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Research Article

Status of Flora in Chinji Forest Preserves

Muhammad Naeem, Salah-ud-Din Baber, Altaf-ur-Rehman Rao and M. Yasin Ashraf
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The present vegetal investigations were aimed at the National Park Reserves Chinji (Talagang). The area of the park was surveyed thoroughly and three study sites were selected in the park, keeping in view the following physiogeogrphic factors:

Nature of vegetation cover, density, frequency and coverage of plant species, species composition, water regimes, extent of desertification, level of salinity and sodicity, soil texture and structure, soil profile, topography. Following three plant communities in Chinji were recognized on the bases of importance value.

S1/Q1 Cynodon - Acacia - Dodonaea
S2/Q2 Cynodon - Dodonaea - Acacia
S3/Q3 Cynodon - Dodonaea - Eulaliopsis - Cymbopogon

The community of Q1, Q2 and Q3 comprised 19, 21 and 19 plant species respectively, out of which 5 in Q1 7 in Q2 and 6 in 03 got vanished during the second year. New colonizers were Eulaliopsis binata and Asparagus adscendens in Q1 and Eulaliopsis binata in Q3.

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  How to cite this article:

Muhammad Naeem, Salah-ud-Din Baber, Altaf-ur-Rehman Rao and M. Yasin Ashraf, 2000. Status of Flora in Chinji Forest Preserves. Pakistan Journal of Biological Sciences, 3: 876-880.

DOI: 10.3923/pjbs.2000.876.880



Geographical area of Pakistan is 79.6 m ha, out of which 26.3% is arid and semi-arid landmass and is being used for agriculture purposes (Anwar, 1997) which has failed to meet food and feed requirements. Increase in agriculture land is a target for Government to achieve self-sufficiency in food.

Government of Pakistan on the advice and encouragement of World Wild Fund (WWF), established 19 National Park Reserves in different ecological zones of the country on experimental basis. While embarking upon these establishments much importance was given to the heterogenity of the environments.

National Park Reserves at Chinji (Talagang, Chakwal) was chosen for the present investigations. The area of National Park Reserve Chinji is 6076 hectares (25007 acres) (Babar, 1996). Its altitude is 680 meters. It is situated in the heart of salt rang about 130 km from Islamabad in the south. Average annual rain is 537 mm out of which 308 mm during monsoon (July-September). Mean maximum temperature in the area is 27̊C in June and the mean minimum in January is 2.2̊C. Frost in the area is not uncommon during winter.

Maximum relative humidity percentage during monsoon is 80. Its deeply eroded landmass and is comprising of sandstone to igneous rocks, with deep torrential streams and raviness sloping sharply toward River Soan ultimately joining River Indus.

To achieve acceleration in agricultural productivity of these rangelands, one has to understand their flora particularly its density, frequency coverage and other related ecogeography, therefore, related benchmark data coupled with periodical increase or decreases in the structure of the endemic plant communities is the main aim of this investigation which can later be used by the planners, environmentalists and plant scientists.

Materials and Methods

The landscape of the National Park Chinji (Talagang) was physically surveyed to identify the desirable and appropriate study areas. To earmark these study ares the following physiographic factors were considered in detail before actually establishing the quadrates.

1. Nature of vegetation cover
2. Species composition
3. Density of plant species
4. Canopy cover
5. Frequency of plant species
6. Water regime
7. Extent of desertification
8. Soil texture
9. Level of salinity and sodicity
10. Soil structure
11. Soil profile
12. Topography
13. Special features, if any

To investigate the vegetation aspects in detail of the National Park Reserve (Chinji) three study sites (S1, S2 and S3) were selected at three different ecogeographical places. Because of inaccessibility, dangers involved and other factors it was planned to establish one large quadrat in each study site further subdividing that into five sub-quadrates as fallow.

Sites 51 S2 S3
Quadrat Q1 Q2 Q3
North q1 q6 q11
West q2 q7 q12
South q3 q8 q13
East q4 q9 q14
Central q5 q10 q15

S1 (Site 1) was chosen in the south-eastern side of Thatti Rest House at a distance of 2.0 km. On road of Jaba (5 km. south-east of Chinji) for establishing Q1.

Q1 with its 5 subquadrats, was demarcated in the site 1 (S1) near the road side on left hand side of Talagang-Sargodha road. It had a characteristic topography. The central most part of this quadrat was its highest point topographically and was gradually losing height in all directions. Reddish brown had stony pan formed the main bed of this quadrat where some narrow and shallow gullies were present. The largest number of fossilized parts of the trees were seen littered around on the surface as well as in the profiles of the rocks.

S2 (Site 2) was nearly 300 m deep gully in the east of Thatti Rest House and comprised a sharp sloping slippery and dangerous trail above the gully (water course). A piece of this quadrat was hummocked in the centre and was gradually sloping on all sides. In the south-west a rather flat piece of land lay there with sandy top.

Q2 (with five subquadrats) was ear marked in S2 towards the east of Thatti Rest House. It was bordered by badly eroded hillocks from all the four sides. Its bottom comprised 17.0 m wide dry water coarse and the meeting point of two small ditches with bedded sand. A 15.0 m high hillock slightly away from its centre formed the most vegetated part of this quadrat.

S3 (Site 3) was selected in an open unfenced area on the right side of Talagang-Sargodha Road about 500 m in the western side of Thatti Rest House. The flat soil surface was rocky to sapstony with some minor land sliding here and there. It was the pasture closest to the locality therefore, the utilization of the plant resources was the maximum. This area was highly elevated than other two sides, and a watch tower was erected by the wild life department.

Q3 quadrat was earmarked in S3, 100 m. away from TalagangSargodha road. It was slowly sloping and eroded surface facing north-east and south-east sides with some trapped soil and sand particles including sandstones. The soil was sandy, compact and hard, just like compacted cement. A pool of rain water lay close to the border of this quadrat serving as a water point in this water scarcity area for the grazier. This quadrat was further divided into five subquadrats.

Collection of Data: Data on quantitative phytosociological attributes such as frequency, density and plant cover were recorded in each subquadrat periodically, these three characteristics of the community are necessary for complete analysis of vegetation. Where vegetation offers difficulty in measuring density then reliance may be made upon the remaining two criteria (Hussain, 1989). Relative frequency, relative density, relative cover, importance value and status of the species were calculated by following method described by Mueller-Dombois and Ellenberg (1974) and Babar (1996).

Difference among the sites and habitats: Variations among the sites such as sloe, topography, water regime, soil texture and structure, apparent salinity and sodacity, decertification and soil profile levels were recorded visually. Altitude of the quadrats was noted with altimeter. Special features of sites and vegetation were also recorded where necessary.


Data were recorded thrice in a year but the ones were recorded after the monsoon appeared important thus are listed below. The following three plant communities were recognized in National Forest Reserve Chinji at three study sites (S1, S2 and S3) in both the years.

S1/01 1st Year Cynodon-Acacia-Dodonaea
  2nd Year Cynodon-Dodonae-Acacia
S2/Q2 1st Year Cynodon-Dodonaea-Acacia
  2nd Year Cynodon-Dodonaea-Acacia
S3/03 1st Year Cynodon-Moss-Dodonaea
S1/Q3 (First Year) Cynodon-Acacia-Dodonaea

Cynodon dactylon, Acacia modesta and Dodonaea viscose having importance values of 82.81, 52.16 and 42.41 emerged as the dominant species in Q1 (Table 1). Moss, Olea cuspidata and Gymnosporia royleana with importance value as 29.83, 26.84 and 22.53 respectively were found frequent.

Grewia tenax was ommon with importance value 15.74, Otostegia limbata, Desmotachya bipinnate, Eragrostis tremula, Lichen, Cymbopogon jwarancusa and Saliva aegyptiaca were infrequent with importance values 7.20, 5.40, 5.30, 4.50, 4.37 and 3.12 while Chrysopogon plumolosus and Argyrolobium roseum were rare with the importance values of 2.82 and 2.51 however, the rarest species was Periploca aphylla showing a value of 2.46.

Table 1:Species composition and their phytosociolooical values in Q1 (Fenced) at National Park Chinji
*R.D = Relative density; R.F = Relative frequency, R.0 = Relative coverage **Values in Italics pertain to second year

Table 2: Species composition and their Phvtosociolooical values in Q2 (Fenced) at National Park Chinji

Second Year
Cynodon-Dodonaea-Acacia Community:
During in its species composition as well as their importance values Cynodon dactylon, Dodonaea viscosa and Acacia modesta respectively having 101.32, 65.16 and 24.75 importance values were dominating in the fenced area. Gymnosphoria royleana was frequent with 21.44 importance value. Cenchrus pennisetiformis, Olea cuspidata, Grewia tenax and Cymbopogon jwarancusa were common with 19.32, 17.66, 16.49 and 10.11 importance values respectively. Eulaliopis binata, Periploca aphylla and Otostegia limbata were infrequent with importance values 8.82, 4.82, 4.50. Eragrostis tremula and Asparagus adscendens were the rarest members with importance values as 2.78 and 2.53 respectively.

S2/Q2 (First Year): This community was charaqcterised by the dominance of Cynodon dactylon, Dodonaea viscosa and Acacia modesta having 100.23, 46.69 and 24.10 as the importance values respectively in Q2 (Table 2). Lantana camara, Gymnosporia royleana, Grewia tenax and Prosopsis cineraria were common showing 15.92, 13.51, 13.32 and 10.63 their importance values. Olea cuspidata, Acacia nilotica, Tamarix troupii, Eragrostis tremula, Dichanthium annulatum, Otostegia limbata, Tavernthra cuneifolia and Fagonia cretica were infrequent with importance values as 9.83, 9.40, 9.11, 5.79, 5.06, 4.56, 4.01 and 3.07 respectively, while Saccharum munja, Zizyphus jujba, Plantago ovata, Asparagus adscendens, Diclyptra roxbergii and Saussuria candicous were found to be rare members with importance values as 2.57, 2.57, 2.40, 2.31, 2.25 and 2.25 respectively.

Second Year
Cynodon-Dodonaea-Acacia Community:
During the second year in 02, this community was characterised by the dominance of Cynodon dactylon, Dodonaea viscose and Acacia modesta having importance values as 105.83, 45.44 and 39.98 respectively, Cenchrus pennisetiformis was associated with 37.85 importance value. Grewia tenax, Olea cuspidata, Prosopis cineraria and Tamarix troupii were common with the importance values 13.62, 13.27, 10.64 and 10.39 respectively. Otostegia limbata, Lantana camara, Acacia jacquemontii, Cymbopogon jwarancusa, Acacia nilotic and Farsetia hamiltoni were infrequent with 9.26, 6.54, 6.54, 4.40, 3.95 and 3.06 importance values respectively. Fagonia cretica, Saccharum munja, Gymnosporia royleana and Zizyphus jujuba were rare members with 2.99, 2.86, 2.68 and 2.66 importance values respectively.

S2/Q3 (First year)
Cynodon-Moss-Dodonaea-Acacia Community:
This community was characterised by the dominance of Cynodon dactylon, Moss, Dodonaea viscosa and Acacia modesta having importance values as 54.42, 36.39, 30.95 and 29.79 respectively in Q3 (Table 3). The frequent species were Otostegia limbata and Gymnosporia royleana with importance values as 28.57 and 26.17 Olea cuspidata. Grewia tenax and Lantana camara were common depicting 17.61, 12.88 and 11.13 as their importance values.

Table 3:Species composition and their phytosocioloqical values in 03 (un-fenced) at National Park Chinji

Argyrolobium roseum, Prosapis cineraria. Cymbopogon jwarancusa, Capparis decidua, Chrysopogon plumolosus, Periploca aphylla and Solarium incanum were infrequent with 9.80, 8.85, 6.45, 5.39, 3.55 and 3.35 as their importance values respectively, while Eragrostis tremula and Pupalia japanica were rare members with importance values as 2.87 and 2.50.

Second Year
Cynodon-Eulaliopsis-Cymbopogon Community:
During the second year this community showed a big change. Cynodon dactylon, Eulaliopsis binata and Cymbopogon jwarancusa having importance values 59.56, 49.82 and 49.00 respectively were dominating. Dodonaea viscose was associated with a value of 36.36 importance value. Acacia modesta, Otostegia limbata and Olea cuspidata were frequent with importance values as 34.95, 32.69 and 26.08 respectively.

Solarium incanum, Heteropogon centortus, Cenchrus ciliaris, Gymnosporia royleana, Lantana camara and Gxewia tenax were common with importance values 16.64, 16.48, 16.10, 14.90, 12.44 and 10.71 respectively. Prosopis cineraria, Periploca aphylla, Trianthema crystallima, Aristida depressa and Asparagus adscendens were infrequent with importance values as 9.33, 5.94, 5.40, 4.31 and 4.04 respectively, while Farsetia hamlltoni and Chenopodium album were rare members having 2.41 and 2.21 importance values.


The scenario of species in National Park Chinji is presenting a though provoking aspect if considered habitat wise or the community wise. The species composition in each table is variable showing that the efforts made to lay down the quadrats were by and large correct. On the other hand the species status is varying from habitat to habitat as well as their status.

This is important to note that the picture of major species available in the area though remain the same but very conspicuous and varied differences are noticeable, specifically when the relative values of density, frequency or coverage are considered. Imtiaz-ul-Haq and Zia-ud-Din (1982) expressed similar views while describing the vegetation of Nowshera.

Important physiographic factors namely rain fall and its associated impacts like dryness, landslide etc. were noted on the spot but not frequently. Land sliding was quite common in 02 and 03. On the contrary, efforts were underway to check the severity of soil erosion by slowing down the speedy running off water through the construction of checkdams. Over exploitation of plant resources in 02 and 03 also changed the status of vegetation to a great extent. Perennial dominating species Acacia modesta was cut and consumed, got reduced in relative value in Q1. Chaghtai and Yusaf (1976) reported dominance of this species in Kohat and later met the same fate. This is quite clear to note that all the three quadrats were distinct and endemic plant communities depicted quite good differing aspects.

The community in Q1 comprised of 19 species where 4 species got vanished during the second year, particularly Salvia aegyptiaca, Chrysopogon plumolosus and Argyrolobium roseum. However, three species namely Cenchrus ciliaris, Eulaliopsis binata and Asparagus adscendens were the new colonizers, but in low densities. With the erosion of fence, grasses increase their densities; new corners were increasing at the cost of undesirable species like Dodonaea viscose; but as expected they increased their coverage and importance values significantly. The change of the status from subdominant to dominant and so on was also noted among some species.

The site Q2 followed the same pattern as given above. The richness of species was higher in this quadrat numberirig 21. The interesting feature of this quadrat was in line with the previous one where palatable grass Cynodon dactylon increased its density and importance value assuming the dominant status in both the years. This is particularly important to note that some species disappeared from the quadrat during the second year due to land sliding and there were no new colonizer, apparently due to erosion and washing away of the seed by the speedy running off water. Dodonaea viscose and Lantana camaxa etc. were reduced in their densities and importance values.

The pattern of change in 03 did not present a big departure from the above listed quadrats. All the 19 species of this quadrat showed a change over the years in their densities and importance values, though it was very minor except the Cynodon dactylon. Five species disappeared during the second year but the Eulaliopsis binata was the fresh arrival during the second year. Disappearance of Capparis decidua a perennial may be because of feeling by the locals from this unfenced habitat.

Since very wide and very deep gullies have now been formed, therefore small to big checkdams have become absolutely necessary for the preservation of the area particularly when the fences have been erected, this will bring about quick and desirable results over a short periods of time. Ahmed (1988) along the way of Gilgit to Chiles reported similar occurrences.

1:  Anwar, M., 1997. Geography of Pakistan. Whiterose Publishers, Lahore, Pakistan.

2:  Babar, S.D., 1996. Status of flora in Chinji and Cholistan forest preserves. M.Phil. Thesis, University of Agriculture, Faisalabad, Pakistan.

3:  Chaghtai, S.M. and M. Yusaf, 1976. Ecology of the native vegetation of Kohat, NWFP, Pakistan. Pak. J. Bot., 8: 27-36.

4:  Hussain, H., 1989. Phytosociological studies on coastal dunes around Karachi. M.Sc. Thesis, University of Karachi, Karachi, Pakistan.

5:  lmtiaz-ul-Haq and Zia-ud-Din, 1982. Phytosociological studies of Shaidu Hills (Nowshera) district Peshawar: An approach to some problems in plants. Proceedings of the 1st Regional Conference of Plant Scientists, April 24-26, 1982, University of Peshawar, Peshawar, Pakistan, pp: 71-76.

6:  Ahmed, M., 1988. Plant communities of some Northern temperate forests of Pakistan. Pak. J. For., 38: 33-40.

7:  Mueller-Dombois, D. and H. Ellenberg, 1974. Aims and Methods of Vegetation Ecology. 1st Edn., John Wiley and Sons, New York, USA., ISBN-13: 978-0471622901, Pages: 570.

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