| NGOs
in the forest sector
AKRSP
The AKRSP serves
a population of about 1,000,000
people living in an area of approximately
70,000 sq. km of Northern Pakistan.
Forest resources are scarce and
often far removed from habitation
and the rapidly growing population
is threatening the fragile ecosystem.
AKRSP’s strengths are the
in its Village Organizations (VO)
and their potentials as extension
tool. This organization is also
heavily involved in agro-forestry.
This kind of forestry has been emphasized
because of the recognition of the
growing need for forest produce.
The AKRSP established its nurseries
soon after its inception and started
giving free saplings to farmers
while also providing support for
the establishment of village tree
nurseries. This has resulted in
large scale planting of timber,
firewood and fodder species on agricultural
land. The AKRSP estimates that about
45 million fuel wood trees have
been planted in the period 1983-2003.
The following statistics
prove the involved of AKRSP in the
forestry sector, including farm
forestry.
During 1990 AKRSP
achievements in forestry were:
• A 20 kanal nursery established
in Gilgit
• Plus tree surveys conducted
in Baltistan and Gilgit
• Planting of plus trees in
the six screening trial sites of
the pilot project and in Khomer
nursery.
• Shifting of the Populus
deltoids clonal bank in Gilgit to
Jutalapan and Khomer nurseries (AKRSP,
1990).
Table 12.
AKRSP involvement in forest nurseries:
cumulative as of Dec. 31, 1999
Activity |
Program
Area |
Baltistan |
Gilgit |
No.
of private forest nurseries
established/supported
No of forest plants /seedling
supplied (million)
No of forest tree self-planted
by VOs (million) |
1388
18
8 |
1225
3.49
5.53 |
93
7.43
2.58 |
Source: AKRSP. 1999.
Annual Report.
Table 13. AKRSP
involvement in forest nurseries:
cumulative & additions in 1998
| Forestry |
Program
Area |
Baltistan |
Gilgit |
No. of nurseries established
Total area of nurseries established
(ha)
Plants supplied by AKRSP(mil.)
Self-plantation by VOs (mil.)
VO/WO specialist trained
|
Cum. |
Add. |
Cum. |
Add. |
Cum. |
Add. |
1,408
80.05
14.80
7.55
1,278
|
16
5.99
3.60
0.83
116 |
1,206
39.81
2.57
4.92
321 |
|
121
23.29
6.41
2.46
590 |
6
1.05
1.52
0.29
58 |
Source: AKRSP. 1998.
Annual Report.
Table 14. AKRSP
involvement in forest nurseries:
cumulative & additions: Jan
1982 - Dec 31, 1995
| Forestry |
Program
Area |
Baltistan |
Gilgit |
No.
of nurseries established
Total area of nurseries established
(ha)
Plants supplied by AKRSP(mil.)
Self-plantation by W/VOs (mil.)
VO specialist trained |
Cum. |
Add. |
Cum. |
Add. |
Cum. |
Add. |
327
71.72
6.24
4.37
781
79 |
42
7.49
2.21
0.74
122
51 |
193
25.66
1.08$
3.25$
223
43 |
13
3.19 0.37 0.46
26
43 |
90
25.69 2.51 0.95
353
14 |
29
4.30 1.14 0.26
66
0 |
Source: AKRSP. 1995.
Annual Report.
Table 15. Nursery
development by AKRSP in 1995
Table 15. Nursery development by
AKRSP in 1995
| Program Area |
Cumulative |
Additions
during the year |
NORAD/AKRSP
Gilgit
Baltistan |
#
of nurseries |
Area (ha.) |
# of nurseries |
Area (ha.) |
9
8 |
12.23
11.67 |
3
1 |
1.97
2.22 |
Program
Area
SFP/AKRSP
Gilgit
Baltistan |
Cumulative |
Additions
during the year |
| #
of nurseries |
Area
(ha.) |
#
of nurseries |
Area
(ha.) |
3
8 |
3.80
3.90 |
0
0 |
0.00
0.00 |
Program
Area
GTZ/AKRSP
Astore |
Cumulative |
Additions
during the year |
| #
of nurseries |
Area
(ha.) |
#
of nurseries |
Area
(ha.) |
| 2
|
1.03
|
1 |
0.35 |
Program
Area VO/AKRSP
Gilgit
Baltistan |
Cumulative |
Additions
during the year |
| #
of nurseries |
Area
(ha.) |
#
of nurseries |
Area
(ha.) |
20
144 |
2.29
5.86 |
14
12 |
1.07
0.97 |
Program
Area
WO/AKRSP
Gilgit
Baltistan |
Cumulative |
Additions during
the year |
| #
of nurseries |
Area
(ha.) |
#
of nurseries |
Area
(ha.) |
56
38 |
5.71
4.23 |
11
0 |
0.91
0.00 |
Source: AKRSP. 1995.
Thirteen Annual Review.
Table 16. Forest
plantations by AKRSP in 1991-1992
Region |
VOs |
Area
(ha) |
Plants |
Gilgit |
200 |
1700 |
3,400,000 |
Baltistan |
200 |
1650 |
3,300,000 |
Total |
400 |
3350 |
6,700.000 |
Source: AKRSP. 1992.
Sustainable Forestry Development.
Report.
Research by AKRSP
Biomass
production of Common Farmland Trees
in Gilgit Region:
In December 1994 AKRSP conducted
a study through Dr. Javed Ahmed,
AKRSP and Raja Walayat Hussain,
PFI on biomass production of Common
Farmland Trees in Gilgit region
(Ahmed and Hussain, 1994). The study
covered eight species - black poplar,
white willow, hybrid poplar, willow,
mulberry, Tree of Heaven, black
locust and Russian olive.
Populus
alba:
White poplar
locally called sufaida is a tall
deciduous tree of Mediterranean
origin. It is light demanding and
frost hardy. The wood being soft
and white gives good quality rafters
for construction, poles are used
as electric and telephone lines
etc. Other uses include shuttering,
packing cases, paper and match industry.
Small wood is used as firewood.
The result of the
analysis gives the range and average
ratio between air-dry and green
biomass of white poplar and is shown
in the table.
Table 17. Range
and average ratio between air-dried
and green biomass of white poplar
Parts
of the tree |
Range |
Average
ratio |
Logs/poles
Firewood
Foliage |
490-.615
.306-.412
.430-.515 |
.547
.360
.470 |
Source: Ahmed,
J. and R. W. Hussain. 1994. Biomass
production of common farmland trees
in Gilgit Region. Pakistan Forest
Institute publication.
Populus
nigra:
Black poplar
locally called sufaida has its origin
in Europe, Central and Western Asia.
It is a fast growing and multipurpose
tree species. It is a light demanding,
tall tree with a narrow crown. Its
future potential in Northern Areas
is good as it meets most of the
demands of the farmers.
The result of the
analysis gives the range and average
ratio between air-dry and green
biomass of black poplar and is given
in the table below.
Table 18. Range
and average ratio between air-dried
and green biomass of black poplar
Parts
of the tree |
Range |
Average
ratio |
Logs/poles
Firewood
Foliage |
.432-.538
.300-.420
.300-.405
|
.473
.364
.365
|
Source: Ahmed, J.
and R. W. Hussain. 1994. Biomass
production of common farmland trees
in Gilgit Region. Pakistan Forest
Institute publication
Salix:
Willow locally
called baed is a moderate sized
deciduous tree. It is found up to
1,800 m altitude growing in wet
swampy places and on alluvial deposits.
A variety known as
Salix alba or sweet willow yields
quality timber. The result of the
analysis gives the range and average
ratio between air-dry and green
biomass of willow and is given in
the table below.
Table 19. Range
and average ratio between air-dried
and green biomass of willow
Parts
of the tree |
Range |
Average
ratio |
Logs/poles
Firewood
Foliage |
.550-.596
.340-.378
.415-.480
|
.568
.352
.450
|
Source: Ahmed,
J. and R. W. Hussain. 1994. Biomass
production of common farmland trees
in Gilgit Region. Pakistan Forest
Institute publication
- Report
on Willow disease in Phandar area,
Gilgit:
Zakaullah Chaudhary, Forest Pathologist,
Pakistan Forest Institute, conducted
a study on the diseases of willow
in Phandar village in May 1989 for
the AKRSP and identified three species
of willows Salix purpurea, S. seriocarpa
and S. tetrasperma (Chaudhary, 1989).
These species are used as fodder,
basket-making, roof construction
material and for timber. Many insects,
fungi, bacteria, viruses and even
higher plants are capable of causing
damage to the leaves, branches,
the hole and also the roots of Salicaceae.
The willows were found suffering
from three diseases: canker, witches-broom
and sap-sucking insects incited
by a bacterium, mycoplasma-like
bodies and aphids respectively.
Bacterial canker and aphid attacks
appeared more common and damaging
as compared with witches-broom disease.
The symptoms of canker
may vary with the host species,
the clone, ecological conditions
and physiological state of the tree:
ringing the buds, die-back of shoots
and appearance in spring and chiefly
on one or two years old shoots,
of a slimy exudates, whitish, changing
afterwards to brown. The witches-broom
includes excessive and premature
development of buds, reduction in
leaf size with leaves often becoming
brittle and chlorotic, shortening
of internodes, followed by decline
or death of affected branches or
the plants. The plants give a black
look due to the growth of nodules
on the foliage which is visible
from a distance. Sometimes the stem
and bark of branches or the soil
below also turn black.
Control:
The canker can be controlled through
the propagation of disease-free
stock. To protect the plants/cuttings
from the attack the entire plant
may be sprayed with Bordeaux mixture.
The witches-broom can be controlled
by planting of disease-free stock,
sanitation cutting of infected trees
etc. and the sap-sucking can be
controlled by applying 30-100 grams
of granules of Disyston, Temik,
Lebaycid and Diazinonf in the soil
around the tree base in 1-2 m circle,
particularly to young plants.
AKRSP
and IUCNPakistan
They issued a joint report of the
Final Review Mission of Hunza Report
Series (June1989). The report covers
the main achievements of the period
October 1987 to June 1989 and are
as follows:
Village nurseries of poplar stool-bed
were set up in Khaiber and Galapan
villages of Gojal using material
from good local trees (Populus nigra
and Populus cilitia) and imported
Populus deltoids; these are now
well established.
A project nursery was set up in
Gilgit to grow certain exotics and
P. deltoids for the project. But
this suffered from flooding and
neglect during civil disturbance.
In the spring of 1987 the Pakistan
Forest Institute (PFI) provided
18,000 imported P. deltoids to the
project; most of these were sold
to VOs outside Gojal.
Cutting from “plus”
trees were selected from Gilgit
district and made available to all
seven pilot project VOs for nursery
establishments.
(AKRSP/IUCN Pakistan, 1989).
IUCN
Pakistan
This organization has been involved
in sustainable resource development
in the Northern Areas and its foremost
project called the Mountain Area
Conservancy Project (MACP) has been
in operation since 1999. Its main
thrust is the conservation of fauna
and flora but the management of
forests as natural habitats is also
one of its main foci. In the Northern
Areas it is working in the Gojal,
Qashqar and Nanga Parbat areas.
It has proposed a
comprehensive plan for joint forest
management in three valleys of the
Nanga Parbat Conservancy (Ali, 2004).
The main objectives of this plan
are:
- to ensure sustainable use of forest
resources
- satisfy current and future needs
of the local communities
- ensure development of biodiversity
- speed up economic growth
The report lays out
details about various steps in developing
the plan, its implementation and
future management and financial
resources to run the plan etc.
The following
information has been taken from
Ali (2004) and provides information
on the forests of the three areas
where the joint forest management
plan is proposed.
Table
20. Forest description of three
valleys in the Nanga Parbat Conservancy
| Region |
Forest
description |
| Astore
sub-division |
Chilgoza,
juniper, temperate scrub,
dry zone blue pine, dry zone
spruce, sub-alpine |
| Dashkin-Mushkin-Turbuling |
Blue pine
mixed with spruce, Rosa webbiana,
Berberis spp., Lonicera spp.and
Rubus spp., in lower elevations
chilgoza forest found around
blue pines and associated
with Fraxinus, Lonicera, Prunus
etc. |
| Basho sub-valley |
Blue pine
with patches of birch above
up to 3,800 m |
Source: Ali, M. 2004.
Prospects and implications of collaborative
management of protected forests
in Northern Areas of Pakistan. Report.
IUCN Pakistan (MACP).
Aga Khan
Planning and Building Services,
Pakistan (AKPBSP/BACIP):
WWF-Pakistan
and BACIP conducted a joint study
on fuel wood consumption practices,
interventions for fuel wood conservation
at the domestic household level
and relative impacts of conservation
of forests and wood resources in
the Northern Areas. The study aimed
to assess the impact of efforts
for fuel wood conservation at the
domestic household level in terms
of technology, products, construction
techniques and community education
on the subject. The results revealed
that:
The major source of energy (86%
average, with 82% used for cooking
and 91% for heating) in the Northern
Areas is fuel wood.
The average fuel wood consumption
amounts to 964,000 cubic meters
during winters and 234,883 cubic
meters during summer. This amount
to 1.1 million cubic meters per
year.
The existing forests are only 10.5%
of the total regional area, i.e.,
7.04 million ha.
Interventions for fuel wood conservation
developed by AKBSP (BACIP) are saving
12% to 60% fuel wood at the domestic
household level per winter season
calculated on the basis of single,
double and triple intervention per
household (i.e. October to March,
with severe cold from November to
February).
The other sources of fuel like fuel
gas, coal, electricity or solar
energy are either scarce, unavailable
or unaffordable by the people.
The interventions for fuel wood
conservation assessed during the
study were fuel-efficient stoves,
roof hatch windows and thermal insulation
techniques for the buildings in
the Northern Areas.
There is a major impact of fuel
wood on deforestation. If the said
interventions are implemented on
a large scale then the pressures
on forests for fuel wood come down
to at least 60%. This will contribute
towards forest conservation.
A sizeable number of people are
involved in the wood trading business.
Their alternative source of income
has to be identified/developed in
line with the conservation process.
The interventions also improve the
general living conditions at the
household level.
(Chaudhry, 2001).
|