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CLOSE THIS BOOKSpecial Public Works Programmes - SPWP - Planting Trees - An Illustrated Technical Guide and Training Manual (ILO - UNDP, 1993, 190 p.)
Appendices - Technical sheets
VIEW THE DOCUMENTAppendix 1 - Surveying and mapping of large planting sites
VIEW THE DOCUMENTAppendix 2 - Laying out and preparing soil and water conservation structures
VIEW THE DOCUMENTAppendix 3 - Survival count

Special Public Works Programmes - SPWP - Planting Trees - An Illustrated Technical Guide and Training Manual (ILO - UNDP, 1993, 190 p.)

Appendices - Technical sheets

Appendix 1 - Surveying and mapping of large planting sites


Figure

Basic forest surveying and mapping is needed for efficient planning and management in reforestation. Information on the area is gathered and a sketch drawn in the field. The final map is completed in the office.

1. Recording of field data and drawing of field sketch

To collect and record the field data, a box compass is needed and sheets for field notes should be prepared. Try to get hold of maps and aerial photographs of the area, on as large a scale as possible. This will make the work easier.

The field work can be divided into three main areas:

(a) General orientation.
(b) Gathering of field data.
(c) Drawing the field sketch.

(a) General orientation

First, acquire a general knowledge of the area. Consult maps, note key points such as forest zone corners, rivers, roads or trails. Familiarize yourself with the terrain by walking around it and get an overview of the variation in site conditions.

Surveying and mapping

General orientation


1. Consult map


2 Walk around

Gathering field data


Compass


Aiming

Drawing the map


Protractor


Drawing

(b) Gathering field data

When you have a general overview of the area, start gathering the field data. Choose a starting point (point 1) that is easy to relocate and describe. Note it on the sheet.

Example: Point 1 - Corner road and plantation, big Acacia tree, 60 cm in diameter.

Now you have to use the compass. A second point (point 2) along the side you want to measure has to be chosen. Always choose a clear landmark to point the compass at - for example, a characteristically shaped tree or a rock.

Occupy point 1, facing the direction of point 2. Hold the compass steady in both hands with your elbows against your body. Then sight point 2 by pointing the front sight of the compass to the landmark chosen as point 2. When the needle stops swinging, read the bearing to the nearest degree. Record the compass reading in the column provided in the field note sheet in line with point 1-2.

When using the compass, make sure that it is free from the effects of magnetism due to iron objects carried by yourself or in nearby surroundings. Otherwise you will get false readings.

Measuring the distances between the points can be done by pacing. The number of paces for 100 metres has to be known so that you later can convert the number of paces recorded into metres. The pace length is individual and must be measured for each person. For exact maps, a tape chain or a rope with metre graduations can be used for measuring. Note on the sheet the number of steps taken to cover the distance. Describe easily defined points and corners in the field note under the column "note". For example: Stone 1 x 2 m, 1 m high, east bank of river.

Survey field notes - suggested outline

Location: _________

District: ______________

Plantation: ________

Date inspected: ________

Area: ____________

Inspected by: __________

POINT

COMPAS READING (degrees)

DISTANCE

NOTES



Paces

Metre


1

-



corner road/plantation acacia tree 60 m

1 -2

334


150

heavily eroded area

2-3

356


210

big stone 4x8 metre

3-4

360


250

dry hilly area

4-5

360


300

after 140 m, high grass

5-6

265


250


6-7

256


100

40-100 metres wet

7-8

181


200

high grass, 10 m crossing path

8-9

182


400

termites, high grass after 310 m

10- 11

100


100

30 m river (no problems crossing)

11 - 12

177


360

eroded area after 130 m

12- 13

136


110


13- 1

214


320

along the road


























(c) Drawing the field sketch

At the same time as you collect the compass bearings, trace a field sketch. Orient the sketch so that the top of the map indicates the North.

In the field sketch, mark the starting point as point 1. Mark point 2 and draw the line between point 1 and point 2. This is just a field sketch and there is no need to be exact but try to use a convenient scale (do not make the sketch too small) and to make the line more or less follow the direction in which you are going (the compass bearing). Then indicate the details of the area traversed.

As you proceed to the next station, take note of and indicate carefully the vegetation cover and natural land marks you come across. If you come across roads, trails streams, take a compass bearing of their direction. Mark them in the sketch with arrows.

Show the approximate extent of different vegetation covers by drawing light lines. Use a square on the sketch to indicate corner points.

Large areas may be divided into numbered compartments of 10-20 ha, and sub-compartments of 1-3 ha, to facilitate orientation, planning and management.

It is preferable to subdivide areas according to natural features (rivers, ridges), existing roads or tacks, and distinctively different ground cover (rocky areas, swamps, rich vegetation, poor vegetation).


Figure

2. Tracing the final sketch

Now the rough field sketch should be turned into a more exact final sketch using all the information collected.

(a) Decide the scale of the map.
(b) Plot the map.
(c) Correction of the sketch.
(d) Determining the area.
(e) Add the details.

(a) Decide the scale of the map

To produce a map of a convenient size, the actual measurements on the ground have to be reduced to a certain scale. According to the scale chosen, the map is a projection in proportion to the reality.

The scales most commonly used in forestry are 1:5,000, 1:10,000 and 1:20,000.

If the scale used is 1:5,000, 1 cm on the map represents 50 m on the ground and 100 m on the ground represent 2 cm on the map. If the scale used is 1:20,000 then 1 cm on the map represents 200 metres on the ground and 100 metres on the ground represent 0.5 cm on the map. The smaller the scale, the bigger the resulting map of a certain ground measurement.

Select an appropriate scale so that when plotted, the map is well contained on the sheet and the details can be clearly seen.

(b) Plot the map

Use graph paper. Always consider the top of the plotting paper as North. In the upper right hand corner of the sheet, place an arrow pointing north and the scale adopted for the map.

Examine the field notes and the field sketch to determine the length and the general direction of the surveyed area. Thereafter decide where on the sheet you should start so that the sketch is placed more or less at the centre.

To transfer the bearings measured with the compass onto the sheet, a protractor is eded. There are two kinds of compasses. One divides the circle into 360 degrees, the her into 400 degrees. Be sure that the protractor has the same number of degrees as the compass used.

Mark point 1 with a dot on the plotting paper and place the protractor so that point p coincides with the dot.

Then mark the reading or bearing by a light dot called a "guide dot". Place a ruler with the "0" graduation of the scale over point 1, and its edge touching the guide dot. Plot the distance between point 1 and 2 according to scale adopted.

The procedure is repeated until all the stations of the survey are plotted. Indicate the corner stations by enclosing them with squares.

(c) Correction of the sketch

When plotted, the final line seldom closes the area completely, because of errors in taking the bearings and measuring distances. When correcting this, point 1, the starting point, remains fixed, and the other corner stations have to be adjusted.

One method of deciding on the adjustment is to draw a straight, horizontal line AB. The length of this line should equal the total length of the measured sides of the area. Use the same scale as used when plotting the map - e.g. 1:20,000. On this line, mark off corner stations from point A at intervals equal to their respective plotted distances. At point B draw a perpendicular line equal in length to the gap between the first and last station when plotted "y". This line is called BC. Then draw the line AC. Erect lines from every point (each indicate one corner station) to line AC. These lines determine the distances by which the stations will have to be moved in order to close up the area.

The broken line figure at the foot of the opposite page is the first sketch plotted. Draw from the corner stations, light lines parallel to line "y". Along these parallel lines the stations are moved downwards, and the distance is determined for each point above (the distances between AC). The adjusted stations in the figure are connected by a solid line which now represents the area surveyed.

In this example the stations had to be moved downwards. If the last station on the sketch ends up below the starting point they will have to be moved upwards.


Figure

(d) Determining the area

The sketch is drawn on graph paper, which is divided off into squares. To determine the area, count the number of squares representing the plantation inside the area. The portion of divided squares is estimated and added to the area of whole squares. If the scale is 1:5,000 and the size of the squares is 0.5cm by 0.5cm, one square equals 625 square meters (25x25 meters). Sixteen squares would make one hectare.

(e) Add the details

Transfer all important details from the field sketch to the final sketch. Show the different vegetation covers by light lines. Indicate them by using abbreviations or with different coloured pencils.

Explain all signs and colours used to avoid misinterpretation.


Final map

Appendix 2 - Laying out and preparing soil and water conservation structures


Figure

In order to be efficient conservation structures have to be spread over an entire slope. All structures should be built along the contour lines. Otherwise the flow of run-off water will be concentrated and the structures damaged or destroyed.

Finding the contour lines

It is impossible to find the contour lines by eye. A simple and practical way to find them is to use a hosepipe water level. This method requires three workers.

Take two stakes, sticks or poles about 2 metres tall and mark them halfway with a series of lines one quarter of a centimetre apart. Tie the open ends of a narrow transparent hosepipe, 10-20 metres long, to each of the poles. Fill the hose with water. Water is added or tipped out until the water level lies between the marked lines on the poles. All air bubbles have to be expelled.

Whenever the bottoms of the two poles are level, the water in each end of the hose will reach the same mark on the poles. These places should be marked with sticks. By moving one of the poles to a position in which the water level in each end of the hose is the same, the contour line may be staked out.

The contour lines can also be found with the help of a water level. Fix a rope (about 10m long) to each end of a pole (at 100cm above ground level). Mark the middle of the rope with a knot. Hang the water level in the middle of the rope. Place the poles so that the water level shows that there is ne elevation. Mark with stakes.

Finding contour lines


Pole moved until water reaches mark


Open ends of transparent hose tied to stakes


stakes level


stakes not level


Using water level

Microcatchments

The size and layout of microcatchments varies according to rainfall and soil type. Where rainfall is high, a large number of smaller catchments should be used to collect enough water but to avoid overflowing. In dryer areas the catchments need to cover a larger area in order to collect enough water to sustain the trees during the dry season.

Microcatchment areas range from about 25 square metres in areas with 400 mm annual rainfall to about 100 square metres in areas with about 200 mm annual rainfall. In areas with over 500 mm of annual rainfall microcatchments should generally not be used because of the risk of overflowing. The catchments are constructed from loose soil and stones.

Triangular microcatchment

A triangular microcatchment is made of V-shaped bunds. They work best on moderate slopes (3-5 %).

Two contour lines have to be established. The tips of the V-shape should be placed on the upper contour line and the corner on the lower. Dig a pit in the corner of the V-shape. In areas with between 200-400 mm rainfall, the pit should be about 2.5 x 2.5 metres wide and 40 centimetres deep.

Use the soil from the pit to construct the bunds. They should be 5 to 10 metres long and about 25 centimetres high. Compact the bunds well.

Plant the seedling in the corner of the pit at the base of the bund.

Microcatchments


The size and layout vary according to rainfall and soil type


Figure


Triangular microcatchment

Semicircular microcatchments (half moons)

The tips of the semicircular microcatchments should be on the contour line. The radius should be about 3 metres and the tree should be about 1 metre uphill from the lowest point in the semicircle. The catchments may be linked together by channels in the shape of "fishbones" (see opposite page). They will channel the water towards the seedlings.

Semicircular bunds (half moons) can also be constructed around existing trees. In dry areas tree species often become like bushes as a result of grazing and lack of water. They will, however, often start to grow into trees when provided with water, pruned and protected from grazing.

Contour ridges

Contour ridges are ridges dug out of the hill slopes along the contour lines. They are used in heavy soil with low permeability. Proper spacing of the ridges is important. If the ridges are spaced too far apart, they will be washed away.

Dig a shallow trench, 5-15 centimetres deep, along the contour line. Compact the earth, preferably mixed with stones, to a ridge 30 centimetres high on the downhill side. The barrier can be strengthened by means of branches and other material secured with stakes.

Semicircular microcatchments


Natural regeneration


Fishbone water catchment

Contour ridges


Figure

Terraces

Terraces are strips levelled for tree planting along contours. They are mainly used on rather steep slopes (more than 20 %). Usually they are constructed with about 2.5 m vertical intervals. A soil depth of at least 0.5 m is needed. For forestry plantations narrow level strips along the contour lines are normally sufficient. Wider terraces are expensive to build, as they require a considerable amount of manpower or heavy equipment, such as bulldozers. Wider terraces should only be built if the area will also be used for crops or grazing.

1. First find the contour lines and mark them with pegs.

2. Remove the topsoil and save it above the terrace. Mixing fertile top soil with infertile subsoil should be avoided.

3. Dig the step. Place the excavated material downhill to extend the terrace.

4. Replace the fertile topsoil.

On wide terraces it may be advantageous to mix trees with crops. The trees can be planted along the edge or at the toe of the terraces, while crops can be grown in the centre. In dry areas the trees will grow better along the toe, which is the wettest section of the terrace. On steep slopes where narrow terraces have to be constructed, fruit trees may be preferable.

Terraces


1. Mark contour lines with pegs


2. Remove top soil, save above


3. Excavate


4. Replace topsoil


Terraces with trees and crops

Appendix 3 - Survival count


Figure

Replacement planting is an expensive measure. The cost per seedling is double or triple compared with the first planting. Therefore it is necessary to decide carefully if replacement is needed or not. This is done by calculating the survival rate.

Survival is difficult to estimate by simply looking at a plantation site. As looking at each and every seedling planted would be extremely time-consuming, the survival of a portion of the plants is checked. The check should include all sections of the plantation (not only the one closest to the road). The best procedure is to check a number of rows equally distributed across the planting area. In areas of less than 2 hectares, you should sample every 5th row and in areas of above 2 hectares you should sample every 10th row.

For every spot in the row where a tree was planted, mark on a piece of paper whether it is dead/missing or alive. An example of a survival count form is given on the following page. Recording plant survival separately for each line will help you to see in which part of the plantation replacement planting might be needed.

If the plantation consists of more than one species, survival should be checked species-wise. This together with information on how many seedlings were planted of each species (noted on the plantation history form), will make it possible to get a good idea of the survival of the different species. Together with estimates of the average height of the species, it can also provide useful information for planning future plantations.

The survival rate is calculated by dividing the number of surviving plants by the total number of plants and multiplying by 100.

Replacement is needed only if more than two out of ten plants are dead and only where at least two successive seedlings have failed. If the overall rate of failure is less than 20 per cent, replanting is carried out only in places where failures are heavily concentrated.

To make replacement planting easier, bring sticks or ribbons along when counting. Mark any part of the plantation with a high failure rate.

The difference in size between the plants used for replacement and the plants at the site should be kept as small as possible to minimize competition. The survival rate should be checked in time to carry out the replacement planting one year after planting, at the latest, in fast-growing plantations. In slower-growing plantations it should be checked in tune to carry out replacement planting during the second year after planting.

During the survival count, the height growth should be estimated and noted.

Survival count form

Plantation: __________

Date inspected: ____________

Area: ______________

Inspected by: ______________

Planting date: _______



Figure

SURVIVAL RATE

ROUGH SURVIVAL RATE SPECIESWISE

Estimated height

Velvel 0.6 m
Vagai 0.4 m
Usilam 0.2 m

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