Base line studies of nawaB shah forest, sindh-
2018
SFM Project Submitted by
Dr. Syed Aneel Ahmad Gilani
Botanical Sciences Division
Pakistan Museum of Natural History, Islamabad
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1. INTRODUCTION
- 1.1.
- DESCRIPTION OF LANDSCAPE SITES (NAWAB SHAH FOREST)
Seven landscapes have been selected to demonstrate approaches and good practices regarding sustainable forest management (SFM), biodiversity conservation, enhancing carbon mitigation and carbon stocks. Two of the landscapes are located within the Temperate Coniferous forests of Siran and Kaghan in Khyber Pakhtunkhwa (KP), one in the Sub-tropical Evergreen Thorn (scrub) forests in Salt Range, Punjab, and two each in the Riverine forests in Punjab and Sindh.
The salient features of these landscapes are described here
- 1.2.
- Dhingano-Lakhat
- Riverine
- Forests
Landscape
The proposed site is situated along the Indus River, downstream of Sukkur Barrage on the left bank in the Nawab Shah District. The landscape is comprised of Dhingano Reserve Forest (1,538 ha) and Lakhat Reserve Forest (1,462 ha) in Nawab Shah District. Both forests are also separately designated as wildlife sanctuaries under the Sindh Wildlife law in addition to their designation as Reserved Forest under the Forest Act. The total area of the Dhingano-Lakhat Riverine landscape is 3,300 ha. One of the reasons of inclusion of this landscape in this project is that most of the forests downstream of Sukkur Barrage do not get inundation except in high or super floods whereas this landscape, situated between Sukkur and Kotri barrages that is in Central Sindh still receives substantial annual inundation. Abad Reserve Forest is located adjacent to this landscape. There is an opportunity of developing a corridor from the riverine landscape to Abad Reserve Forest. River meandering in this section of the river is common with the result that the processes of erosion and accretion are also common. Thus, there is an opportunity for recreating new riverine forest with traditional regeneration techniques that is broadcasting of treated seed of native species including Populus euphratica during the last receding flood There are two villages and hamlets situated in and around these forests which consist of 1,670 households and 10,000 forest dependent local persons. One of the two dependent local communities are actively involved in protection and conservation of forests.
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- 1.3.
- Map of Nawab shah forest area
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- 1.4.
- Sindh Forest area
Sindh Forest Department controls an area of 241,198 hectares in the Riverine tract of the province which are categorized as "Riverine Forests"; locally known as Kacho forests. These forests are located along both the banks of River Indus in Thatta, Hyderabad, Dadu, Larkana, Naushero Feroze, Nawabshah, Khairpur, Sukkur, Shikarpur, Ghotki and Jacobabad Districts and
have been declared as “Reserved Forests” under Forests Act, 1927. The rich alluvial soils
support the tree species including Acacia nilotica (Babul), Populus euphratica (bahan), Tamarix aphylla, Tamarix dioca (Lai) and Prosopis cineraria (Kandi). Riverine forests are the most productive forests of Sindh; producing wood material for domestic and commercial purposes. Existence of Riverine forests of Sindh is dependent on flooding by the river. They are flooded by the spate of River Indus, on lands and soils over its banks. Floods occur due to the flow of large quantities of water in the river that cannot be accommodated. Both the land configuration and the soils in riverine tract are made by flood waters. The spate was a common summer phenomenon in the past, until such a time that the river water was not diverted and extracted through dams, barrages, head-works and link-canals.
Riverine forests are the mainstay of forestry in Sindh. They provide products and services such as timber, firewood, pit props for mines, forage and browse for livestock; supports biodiversity and game animals. Other non-timber forest products include tannin from bark, gum, honey and even fish from dhands (ponds) and dhoras (depression of old river beds). They act as carbon sinks, moderate climate, stop soil erosion and also protect soils and settlements from the ferocity of flood waters.
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- 1.5.
- GIS Map of Nawab Shah Forest
1.6.
Map-01: Nawab shah forest Grids on the GIS Map
Map-02: GIS Map for the Nawab shah forest sites
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Map-03: Nawab shah Reserve Forest Locations for the field work
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2. Methodology (Vegetation Analysis)
Collection: Flowering plants should be collected when they are in the flowering or fruiting stage, it is better if both flowers and fruits are present. Entire plants of herbs and grasses are to be collected. In case of shrubs and trees, take cuttings of the flowering and fruiting shoots. Put the collected specimens in a large polythene bag to prevent drying and put a tag inside the bag giving the name of the locality. Note the date of collection, field number, habit of the plant, flower colour, etc. in a field notebook. Press the plants in the field between newspaper sheets and blotters. Change the blotters daily till the plants are completely dry. Use extra blotters for fleshy plants and change blotters twice a day. Some heat may be applied to facilitate drying. Some plants turn black if they are not dried quickly. Trim large flowers, rhizomes, etc. to make them thin; cut away the thicker branches.
Preservation: For preservation, soak the dried specimens in a solution of ethyl alcohol containing 3% mercuric chloride. Then dry them again. When fully dry, mount each specimen on a herbarium sheet. Use some glue to fix the plant on the sheet. Use scotch tape to fix thick fruit or floral parts. Seeds can be kept in a paper-pocket and pasted on the sheet. Preserve large and fleshy fruits in F.A.A. (90 ml alcohol + 5 ml acetic acid + 5 ml formalin) in glass jars. Herbarium sheet size: 11.5 x 16.5 inches (PMNH Herbarium)
Mounting and Storage: Put a label on the lower right side of the sheet. Write down the name of the plant, family, locality, collectors name, identifiers name and field numbers on the label. After giving an accession number to each sheet put the specimens family-wise in steel almirahs arranging them genus and species-wise alphabetically.
Vegetation Analysis
Phytosociological survey, an important tool of ecology for vegetation assessment to be conducted in Sept. 2017 at Kaghan and Siran valley.
On the basis of Importance Value Index (IVI.), sampled vegetation shall be described into different plant communities. The community within each stand was named with the first three of the species having highest Importance Value Index irrespective of its habit. When two or more species closely approached each other in order of Importance Value, the community shared the names of these dominants. The name of the species with highest I.V appeared first followed by other dominant species. The generic names of the dominant species were used for naming the community.
Quadrate Analysis
For vegetatoinal investigations the quadrate method is the important method if we are studying vegetaion structure in a particular habitat.
Bryophytes & Lichens
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0.5 ×0.5 meters Herbacous flora 1 to 2 ×2 meters Shrubs 5-10 × 10 meters Trees 10-20 × 20 meters
Density.
Number of individuals of a species in a unit area is called density. (Mass per unit volume). Density should not be compared with the similar types of plants. The relative density is referred to as percentage of the individuals of each species that contribute to the total individuals in a community or the area. Density of a species = Total number of individuals of a species in all the quadrates (plots)
Total area of the sample quadrates e.g. sample area = 10 × 10 m, five plots = 500 m2 Relative Density = Number of individuals of a species ×
Total number of individuals of all speceis
100
Frequency
The percentage of the plot, point or quadrate in which a species occur is called the frequency (%). It only tells us the chance of finding a speceis in a sampling area. Relative frequency of a species is a percentage frequency of the total frequency. Frequency (%) = No.of quadrates in which a speceis occur
Total No. Of plots taken
× 100
Cover
Cover is one of the most important attribute in phytosociological studies. It is a ground area occupied by herb, shrub, or tree. Canopy cover is a total ground surface under a canopy of a plant and could be a larger than the actual area sampled due to the overlapping branches of different trees, specially in the stratified forest. For DBH (diameter at breast height) of tree species, diameter measuring tape is used to measure stem girth at 4.5 feet above the ground surface. Each measurement is individually converted into the basal area using the following formula.
Basal area of the tree = π r 2
For example DBH of tree is 25 cm Radius will be 25/2 = 12.5 cm Now basal area of the tree will be 12.5 × 12.5 × 3.1415 = 490.86 cm2 For m2 = 490.85/10000=0.049 m2
- Average cover of a species =
- Total basal area of a species
- × 100
No. Of plants of that particular speceis
- Relative cover of species= Total cover of all individual of a species
- × 100
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Total cover of all the speceis
IVI (Importance Value Index)
Density indicates the number of individuals of a species while, frequency shows how these individuals are distributed (pattern of distribution) in a community. If a species is regularly distributed, the frequency value will be high, otherwise, low frequency value be recorded, a species with irregular distribution in a community. Cover tells how much area is occupied by a species. Ecologists use to recognize dominant species of the community on the basis of frequency or density alone. Now scientists give equal weight to all the 3 attributes.
IVI= RF+RD+RC = IVI RF= Relative frequency RD=Relative Density RB/RC= Relative basal area/Relative Cover
Dominance
If a group of speceis has a capacity to control the community due to its high number, large volume or some specific activity is called dominant species. Dominance is considered as a biological structure of community too.
Dominance = basal area or area coverage of a species Area samples Relative Dominance = Dominance of speceis A
Dominance of all species
× 100
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3. Results
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3. Results
3.1. Location-01 Kot Dingano
GPS Data / Coordinates
Location
Kotdngo
- Coordinates/GPS
- Altitude
N26 16.339 E67 56.810 N26 16.249 E67 56.697 N26 16.339 E67 56.810 N26 16.441 E67 56.908 N26 16.579 E67 59.636 N26 16.532 E67 59.495 N26 16.488 E67 59.353 N26 16.666 E67 57.975 N26 16.732 E67 57.822 N26 16.697 E67 57.676 N26 15.524 E67 57.284 N26 14.765 E67 57.355 N26 14.884 E67 57.085 N26 14.596 E67 57.116 N26 14.863 E67 57.069
95 ft 95 ft 95 ft 93 ft
Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo Kotdngo
141 ft 131 ft 116 ft 107 ft 116 ft 92 ft 102 ft 99 ft 131 ft 116 ft 116 ft
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Site-01 (Kot Dingano Forest) Transect-01 Table: 01
S.No
1.
Plant Species
Tamarix dioica
- IVI
- Community
35.36 Desmostachya-Acacia-Prosopis Community
2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13.
Acacia nilotica Sonchus asper Prosopis cineraria Phyllanthus sp Tamarix aphylla Solanum surratense Solanum nigrum Amaranthus viridis Desmostachya bipinnata Launea procumbens Alhaji mauroram
50.43 14.76 37.82 16.31 26.49 9.2 5.98 11.11 52.99 11.81 10.4
Saccaharum spontaneum 14.19
Vegetation (Transect-01)
In this transect the data describes the equal distribution of the floral diversity including the trees, shrubs and herbs. The maximum plant species with highest IVI is Desmostachya (52.99) with second highest specie is Acacia nilotica with second highest IVI value (50.43) and third highest value of IVI is Prosopis with value of (37.82). The plant species with lowest IVI is Solanum nigrum having the lowest value of 5.98. The sampled area has more herbs including the fair representation of trees and shrubs. The Phyllanthus is the most commonly found shrubs along with Saccharum. The tree species with fair representation is Acacia nilotica. The IVI values of the plant species is mentioned in Table: 01.
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Site-01 (Kot Dingano forest) Transect-02 Table: 02
S.No
1.
Plant Species
Tamarix aphylla
IVI 33.43
Community Populus-Tamarix dioica-Tamarix aphylla community
2. 3. 4. 5. 6. 7. 8. 9.
Pantanema sp
7.96 18.67 7.16 15.82 20.82 9.51 57.55 23.49 10.99 5.37 15.18 37.74 7.45 2.94 8.06
Desmostachya bipinnata Launea procumbens Cynadon dactylon Saccharum spontaneum Salix sp Populus euphratica Phyla nodiflora
10. Solanum surratense 11. Sonchus asper 12. Alhaji mauroram 13. Tamarix dioica 14. Calotropis procera 15. Citrullus colocynthis 16. Cyperus sp 17. Aerva javanica 18. Acacia nilotica
6.36 11.15
Vegetation (Transect-02)
In this transect the data describes the equal distribution of the floral diversity including the trees, shrubs and herbs. The maximum plant species with highest IVI is tree species Populus euphratica having the IVI value (57.55) with second highest specie is Tamarix dioica with second highest IVI value (37.74) and third highest value of IVI is Tamarix aphylla with value of (33.43). The plant species with lowest IVI is Citrullus colocynthis having the lowest value of 2.94. The sampled area has more herbs including the fair representation of trees and shrubs. The Tamarix aphylla and Saccharum spontaneum are the most commonly found shrubs in the sampled area. The tree species with fair representation is Populus euphratica and Tamarix dioica. The IVI value of all the species is mentioned in the Table: 02.
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Site-01 (Kot Dingano forest) Transect-03
Table: 03 S.No
1.
Plant Species
Prosopis cineraria
- IVI
- Community
84.32 Prosopis-Cynadon-Desmostachya
Community
20.29 4.85
2. 3.
Tamarix dioica Sonchus asper
4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14. 15. 16. 17.
Cynadon dactylon Launea procumbens Phyla nodiflora Desmostachya bipinnata Polygonum plebium Euphorbia prostrate Tribulus terestris Phyllanthus sp
34.54 6.3 20.36 31.36 12.83 6.75 4.56 13.71 10.94 9.03 11.48 4.48
Acacia nilotica Solanum surratense Alhaji maurorom Eclipta alba Heliotropium sp Cyperus sp
13.23 10.64
Vegetation (Transect-03)
In this transect the data describes the equal distribution of the floral diversity including the trees, shrubs and herbs. The maximum plant species with highest IVI is the plant species Prosopis cineraria having the IVI value (84.32) with second highest specie is Cynadon dactylon with second highest IVI value (34.54) and third highest value of IVI is Desmostachya bipinnata with value of (31.36). The plant species with lowest IVI is Tribulus terestris having the lowest value of IVI i.e. (4.56). The sampled area has fair representation of trees, shrubs. The Tamarix dioica, Acacia nilotica and Prosopis cineraria are the commonly found tree species. Phyllanthus sp is the most commonly found shrubs in the sampled area. The herbs commonly found are Cynadon, Polygonum plebium, Desmostachya, and Phyla nodiflora. The IVI value of the plant species is mentioned in the table: 03.
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Site-01 (Kot Dingano forest) Transect-04
Table: 04
S.No
1.
Plant Species
Tamarix dioica
- IVI
- Community
50.13 Zizyphus-Tamarix-Desmostachya
Community
10.77 24.78 29.6 23.13
2. 3. 4. 5.
Prosopis cineraria Saccharum spontenaum Desmostachya bipinnata Acacia nilotica
6.
Phayllanthus sp
10.72
7. 8. 9. 10. 11. 12. 13. 14. 15.
Cynadon dactylon Zizyphus Mauritania Alhaji mauroram Chenopodium sp Calotropis procera Amaranthus viridis Heliotropium sp
20.52 59.41 10.89 14.76 4.72 11.79 11.81 6.83
Capparis deciduas Solanum surratense
10.1
Vegetation (Transect-04)
In this transect the data describes the equal distribution of the floral diversity including the trees, shrubs and herbs. The maximum plant species with highest IVI is the plant species Zizyphus Mauritania having the IVI value (59.41) with second highest specie is Tamarix dioica with second highest IVI value (50.13) and third highest value of IVI is Desmostachya bipinnata with value of (29.6). The plant species with lowest IVI is Calotropis procera having the lowest value of IVI i.e. (4.72). The sampled area has fair representation of trees, shrubs. The Tamarix dioica, Acacia nilotica and Prosopis cineraria are the commonly found tree species. Phyllanthus sp and Calotropis sp are the most commonly found shrubs in the sampled area. The herbs commonly found are Cynadon, Alhaji mauroram, Chenopodium, Amaranthus and Heliotropium sp. The IVI value of the plant species is given in the Table: 04
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3.2. Location-02 Lakhat Forest
GPS Data / Coordinates
GPS Points (Lakhat Forest)
- Location
- Coordinates/GPS
- Altitude
Lakhat Lakhat
N26 15.153 E68 01.605 N26 14.977 E68 01.832
127 ft 127 ft
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Site-2 (Lakhat Forest) Transect-01
Table-05
S.No
1.
Plant Species
Imperata cylindrica
- IVI
- Community
31.73 Zizyphus-Imperata-Melilotus
Community
2. 3. 4. 5. 6. 7. 8.
Anagalis arvensis Desmostachya bipinnata Melilotus indica Alhaji mauroram Carthamus oxycantha Chenopodium sp Sonchus asper
12.96 14.22 22.86 9.19 9.34 9.19 10.9
9.
Polygonum plebium Solanum nigrum Phlaris minor Zizyphus mauritania Acacia nilotica Launea procumbens Aerva javanica Citrullus colocynthis Calotropis sp
12.88
- 7.13
- 10.
11. 12. 13. 14. 15. 16. 17.
21.88 92.83 11.23 10.98 9.19 7.13 6.3
Vegetation (Transect-01)
In this transect the data describes the equal distribution of the floral diversity including the trees, shrubs and herbs. The maximum plant species with highest IVI is the plant species is Zizyphus mauritania having the IVI value (92.83) with second highest specie is Imperata cylindrica with second highest IVI value (31.73) and third highest value of IVI is Melilotus indica with value of (22.86).
The plant species with lowest IVI is Calotropis sp having the lowest value of IVI i.e. (6.3). The sampled area has fair representation of trees, shrubs. The Zizyphus Mauritania and Acacia nilotica are the commonly found tree species. Calotropis sp is the most commonly found shrubs in the sampled area. The herbs commonly found are Melilotus indica, Lzunea procumbens, Polygonum plebium, Phlaris minor,Imperata cylindrica, Citrullus colocynthis and Sonchus asper The IVI value of the plant species is given in the Table: 05
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Site-2 (Lakhat Forest) Transect-02
Table-06
S.No
1.
Plant Species
Euphorbia hirta
IVI 4.46
Community Acacia-Alhaji-Carthamus Community
2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14. 15.
Solanum surratense Aerva javanica Amaranthus viridis Cynadon dactylon Euhorbia prostrata Cyperus sp
11.33 11.56 5.93 15.11 14.33 18.55 93.29 40.9 26.78 26.55 11.33 5.7
Acacia nilotica Alhaji mauroram Carthamus oxycantha Phlaris minor Heliotropium sp Citrullus colocynthis Convolvulus arvensis Melilotus sp