by welding on a new spike. A smith and his mate can repair 30-40 pickaxes per day. It is necessary to expect that about 20 per cent of the stock of pickaxes will be in fcr repair. The pick.
This
The wedge. break fissured
a pickaxe
with
made of
steel
This is rock. A steel
The crowbar. Portable
is
mechanical
lever
tools
Pneumatic spades which have an output of 5-10
from
a small
mobile
m in
1.20
Tools
5.2.2.
for
loading
For loading -
the
are used in times higher
which
a steel blade A shovel load loaded -
5.2.3.
end for
use
in
soft
with
a 2 kg sledgehammer
used
to break
fissured
rock. to rock.
heavy than break pick,
soil the soft
of compact clay hand pickaxe. or
wedge
fissured
rock.
and crowbar
and receive
their
or marl.
which
compressed
They
They have an they replace. air
supply
compressor. earth
excavated
shovel
length
each
include:
by one man alone
motor
at
and struck
Pneumatic picks which are used to output 5-10 times higher than the They can be handled
a point
earth,
use
can be used
weighing usually
1.0-1.5 weighs
is
made of:
for
excavating very loose earth. It is made of kg fixed to a wooden shaft 1.20 m in length. 2.5-3 kg; lumps weighing more than 5 kg are
by hand;
the --fork by size. Tools
which
for
has teeth
soil
Depending on the means are employed: -
wicker
-
hoppers
-
2-man
-
40-60-litre
3-4
and is
used
to grade
stoney
materials
haulage country,
local
baskets; carried
cm apart
on the
bamboo stretchers; wheelbarrows.
back;
resources
and haulage
distances,
the
following
-
For
larger
equipment -
is
pack
capacities used,
saddle
and haulage
such with
142
-
distances
a capacity
loo-150
of:
120-150
and
cart
l,OOO-1,200
-
sledge
with
-
shaft,
piece
Example
of
kg for
a pair of
100 m),
animal-drawn
of
side
an ox, a mule, a donkey, a camel;
400 kg for
of:
an ox,
donkey
of
2 m2 and 2,000 which
the
kg for
animals
are
it may be necessary not available, motor barrows, dumpers, etc.
is
equipment:
or horse,
oxen;
400 kg for
wood to each
haulage
haulage of
a capacity
a capacity
Where animal mechanical
with
for kg for kg for kg for
kg
60-100
single-axle
than
as: TO-120
-
(greater
7 m2; harnessed. to use
light
productivity HAULAGE AND UNLOADING OF HOMOGENEOUS LOOSE MATERIALS (by ox cart)
4
On level
ground
cework d
on 0
iO0
200
Distance The upper curve vision, with payment under poor supervision, Mean cart 5.2.4.
Tools
capacity: for
soil
300
in
400
500
metres
shows the outputs attainable with good organisation by piecework. The lower curve shows the outputs with daily rated payment. 0.315
and superattained
m3.
compacting
The simplest soil compacting tools are hand tampers maniptilated by a single worker and pneumatic tampers also operated by a single worker and supplied with compressed air by a small motor compressor. 5.3.
Manpower
Earth moving is ideal for the employment of large and meets perfectly the objectives of labour-intensive utilisation is a solution to the economic problems of
L
numbers of unskilled workers work in which manpower a developing country.
- 143 -
there are However, and the factors affecting
conditions
and limits
working
conditions
for
climate;
-
workers'
-
nutritional
-
local customs which govern periods of work, of certain types of work (work with feet in
-
skill
-
the
conditions
-
the
way in
manpower
in
this
way,
include:
health; status;
in
the
of certain
use
under which
workers
LOADING,
grading
is or
project
buffalo-drawn
soil.
pil,:s
(e.g.
soil tipped in small piles (e.g. scraper maximum haulage capacity:
differences in and supervision.
output
that
can be
bamboo scraper)
The scraper by ploughing. Average output:
can also
by a buffalo
cart):
be used
5 m3/hour
by a dump truck):
25 m3/hour 0.05
m3
15 10 5 0 20
Distance
40
in
60
metres
curve shows the outputs that are obtainable with good organ isat ion The iower curve shows outputs attainwith payment by piecework. supervision and daily rated payment.
The special
factors
-
age and condition
-
proximity
-
soil
-
slope
of
water
affecting of for
type; of
out;
20
0
The upper and supervision, able with poor
carried
being
illustrates the of organisation
loose
large
cl s a ff; .5 m c +.A 2% 3 u 803 a
is
paid.
loosened
spreading in
inacceptability
HAULAGE AND UNLOADING HOMOGENEOUSLOOSE SOIL
previously
tipped
the are
(using The soil
job distribution, water, etc.);
tools;
which
The example below clearly expected depending on the level
soil
use of
and output
-
fcr
the
haulage
route.
buffalo; buffalo;
productivity
include:
- '144 -
Labour
5.4.
organisation
A manual earth-moving water labourers, leaders, and a watchman of
for
the
There is the work.
usually
The basic
gang
-
either
-
or two men:
-
or three
site comprises: carriers where
supervisor,
necessary,
four
a topography
men or gang
team,
a tallyman
equipment. one gang
leader
for
every
20-25
men depending
on the
difficulty
comprises:
one man with
a pickaxe
one with
and shovel;
a pickaxe
men,
with two and two shovels
pickaxe
a site
and the
other
pickaxes and a shovel in softer ground.
with for
a shovel; very
hard
ground,
or one
on the means employed. The way in which manpcn pr is used may vary depending Either the earth moving can oe done entirely by manpower or by manpower in combinaThe type of soil tion with local resources such as animals or mechanical plant. Where the and haulage distances will often decide the solution to be employed. it may be better to excavate and load by hand and haul haulage distances are la?ge, and ripping Certain work cannot be done by hand, such as subsoiling mechanically. manpower
is
a back-up
here.
certain earth-moving Finally, applies to ditching and banking in Earth-moving
5.5. 5.5.1.
Trench
methods digging
jobs
are
suitable
for
piecework
payment;
this
particular.
and outputs
and spoil
removal
trenches may be dug directly with a shovel; In very loose ground, in ground, the soil is first loosened and then removed with a shovel; pickaxes, wedges or crowbars may be required.
in harder hard ground,
The work may advance along the axis of the trench using two or three workers: the first loosens the soil with a pickaxe while the second (and third) follow and This is the procedure usually used for shovel out the s%oil or deepen the trench. narrow trenches.
to Fig.
For wider trenches, the trench axis. E-18.
the
workers
may be arranged
in
a line
and work
perpendicular
- 145 -
Trench
digging
methods
Fig.
E.19:
Terrace
construction
Fig.
E-20:
Construction
Deep trenches
are
of
should
shown
in
a protection
the
diagrams
below:
ditch
be dug as follows:
Construction ditch with downhill
Output in earthworks and trench size. Soil other
such
Cohesion pickaxe
is
and adherence
as soil
the
considerably
water
measure
content
of
soil
depending
are
on soil
the
main
factors
may also
play
a role.
hardness
and directly
characteristics
influencing
affects
the
output;
output
of
the
man.
Density Soil Worker sufficiently way. Under follows:
density
cohesion,
factors
varies
of a protection spoil thrown
affects adherence
the
shoveller's
to the
tools
output. affec'ts
the
output
of both
pickaxe
and shovel
men.
Workers should be deployment also has a great effect on output. spread out (about 2 m apart) so that they do not get in each other's
optimal
conditions,
maximal
output
of
workers
using
hand
tools
is
as
- 146 -
Fig.
E.21:
Output
in
manual
IType
of soil
earthworks Daily
I
3.5-5.0 2.5-3.5 l-O-2.5
.In 'ihe case of narrow ditches, about 20 per cent if the trench is Some common outputs in fig. E.22.
Fig.
E-22:
Common values
and the
for
(m3/md;l
5.0-7.0
Light soil Ordinary soil Heavy soil Very heavy soil
shown
output
workers are hindered less than 1.20 m wide
breakdown
output
in
between
trench
digging
and output or over
lowered
by
2 m deep.
and spoil
removal
are
digging -
Soil
type
Topsoil etc.)
(loam,
Cubic metres excavated and thrown 1 m in an a-hour day
Breakdown
of
8-hour
Excavation (hours)
Spoil removal pitching or loading (hours)
3.0
5.0
3.0
2.0
5.3
2.7
1.5
5.7
2.3
1.5
5.6
2.4
1 .o
53
2.2
sand,
or clay soil, moderately compact Hard, compact soil Chalky soil Marly
Waterlogged
soil
Moderately hard laterite Very hard laterite Soft rock worked with pick or wedge
1.0
6.7
0.8
7.0
0.6
7.0
1.3 :
1.0 1.0
day
-
FIR.
Maximum
E.23:
Type
shovelling
output
Hourly
of operation
shovel throw a wheelbarrow
Loading Loading Loading
a truck a cl^rt a lorry Spoil
5.5.3.
in
loading
output
Light
Simple Loading
147 -
in
soil
or
picking
m3 of
bulked
up soil
soil
Ordinary soil
Heavy
soil
1.5-1.0
1.0-0.8
0.8-0.6
2.5-2.0
2.0-l-5
1.5-1.0
l-O-O.8
2.0-l-5
1.5-l-O
1.0-0.8
0.6-0.4
l-5-1.0
1.0-0.8
0.8-O-6
0.6-0.4
1.0-0.8
0.8-0.6
0.6-0.4
0.4-0.3
Very soil
heavy
0.6-0.4
haulage
The main
means of
haulage
are
shown
in
section
4.2.
The simplest means are usually used for haulage distances of less than 100 A wheelThe wheelbarrow is the most common and has a capacity of 40-60 litres. barrow pusher can complete a return journey of 30 m in each direction whilst a shoveller is filling a 50-litre barrow. Animals or mechanical equipment Animal haulage requires flat ground empty return being uphill. The theoretical
output
for
are used for or the haulage
transport
haulage should
equipment
is
q
.
of more than 100 m, be downhill with the
given
by the
formula:
1 cu x v Rt = 2 in
which:
Fig. Fig.
E.24:
Cu is V is
the the
E-24 gives Theoretical
payload haulage examples
capacity speed in of
output
Equipment
theoretical
of
cc
various
outputs. types
0.075
of
haulage
equipment
Remarks
RI = 1 CuxV 'z
(t)
(a) Wheelbarrow, 50 1 Cart - 1 horse, 750 1 Cart - 2 horses, 1 500 1 Motor barrow, 300 1 Small dumper, 350 1 Small dumper, 600 1
km/h.
Small
haulage
equipment 0.12
1.125
1.7
2.250
3.4
0.450
1.12
0.525
1.3
0.900
2.7
1
3 wheels, 4 wheels, 4 wheels,
3 hp 4 hp 8 hp
-
of
Wheelbarrow O-5 per cent
Fig.
148 -
Output and gang haulage: (good haulage track).
composition
for
natural
gradients
E-25. Volume
of
No.
material
of workers
(m3)
Haulage
Spreading
2.0
1.0
1.0
13.5
1.5
1 .o
1.0
8.5
10.5
1.0
1 .o
1.0
6.5
8.0
1 .o
1.0
0.5
5.5
7.0
0.5
1.0
0.5
In situ
Bulked
Loading
13.5
17.0
10.5
A buffalo-drawn steel scraper unloading of homogeneous loose soil
of
1
gives good results for for haulage distances
The diagram below shows mean outputs 0.075 m3 on flat ground.
for
the
Compaction
loading, haulage of up to 100 m.
scraper
which
has
and
a mean capacity
25 20
Output in m3 for an a-hour day
15 10
Distances 0
5.5.4.
Unloading,
spreading
in
q etres
5 40
20
60
80
100 m
and compacting
manual spreading can be carried out at a rate of 2-4 m3/h/man. After unloading, The work varies however depending on whether the spoil is normal or compacted. Normal spoil is usually encountered in the type of soil conservation work described here, with the exception of fill for dams. Ordinary spoil vegetable debris. being compacted.
should be cleaned of mud, running It should be tipped over the total
soil, peat, sods, stumps and height of the dump, without
Compacted soil should be prepared in the same way, then evened out in Since horizontal layers 15-25 cm thick over the total height of the platform. compacting is often inadequate on the edges of banks, the structure may be 20-40 m oversized on each side. Each layer should be dampened and then carefully compacted with hand tampers or drawn rollers to the specifications laid down. Before each new layer is spread, the base should be scarified, then dampened. The gradient of the bank slope r,houid be checked using a jig fitted with a spirit level. Output for manual compacting higher using a drawn roller.
is
1.2-i-5
m3/h
using
hand
tampers
and
IO-15
times
- 149 -
Bank grading
5.5.5.
The definitive every
Workers gradient
I
5.6.
is
is
trimmed
are
given
to
of
the
bank
by cuts
made with
a pickaxe
about
mark and stake
out
existing
excavate
a trench
(e)
dig
(f)
stretch pickaxe;
a line
(g)
roughly
dig
(h)
give
a trench
levels
check
the
bottom. at
between
intervals
two
of
about
The
1.5 m.
cuts.
or ditch
stakes
with
vertical with
between
these
shape with
the
the
30 cm wide
out
the
as follows:
width
and,
sides the
and mark out
level; with
to
planned
banks;
a spirit
of the
using
banks;
to the
cross-section
are
canal; stake
soil,
(d)
check
to line
a line
involved the
between
final
a horizontal
of a canal operations
a line trench;
top
earthworks
The various
run the
along
from
by stretching
Construction
on the
working
placed
checked
Examples
5.6.1.
(b)
is
10 m.
The slope
I
gradient
a jig.
ditch;
a pickaxe, the
mark the
finished
depth
shape
of
the
the
edges
of
ditch, the
boundaries of
of
the
ditch;
every
5 m;
ditch
with
a
- 150 -
Fig.
E.26:
Ditch
digging
techniz
Staking out the final dimensions of ditch Phase
/
1:
Staking out the final width and vertical excavation down to specified depth
Phase 2:
Excavation of a trench to final width of the ditch
Phase 3:
Shaping
Phase
Checking the section with spirit level
4:
crossa
Construction
5.6.2.
The various set
of operations mark
up site,
construction strip
dam, additional
a coffer
dam for
from
foundations
in
insta
as follows: reconnaissance;
temporarily
diverting
the
water
course;
basin;
foundation
are: a; ground
and emptying
filtration
11 foot
from
to natural
take-off
bring
are
zone;
topsoil
install
involved
and trees
borrow
remove
fill
of
dams
out
vegetation
prepare
earth
level;
pipe ;
materials;
drains;
fill; civil
engineering
work
for
take-off
civil
engineering
work
for
flood
cover
banks;
install
hydraulic
finishing
work.
Reafforestation principle working
6.1.
Nursery This
escape;
equipment;
E-6.
the
and feedback;
IMPLEMENTATION
techniques methods
have been and outputs.
OF REAFFORESTATION WORK described
in
Chapter
B.
Given
below
are
work
comprises:
-
nursery
construction;
-
seedbed
construction;
-
sowing
-
pricking
-
watering;
-
plant
in
seedbeds, out
into
plant plant
beds beds
or
or
pots;
POtSi
transport.
The tools lines, stakes,
used are: hoes, pickaxes, watering cans, secateurs,
spades, shovels, rakes, spirit polyethylene sachets, etc.
levels,
Work times depend mainly on Nursery work requires large amounts of manpower. A basis can be the type of plants being grown and the type of care being given. for various plant spacings, gives the following taken 0.3-0.6 hours per plant which, work times:
- 152 -
Plant
spacing
No. of
(m)
Work times
plants/ha
Minimum
Maximum days/ha
days/ha
3.0
x 3.0
1 100
47
94
2.5
x 2.5
1 600
68
136
2.0
x 2.5
2 000
86
172
2.0
x 2.0
2 500
107
214
1.5
x 2.0
3 300
141
282
1.5
x 1.5
4 400
188
376
Planting
6.2.
Preparatory preparation.
work
includes
marking
The tools used for planting pickaxes, hoes, lines.
are
out,
the
staking
out,
same as those
clearing
used
in
and soil
trenching,
i.e.
shovels,
The basic gang comprises two workers: second transports the young plants in pots, holes and completes the planting operation. may do the whole operation himself. The workers advance in leader being slightly ahead of materials. Planting
should
A foreman should to ensure that from the tip.
be sufficiently
first
digs
the
planting
hole,
the
sacks or baskets, places them in the In certain cases, a single worker
straight or diagonal Other workers ensure
the line; a constant
gang supply
and deep to take the whole root Roots should not be bent system without crushing the roots against each other. and should be fully covered with earth. To in towards the centre of the hole, hold it at the earth mark whilst ensure the pl.ant is covered to the right depth, Soil should be placed around the plant with care the hole is filled with soil. and trodden down when the hole is half full and then trodden down once again when the hole is completely full.
plants pulled
holes
a more or less of the rest.
the
wide
follow up the line of planters they are vertical and do not
to check a proportion come out of the ground
of the when
Under the best working conditions, when using hand tools, gangs c?.n plant 100-500 trees in an R-hour working day. This level of output will vary depending density of vegetatioil cover, type of on the diffic:Alties of the site (topogra;:,y, scil, soil preparation, etc.). 6.3.
Construction This
comprises
of
forest
basically
tracks earth-moving
According to the FED productivity requires 7.6 hours of work per cubic
work.
norms in Rwanda, forest metre of earth moved.
track
construction
- 153 -
6.4.
Plantation
maintenance
Plantation maintenance years (replacement of plants regularly thereafter. Maximum output Clearing
for
around
requirements are considerable that do not take, weeding)
weeding
young
is
200-300
plants
requires
maintenance In Mohanda (Burundi), callitris plants/ha have been estimated days pel hectare per year. 6.5. Fig.
Planting
along
the first decrease
two
m2 per man-day. a man-day
for
requirements for at 0.3 h/plant,
200 plants. a plantation of 3,000 i.e. 128 T-hour working
planting
Examples of a plantation: Song contour lines E.27:
during and then
contour
lines_
#-B -w---c,
-7zg-z
L.ine of stakes With an interval d between plants, a line to the slope and spaced at d from each other. in
A first length.
row of trees
is
planted
along
the
of stakes contour
is line
inserted using
however, Subsequent rows are planted in a similar manner; between the trees is less than 0.8 d, a new row is started. When the inserted until
distance between rows is 1.6 d or more. an additional the spaoe between the rows falls to 0.8 d.
perpendicular a spirit
when the
level
d
distance
row should
be
Planting in an arid Arrangement designed concentrate surface
zone. to run-off
Productivity
6.6.
norms
Manpower requirements in man-?ays/ha with a density covering nursery work, planting and maintenance: ranging in Burundi. Some typical -
filling
-
pricking
-
planting:
-
hole
-
holing:
outputs
sachets: out
digging
(Rwanda):
0.03
sachets: 100 plants
man-days
per plant;
0.01-0.02
man-days
per T-hour
and planting:
number of holes in rocky soil: in stony soil: in deep soil: care:
of 2,500 plants/ha, from 272 to 478 man-days
per
plant;
day;
300 plants
per man-day;
per man-day 24-30 30-45 40-50
-
plant
-
creating a windbreak by direct sowing: 24 man-days for 100 m comprising staking out, tilling, sowing, mulching, separation, three thinning outs, separation or natural regeneration followed by thinning out;
-
creating a windbreak by planting: rows and a spacing of 2 m.
200 per man-day,
i.e.
300-400
m2;
22 man-days
for
100 m for
plants
in three
-
IMPLEMENTATION
E-7. Installation
of
The collectors The drains
Fig.
which
marked
are
mark out
the
mark out distances
a line equal
mark out
a second
the
a drainage
are
first
155 -
network out
in
grouped
drain
OF DRAINAGE WORKS
the
in
in
parallel
relation
perpendicular to the drain
same way as the
to
to the spacing;
perpendicular
lines
line
can
fixed
ditches.
be marked
reference
first
drain,
which
is
out
as follows:
points;
and this
staked
out
is
in
staked
the
out
at
same way as
first;
trace a line between the points staked this line the specified drain length;
out
stake
stakes
out
E.28:
the
whole
Installation
drain of
network
a drain
with
on the
perpendiculars,
every
marking
on
30 m or so.
network
Perpendicular Stakes
indicating
drain
spacing
e--e -----
7.2.
Tracing
0.30
Drainage and 0.70
out
trench
width
trenches intended m at ground level
The trench A line marked with
total
is
marked
between the a pickaxe.
out
on the
pickets
The line is subsequently and a second groove is marked The line
itself
is
for laying of underdrains vary in and 0.06 and 0.20 m at the base.
marks
ground the
by a line trench
of
string
external
attached
at
stake. 7.3.
Calculating
trench
The mean depth The level
is
depth
and the obtained
minimal using
drain
a dumpy
gradient level.
are
between
pickets. along
axis;
moved sideways to the along this line.
a 30-m length
of
width
known.
this
limit
each
a groove
of
the
end to
is
trench
a wooden
- 156 -
A 20-cm wooden there
is
no rapid
A surveyor's
staff
The elevation The depth uniform
of
is
hammered
into
is each
placed
alongside
stake
is
approximately
every
50 m if
from
stake.
a single
then calculated depth is written
surveying
point.
whilst maintaining on each marker.
used may vary slightly depending used for manual trenching:
an ordinary
-
a fork
-
a draining spade which has a blade arranged in direct prolongation of are curved slightly inwards;
a relatively
garden
spade
and pickaxe
for
for
removing
excavating
the
country.
the
sod and the
top
layer
40-50
the
on the
cm in shaft.
of
In general,
topsoil
stony
the
layer;
soil;
length and lo-15 The long edges
cm in of the
width, blade
a scraper which is used to finish the trench bottom and produce the correct It is made from a piece of curved metal 30-35 cm in length, shaped slope. and sharpened at the end. The shaft is 2-3 m in length and is at 40-50 0 to the blade. Blade diameter should be matched to the diameter of the drainage pipe. It
Fig.
each
noted
-
uphill
level
digging
The tools following are
-
soil
in gradient.
of the trench is and the relevant
slope, Trench
7.4.
stake
change
is necessary to start digging so that any excess water will
E.29:
Longitudinal
Digging
a drainage
cross-section
the drain at the drain away as the
lowest point, work advances.
working
trench Strip
1st digger
topsoil
Soil
surface
_---me----
Second diaffer Swcified -
Plan
Spoil
view
Transverse
cross-section
bottom
---
from 2nd digger
Topsoil
Spoil
from 2nd digger
- 157 -
The first
digger
cuts
placed on the right of way for the pipe layer.
up the
the
sod and removes
the
trench about 30 cm from This topsoil is the first
This
tOPSoil.
the trench to be used
topsoil
is
edge leaving a pathwhen the trench is
backfilled. The trench is The spoil
then dug with a draining is thrown onto the left
50 cm.
spade to a depth of approximately bank of the trench.
The second digger works approximately 3 m behind the first digger. deepens the trench but to a smaller width and throws his spoil onto the He digs the trench an additional 50 cm approximately. of the trench. the trench is further deepened by a third digger i&o works in the sav, as the second. The trench for 7.5. are
the
obtained
in
this
way will
be slightly
than
that.
specified
drain. Trimming
the
trench
For this operation mounted adjustable
bottom
one uses rectangular
the scraper crosspieces
and wooden ("boning
The object here is to connect these points
to dig the trench to by a uniform gradient.
the
Using the drainage pipe.
the
smoothed
The trimming Fig.
shallower
He left bank 2f necessame way
E.30:
scraper,
process
Trimming
trench
is
a trench
shown
bottom
is
depth
diagrammatically
or steel rods"). marked
staffs
on the
and compacted
on which
markers
to
receive
below:
bottom
n
A
Specific
bottom
Measuring rod
and
the
- 158 -
At point
A marked
by a stake,
boning above
rod adjusted the bottom of
places a fixed the boning rod At point marker
B where
the depth hb above the
at a height
C, one places A, C and B.
line
At point between
drawn
To trim the trench at height H. The correct mark on the
the
On flat to have the assistants.
laying
The tools
the
trench
such
uses
the
that
it
scraper
a long-handled
-
a steel
pick
laying
tile
hook
to
are in
piles
pick
cutting
brought of
30-35
or
concrete
up the
pipe
or holing
to
form
on which
one of
a
a sight
a mark has
established
been
between
and it is preferable an operator and two
trench
earthenware
hammer for
The drainpipes placed trench.
for
one places
will
is reached when R sight line is and the crosspieces A and C.
the
is known, The height
ha above the ground. is equal to Pa + ha = H.
of a length
worker
and backfilling
used
-
They are from the
Pa of
Pb of the trench is also known, ground so that hb + Pb = H.
the
depth shaft
depth
to height the trench
a marker
depth,
the
ground, checking the gradient is more difficult work done by a topography survey team comprising
Drain
7.6.
trench scraper
where
the
site
pipes
pipes
and lay
the
pipes
on a trailer
every
are:
it
in
the
when being
trench
bottom;
laid.
or on stretchers.
10 m or so and at
a distance
of
3-4 m
The pipes are laid starting at the highest point. The pipe layer picks them up with the tile hook and places them on the trench bottom, striking them sharply several times on the edge with the iron hook to seat them together properly. When it pipes at
the
is necessary to turn the pipes an angle with the pick hammer.
When placing together drainpipes covered with earthenware crocks. Long drains sections on the
(6 m) are put trench bottom.
Long concertina-type
of
together
PVC drains
round
di_fferent
outside
machines
which
dig
the
trentih;
-
machines
which
dig
the
trench
backfilled alongside
first the
The trench is was laid separately out
by shovel
using
the
remainder
not
this
diameters,
the
and also
designed
ditch
is
the
done by cutting
joints
and then
laid
are
in
whole
manual laying and are In certain countries: laid directly on the trench bottom by drainage machines. They do not come these machines have almost entirely replaced manual labour. It should within the framework of this report on labour-intensive public works. merely be noted that there are two types: -
are
a curve,
lay
the
for
drainage
pipes.
by covering the drainpipe with trench. Subsequently, backfilling of
the
spoil
and then
lightly
topsoil which is carried
compacting.
-
Fig.
E.31:
Main
drainage
159 -
tools
II III I 3 Y-L -W
Footpiece
I4
Drainage
spade
Scraper
n IL
Tile
hook
-. I -===I II I T Pick
hammer
Small spade
drainage
-
Mrnpower A,.
'i -7.
and output
A drainage -
a skilled -
site site
in
manual
usually
work
supervisor
workers
and 4-8
whose
jobs
2-4 workers depenciing on the 1 worker; pipe transport: 1 worker; pipe unloading: 1 worker; pipe laying: 1 or 2 workers. backfilling the trench:
a good
(loose earth), trench per hour.
a gang comprising a site conditions, Output of only half drain per day.
types
divided
up as f'o
depth;
drainage
worker
can advance
supervisor and four this may nevert,;eless
diggers be con-
CONSTRUCTION OF MASONRY WORK
E.8. Different
are
tlanch
earthworks:
Under these can lay 250 m of sidered normal.
8.1.
drainage
comprises:
Under very good conditions m of ordinary 0.8 m depth
6-8
160 -
of masonry
work
The term masonry work covers all types of structures made from stone. for the construction of gully Masonry work is used in soil. conservation projects or ravine erosion protection work when the necessary materials are found in adequate quantity close to the site. One may distinguish
between
dry-stone
-
normal ceme,lt
masonry or lime
work in mortar;
which
the
gaps
-
gabion sage.
masonry
work
which
the
stones
Dry-stone
When they made of blocks
work
masonry
in
in
which
types
_
8.2.
masonry
three
stones
of are
masonry fitted
between
are
are subject to of a sufficient
the
held
without
stones
are
together
in
the action of water, dry-stone weight to resist the action on the
basis
of
current
Vmax = 0 .qpiyT--A which: Vmax is
the
maximum current
n
is
the
rock
l3
is
the
acceleration
Ps - P = density P
together
binder;
filled
with
a metal
mesh
work
Stone size may be calculated IZBASH's formula:
in
work:
speed
at
high
Water
(9.81
m/s21
diameter
of
of the
gravit.y
material
under
water.
of
facings should the current.
speed
using,
for
be
example,
-
161 -
the thickness of the dry-atone In principle, it When atones are placed on erodable material, stones and the bank a filter made up of a gravel Mean output
for
stone
breaking
Mean dimension breaking
facing is
I,40
11 mm
0,IO
the
dry-atone
-
shape
and compact
-
place their
the stones by laying them greatest length is in the
-
insertion of approximately
facings
is
least
30 cm.
between
the
thickness.
as follows: per
m3
30 mm
40 mm
constructing
cm in
IO-20
0,8Om3 0,75 a3 0,70 m3 0,55 m3
of
to place
mean output of 8 hours
Approx. man-day
after
45 mm
The method
be at
by hammer may be estimated
50 mm
m3 as follows:
bank; perpendicular thickness of
larger atones, called 20 cm into the bank,
Stones these voids
should be fitted together can be filled with atone
Fig.
Construction
E.32:
necessary bed of
mm
135
should
of a dry-stone
to the
the bank facing;
surface
which are anchored headers, at a distance of one every
with the fragments.
minimum
of
voids;
that
at a depth m2. if
faca
\20
30
cm
necessary,
of
- 162 -
The table below shows facing constructed manually
the number of at thicknesses
Man-hours
Material
Normal
per
20 cm
Brick Sandstone/limestone
0.55
0.60
0.60
0.65
Granite
0.65
0.75
masonry
that the immediate
stones, vicinity
in
thick
the required of the site.
sizes,
to
running
are
bound
together
with
cement
given below presuppose of the site.
that
Wall thickness in cm
mortar
when the
the
materials
cm in the specialised
20-40
is
structure
are
Mean thickness
of
15 cm
between
been
is
exposed
water.
The outputs immediate vicinity
It
have
work
The atone used for this type of work may be natural stone of largest plane or cut atone of various dimensions. Stone cutting wc:-k and cut stones are used only rarely. The stones
dry-atone
m2
15 cm thick
These figures presuppose supplied from a quarry in the 8.3.
m2 of
man-hours required per of 15 and 20 cm.
4.0
mh/m2
60
7 mhlm'
5.5
90
10 mh/m2
8.0
mhlm' mh/m2
mason and the
For a mortar-bonded -
manual
mixing
-
mortar
jointing
Approximate
of
the
time
per
square
metre
is
divided
take
into
labourer. it
wall, cement as the
quantity
required
or work
is lime
necessary
mortar:
advances:
of mortar
Thickness of wall in cm
also
1.0
to
man-hours
8.5
man-hours
per per
account: m3;
m2.
required:
Mean thickness 15 cm
30
0.07
60
13.00
90
20.00
the
30 cm
5 mh/m2
that
to
stones
30
can be taken the
brought
of
stones 30 cm
m3 m3 m3
0.05 10.00 15.00
m3 m3 m3
equally
- 163 -
350-400 kg of cement per cubic The cement content of a mortar is as fOl10W3: If the sand is very fine and made up of grains of less than metre of dry sand. 0.5 mm, the quantity of cement should increase by 20-25 per cent. The amount of mixing water (in litres) should be 25 per cent of-the weight of the cement plus 6 per cent of the weight of the sand, i.e. 220 litres of water of water for a mortar for mortar containing 350 kg of cement/m3 sand and 23g litres containing 450 kg cement/m3 sand. Mortar and plastic, not fracture.
is checked not stick
Constructing
The ball of mortar should be firm it by hand. of 20 cm, should and, when dropped from a height
by modelling to the akin
a mortar-bonded
wall
comprises
the
following
-
ccnstruction of concrete footings crete for small structures, steel
-
laying
-
settling filling
-
laying headers good bond with
-
cleaning
-
pointing; in which the joints are cleaned to a depth of 3 cm before the and then finishing them with a fine sand mortar with a cement mortar sets, content of 600 kg cement/m3 sand. Gabion
8.4.
stones
on a thick
layer
at the base of the reinforced concrete
operations:
of mortar
the bricks against each other the voids with atone fragments
the
40 cm long the bank; joints
masonry
(bed of mortar); by striking them with a hammer and without moving the larger atones;
at intervals
by removing
structure (ordinary confor larger structures);
of approximately
mortar
1 mc to ensure
a
runs;
work
Characteristics Gabions
are
boxes
made out
of metal
mesh filled
A distinction is made between: cage gabions and footing gabions (0.50 body work of structures; of foundations which may be subject to deformation. Fig.
E-33:
Common sizes
Footing
gabions
Width (m)
1 43 111 I 1 2
1
5 6
Cage gabions
(1
carefully
aligned
stones.
m high) used for the main m high) used for the body work
of gabions Length (m)
Type
with
1
1 '5 6
1 1
Height (ml 0.50
Weight
(mesh in kg
9.8
120-100)
0.50 0.50 0.50
18.2 14.0 22.4 26.6
1 1 1 1 1
14.0 19.6 25.2 30.8 36.4
- 164 -
Weir made from gabions
and dry-stone
The gabion walls are made of galvanised The most common mesh sizes hexagonal mesh. the size of the smallest filling of this size, and the weight of the atones around 5-10 kg. T'I ensure sides zre held
that the gabions do not together by steel wire.
Method of manufacturing mesh is
the wire
cut
(b)
the walls
(c)
the gabion
(d)
the edges are
bound
(e)
the bottom soil;
anchored
(f)
the
stone
(g)
fit
in the
(h)
continuation necessary:
(i)
closing adjanent
folded
is
located
is filling
The tools
in its
to the
wire
-
pliers;
-
jumper
-
wooden blocks
-
a sledgehammer
fig.
adjacent
E.34)
flat; are
tied
together;
position; gabion;
ground
using
steel
stakes
rammed into
the
trusses; whilst
and tying
adjusting the
upper
the
include:
stake;
to wedge the to drive
stones;
home the
jumper
internal
edges together
cutters;
bar or steel
when stacked,
commenced;
of filling
-
final
to the adjacent
internal
required
out
(cf.
in to form a box and the edges
is
the cover gabion.
shape
gabion
to shape and laid
(Cape Verde)
steel wire, with a double twist are 100 x 120 mm. When using mesh stones should be at least 160 mm, their
a stone-filled
(a)
are
lose
work
bar.
trusses with
those
as and when of the
- 165 -
Fig.
E-34:
Assembly
and installation
of wire
. .63 ..
mesh gabions
. . 6s,.
Fold walls to form a box open at the top
Wire mesh cut and laid out flat
Tie edges together
Detail truss
Fill
Using a jumper bar align the sides
with stones
Fill centre of gabion with small stones if not sufficient large stones
Trusses
Cabion 4xlxO.5D Plan
Plan .. .. .. .. l3IIl
m-1 Elevation
of a wire
Diagram of trusses
Trusses Gabion 4x1~1 Plan
Elevation
Gabion 0.5 m high used for footings
Gabion 2x1~1 Plan
Kiilg
m
Elevation
Elevation
Gabions I m high used for the main body of the structure on the footing or foundation
Tying the edge of the cover with adjacent gabions Tying the cover Unit weight
Gabions can be installed objectives of labour-intensive
using unskilled projects.
labour
and they
meet perfectly
the
-
166 -
Weir in stone
Front
view
Detail
masonry
-
Characteristics
of
concretes
Concrete is obtained by mixing and water which act as the binder. There
are
numerous
-
CARRYING OUT CONCRETE WORK
E.9. 9.1.
167
sand
categories
of
and gravel
(called
aggregates)
lean concrete aggregate;
with
a cement
content
of 250 kg cement
per
-
rich concrete of aggregate;
with
a cement
content
of
cement
-
normal concrete aggregate.
a cement
To obtain good quality to avoid the use of friable adhesion between aggregates. The choice
of
content
concrete, materials,
materials
plays
it
450-600 of
kg of
350 kg cement
cubic
per
per
metre cubic
cubic
Concrete A simple
mix
a 50 kg sack
-
two 70-l
-
a 70-l
-
20-30
an important
role
in
concrete
quality. dimensions where same
be sharp.
(by of
barrow barrow
volume)
and contain or sulphates
less than 2 g/l of dissolved which attack ordinary cement
should
of concrete
is
as follows:
load
of
of gravel; sand;
depending
normally
shovelled in first, followed then water is added. Mixing concrete. category
a batch
cement; loads
1 of water
for
on the
Another way of proportioning with a known capacity. A crate capacity of 0.1 m3.
Lower
of
preparation
-
Concrete
metre
is necessary to use suitable aggregates and reduce voids to the minim.um and ensure good
The water should be clear, odourless salts. Water containing organic matter should be avoided. 9.2.
of
metre
The aggregates should be correctly graded with components of various to minimise the size of voids. It is advisable to use well-known quarries the aggregates are always produced using the same materials and under the conditions. The sand should
cement
concrete:
-
with
with
concretes
ambient
temperature.
concrete constituents is to use bottomless 60 cm on each side and 28 cm deep will have
The aggregate is a concrete mixer. the mixture is first turned dry and cement; two minutes and should produce a homogeneous
be mixed by the lasts
crates a
in
can be mixed
by hand
in
small
quantities.
- 168 -
the concrete is usually transported sites, The time between mixing and placing should
On small wheelbarrow. in moderately
to
the
not
placement
exceed
site
by
20 minutes
warm weather.
from a height during placing since this The concrete should not be dropped When it is placed in wooden shuttering, the cause segregation of aggregates. watertight and wetted prior to placing. When a large latter should be clean, it should be poured in successive layers. height of concrete is to be placed, The concrete should improve its consolidation. suitable
for
shallow
Sodding
is
carried
rodding or vibration to be compacted by tamping, Compacting can be done by hand tampers and this is
then
layers out
(20 cm). by thrusting
Vibration is the most effective compressor and a vibrating needle.
a steel
rod it
procedure;
into is
after-care is Once the concrete has been placed, to ensure that the water does not vaporise too rapidly; After-care may be carried out by covering the concrete constantly
moistened
Shuttering
may
sacking,
the
carried
required this with
placed out
concrete. using
a
for around two weeks is called curing. a curing
agent
or with
etc.
may be removed
after
2 1 days
of
drying.
Shuttering
9.3.
usually These are moulds, is placed and the concrete is suitable for their task.
ment cient least
which the steel be constructed
reinforcement robustly and be
Usually planks of 2-3 cm thickness are used and the distance of the reinforcerods between themselves and from the walls of the shuttering should be suffito allow the correct placement of the concrete and leave a free space of at the maximum size of the aggregate.
A distinction of the structure used for exterior 9.4.
made from wood, in poured. They must
Steel
is made between the which are underground walls.
reinforcement
ordinary or not
shuttering which is visible, and high-quality
used
for parts shuttering
4
The main purpose of the steel reinforcement in reinforced steel concrete The is to accept the tensile stresses to which the concrete may be subjected. strength of a reinforced steel concrete structure depends not only on the quality of the concrete but also on the correct layout of the steel reinforcement bars. Two categories -
smooth
of reinforcement
mild limit
steel of
maximum relatively
bar
are
usually
used:
bars:
elasticity:
2,400
permissible working poor adherence;
kg/cm2; load:
1,600
kg/cm2;
-
-
high-adherence
steel
high-adherence
bars whilst the majority
4,200 kg/cm2; 2,800 kg/n,m2.
steel
they are 75 per of cases.
bars
cent
stronger,
scarcely it is
for plain
high-adherence round bars.
A reinforcement plan designed circumstances be carried out with Steel
bar steel
reinforcement
-
the
rods
-
loose
-
the
-
the individual components are
rust rods
Bending
are
is are
radii
mild
is cut
to
removed bent
to
(R) of
prepared the
shape
round
in
lengths
Installing
the
rods
should
by the
reinforcement
annealed
not
exceed
steel
wire
the
fol:.owing
Steel
of
assembled
values:
R =50 R=20 bars to ensure maintenance of Steel reinforcement too The bars oxidise and this
walls are Since these
awaiting
Steel reinforcement which is left to be bent and then unbent, intentionally fissures in the rods, especially those brittle. it is advisable Consequently, steel. Storage
plan;
and the
To ensure that the distances between the rods and the shuttering maintained during concrete placement, use is made of concrete wedges. wedges are embedded in the concrete, they must be rot resistant. sections
no
phases:
The main concern in installing reinforcement bars is the distances between the steel and the shuttering walls. close to the wall is poorly protected against corrosion. results in blistering which may spa11 the wall.
Steel reinforcement installation
under
R=30
steel
reinforcement
following
bars
bench:
using
should
steel
plain round former in
brush;
on a bending
rods
more expensive than advisable to use the
required
boxes, hoops, hairpins in mild steel 9.5.
the
a wire
assembled
steel
plain
high-adherence
are
by means of
rods are labelled.
steel
-
bars:
limit of elasticity: maximum working load: Since
169
on the site awaiting installation is likely or otherwise. This is likely to cause of high-adherence steel which is relatively to have such reinforcements made from mild
reinforcements
reinforcements
should
be stored
away from
moisture.
it is necessary to avoid contact For prolonged storage, that during storage rods of different diameters and different mixed up, which may result in subsequent errors on the site.
with
the
strengths
Ensure
soil. are
not
-
171 -
APPENDIX I STANDARD PLANS
Standard Protection
terrace ditch
cross-sections
Ridges
Progressively constructed Bench terraces Grassed channels Bank stabilisation Bank protection Gully correction Stone dams Weir Small earth dam Drainage techniques
terraces
5-6-7-8
176,
9
180
10
181
11
182
177,
178,
179
187,
188 194
12
183
13
184
14-15-16-17
185,
186,
18-19
189,
190
20-21-22-23
191,
192,
193,
24
195
25-26-27
196,
197,
198
28
199
29-30-31-32
200,
201,
202,
203
-
-L
172 -
5 00 Ill
- 173 -
cm
.
- 174 -
1
.. . .
=!itzLz~
AJ7-
._. 1, ..i.
-
y& ,~i -1,’ .\; .;F-T
-
176
-
1
-
177
-
I=rh c =v&h 3
z vaho
tn.
- 178 -
-
179 -
6 4a
L
6.50 m I
44s
a-/,
l.50
2.00 12.00
400 / 550
0.50 IO.60
0.60
IO.70
6.50 17.30
1.03 1 0.95
0.50 IO.60
1.7 5 1 1.80
-
QamYlON
180
-
blha4
cs
1
123456789
10 I40 I50 145 1.40
Ia 125
I+hdi~+diU#+di~[~)
0.5 1 0.4 1 03 1 07 1 02 101s
1 0.1s 1045
015
1
h=
100s
2.00 m.
1 =
lOOr
5.00 m
h
0.70 m.
=
-lmlGl -ct$Qace: w-k
uldrk.
5.2 w6
______*------
-
PaqpSS
~VELY
ccdwocrf2 3mi I~J’&,
af+hlU
&¶je
182
-
COAJSTRUCTED
,L@xx ’
na?Qec~~:
’
-
WlTll
183
-
-
184 -
-
185 -
- 186 -
.--
-1
V
@Wi
l=lu&g)
WATTt.Eb 6ejctSS WITH EAeql-
-
gobion
lad
-
cage L
gobion
+ob% I
Cc-
--
lboc q-i-
------.-.. ___
-
190 ‘-
-
GlLCY
~RRccnoN
rholwcq
191
-
-
192
-
(hz
6
OAOm.)
. ---‘e’ ----23 E
-
195
-
-
196 -
IS.00 m
-T I
-
1.W
5 .oo
197
-
2.00
-
198
-
-
199
-
.
. .
.
..:* *..:
,
,..
. . . -. .: .
- -_ _.. _-
29
-
201
-
. . .:. .. .
- 202
-
2OoWmm eYKT--@:,=
~~-
----
si
.----
-
. .
.
. . .
.
.
203
-
I
-.-_----we
OtJrhEkT Of AmzA\N \NTO a cnus cm2n mm=~
32
:P-.B
.-
-mm--
-
205
-
APPENDIX II BIBLII!GRAPHY -..--Reference 1
CTFT.
Conservation des sols au Sud du Sahara. rurales en Afrique, No. 12, 1969.
Collection
2
Soil
Conservation Service of the US Department of Soil conservation manual, Washington, 1950.
Agriculture.
3
Ministkre de la Techniques
4
BRGM.
5
FAO.
6
FAO.
Cooperation. Memento de l'agronome. rurales en Afrique, 1974.
Drainage agricole en rapport Bulletin du Bureau de recherches Section III, No. 2, 1978.
avec l'irrigation geologiques
Techniques
Collection et la et minieres.
salinite.
Drainage of salty No. 16, Rome, 1973.
soils.
Irrigation
and Drainage
Paper,
Drainage of heavy 6, Rome, 1971.
soils.
Irrigation
and Drainage
Paper,
No.
Earthmoving by manual labour and machines. Series, No. 17, Bangkok, 1961.
7
United
Nations. Flood Control
a
FRO.
Methodes et machines pour poterie et autres materiaux. Bulletin No. 6.
9
de 1'Agriculture: Agriculture et Ministere March-April d'information, NO. 347-348, A manual on establishment February 1973.
le
drainage Energie
techniques
10
FAO.
II
La conservation M. DELOYE and H. REBOUR. Collection des techniques agricoles
12
FAO.
Soil No.
conservation
for
par canalisations en et machines agricoles, Bulletin
forzt. 1980. in
man-made
forest,
de la fertilite mediterrankennes,
developing
des ~01s. 1953.
Soil
countries.
technique
Bulletin
30.
13
Ministkre de la Techniques
14
GOOR et al. arides.
Memento Coope?ration: rurales en Afrique.
Les methodes FAO, Rome,
de plantations
Reboisement PONCET A. 1974. eionomiques,
16
L. GUEFIN/P.
17
A-1.
FRASER.
18
W.F.J.
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