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Journal of Medicinal Plants Research Vol. 5(4), pp. 599-603, 18 February, 2011

Available online at http://www.academicjournals.org/JMPR

ISSN 1996-0875 ©2011 Academic Journals

Read About Deosai Plais Read About Sheosar Lake


                                  Full Length Research Paper

 Vegetation types of Sheosar lake and surrounding landscape in Deosai plains of
                      North Pakistan, Western Himalayas

                         Hamayun Shaheen* and Rizwana Aleem Qureshi



            Department of Plant Sciences, Quaid-i-azam University Islamabad, Pakistan.



                                   Accepted 19 January, 2011



Sheosar Lake is located in Deosai plains of great Himalayas, Northern Pakistan at an altitude of
4142 m. Due to its exiting and isolated geographic location and diverse climatic conditions, area
harbors very peculiar, highly endemic and unique vegetation. Phytosociological expeditions were
carried out to study the vegetation dynamics of the area. A total of 114 plant species belonging to
28 families were reported from the area. Carex-Geranium-Bistorta and Sibbaldia-Saxifraga-
Eragrostis communities were found to be the dominant associations. Primary data was analyzed
by deterrended correspondence analyses (DCA) which revealed strong correlation between
vegetation distribution and the moisture gradient. Regular and integrated explorations are further
recommended for conservation management of endemic flora.



Key words: Deosai plains, deterrended correspondence analyses, Himalayas, Sheosar Lake,
vegetation

dynamics.
INTRODUCTION



The Himalayas constitute one of the richest and most unusual ecosystems on earth. The
Himalayan alpine areas are characterized by low productivity, high intensity of solar radiation
and high degree of resource seasonality. The vegetation of this fragile biome is adapted to the
extreme conditions occurring with sparse populations. Himalayan high altitude grazing pastures
are very important being a wild life habitat, water catchment and a livelihood source for nomadic
and transhumant inhabitants. The community structure and distribution patterns of Himalayan
forests and alpine pastures have not been given due attention till the date by the plant ecologists,
and hence poorly understood (Peer et al.,

2007). The distribution and community structure of alpine vegetation is governed by adverse
edaphic and climatic factors; mainly by rainfall and redistribution of water that decrease with the
increase in altitude. Temperature is also one of the most important limiting factors controlling
the distribution and community structure of Himalayan vegetation. Here the altitude has much
greater effect on temperature than latitude. Mean annual temperature decrease with increase in
elevation, more rapidly in summer than in winter. This altitude based temperature gradient is the
vital factor shaping the vegetation types and determining their diversity and distribution (Heaney
and Proctor, 1989; Tanner et al., 1998; Vazquez and Givnish, 1998).



Alpine areas are characterized by scanty rainfall, high ultraviolet (UV) radiation, high wind
velocity, blizzards, low temperature and snowstorms. The plants of this zone show an adaptation
to these conditions and are generally dwarfed, stunted, wooly or spiny, and develop a mosaic
patch of different forms. They possess an early growth initiation with a short vegetative span
ranging from several days to a few months. The community as a whole usually exhibits seasonal
fluctuations, and its structure and composition are strongly influenced by the extent to which
periodic phenomena in the individuals are adjusted to each other (Kershaw, 1973). In Pakistan,
alpine pastures cover 1050,000 hectares, which makes 1% of country area lying between snow
and tree line at an average altitudinal range of 2500 to 4000 m 600            J. Med. Plant. Res.
(Sardar, 1997). These pastures are used for grazing during March-April to September–October
and for rest of the time these remain under snow. Western Himalayan pastures are severely
degraded due to nomadic and sedentary livestock overgrazing. Due to huge population increases
and frighteningly increasing urbanization practices, existing reserve forests and grazing lands are
overburdened with community rights making it impossible to reduce the grazing pressure
(Gupta, 1970, 1977). Grazing practices are one of theimportant determinants of vegetation
distribution patterns and having most obvious impact on the floral biodiversity of an area
(Vallentine, 2001). Many researchers (Vigne, 1842; Duthie, 1892; Stewart, 1961; Dickore, 1995;
Negi, 1995; Sardar, 1997; Stainton, 1998; Shinwari and Gillani, 2002)
have studied different aspects of vegetation structure and distribution patterns in alpines of
western Himalayas. Phytosociology or plant sociology is an invaluable method for vegetation
survey and assessment involving investigation of characteristics of plant communities using
simple and rapidly employing field techniques (Rieley and Page, 1990). In the present study, an
effort has been made to investigate and analyse correlation of vegetative attributes with key
environmental factors using the

multivariate analyses techniques.



MATERIALS AND METHODS

The study area lies in Deosai plains in the great Himalayan range, Northern Pakistan. The area is
uninhabited grassy plateau with an average altitude of 411m. The Sheosar Lake is situated at an
elevation of 4,142 m having length 2.3 km, width 1.8 km (1.2 miles) and average depth 40 m.
Area exhibits very harsh climatic conditions having long and severe snowy winters from October
to May. In whole winter area remains snow covered and temperatures always below the freezing
point. It has a very short growing spring season from May to July. The study area has very
unique geographic location lying between the western Himalayan massif and Karakoram range
covering 1400 km². Deosai is also called „Roof of the earth‟ and „the land of Giants‟ . The
phytosociological expeditions were carried out in the JuneJuly, 2008 to the Deosai plains. Line
transect method was used to study and analyse the vegetation dynamics as well as to collect the
primary data for statistical analyses. Transects were laid in selected sites having best
representation of floral biodiversity and geographic extent of the area. A total of 15 transects, 10
m each were laid in the study area. Vegetation attributes including frequency, density, cover and
richness were recorded along with environmental coordinates like latitude, longitude, altitude
and slope using GPS. Plants from the premises of sampling points as well as isolated vegetation
patches were also collected to record maximum number of species and their distribution patterns.
Collected samples were pressed, dried and transported to herbarium of Quaid-I-Azam University
Islamabad, Pakistan, where they were identified and classified following Stewart (1961) and
Nasir and Ali (1972). Deterrended correspondence analyses (DCA) was applied to the species
abundance data by using reciprocal averaging ordination (Hill, 1980). The primary data
regarding species cover and abundance was analyzed to determine natural plant associations as
well as to measure the variations in dynamics and distribution of species.



RESULTS AND DISCUSSION

A total of 114 species belonging to 28 families were recorded during the field expeditions.
Compositeae was the leading representative of local flora comprising 13.15% of cover followed
by Ranunculaceae with 10.52%. Cruciferae, Gramineae, Leguminosae, Scrophulariaceae,
Apiaceae and Polygonaceae were the co dominant families in the study area.The study area
represented a mosaic of meadow, open scree, scrub and rock vegetation types. Rich soil moisture
with cold climate has resulted in the accumulation of rich humus layers enabling tall
hygrophilous forbs like Aconogonon, Gentiana and Geranium to grow along with smaller herbs
like Vicatia, Sibbaldia and Pedicularis. Saussurea, Androsace, Rhodiola, Saxifraga, Myosotis,
Erigeron, Draba, Trollius, Thalictrum, Potentilla, Carex Oxytropis, Ranunculus, Leontopodium
and Chorispora were the dominant species making the major framework of community structure
and distribution.



The distribution of vegetation is controlled by complex edaphic, climatic and anthropogenic
factors like exposure, humidity and grazing intensity. Salix and Primula populations were mainly
confined to permanently moist, snow covered trails. Scrub and dwarf scrub "Krummholz" of
Salix karelinii were found to be attaining a height up to 100 cm mostly covering the North facing
slopes having low grazing pressure. South facing slopes represented much drier conditions and a
greater grazing intensity, mostly colonized by chamaephytes and drought resistant herbs like
Bistorta affinis, Elymus, Silene, Oxytropis and Rhodiola. The intermediate rocky slopes were
characterized by open scree plant communities. The two major plant associations developed as a
result of species data analyses were as follows:



Carex cruenta – Geranium himalayense – Bistorta affinis community

The dominant species included C. cruneata and G. himalayense with indicator species B. affinis
and Rosularia rosulata. This association was a characteristic feature of most North facing slopes
having maximum soil moisture and less grazing intensity.



Sibbaldia cunneata–Saxifraga flagellaris– Eragrostis community



This plant community was dominated by Sibbaldia and Saxifraga species exclusively growing in
crevices and low moisture places. Avena fatua and Leontopodium were among the indicator
species of this community.



Detrended correspondence analysis

DCA results showed very clear and understandable distribution of vegetation communities along
DCA axis 1. The three positively valued communities were aggregated on the left separated from
the CarexGeranium-Bistorta community at the right. The 1st axis indicates soil moisture gradient
as the major limiting factor controlling the structure and distribution of plant communities. The
aggregation of communities in the drier region can be easily interpreted to support the
assumption (Malik and Husain, 2006). Community distribution trend along the DCA axis 2 is not
clear as several edaphic and biotic factors appear to be acting together. The species composition
of Carex-GeraniumBistorta found atmesic site showed negative correlation with the moisture
gradient, whereas other plant associations were restricted to drier area.



Chorological spectrum



The chorological spectrum of Sheosar lake flora revealed the lowest proportion of
cosmopolitan species (<5%) 2 Axis 1 where as Eurasiatic elements were the top ones (27%).
The endemic to Hindukush Himalayan members made 15% of the total local flora (Figure 3).
Centrasiatic and Sino-Himalayan elements showed medium trends. Minor proportions of flora
showed affiliations with IranoTuranian, Tibetan, Mediterranean and Circumpolar regions
representing a high degree of endemism.




CONCLUSION AND RECOMMENDATIONS

The area still needs very detailed and comprehensive investigations regarding different
vegetative attributes and their correlation with environmental as well as anthropogenic variables.
A single study can not serve the whole purpose in such a large, diverse and geographically
important area. Repeated and integrated explorations are recommended in all parts of Deosai
plateau to explore the dynamic and variations in floral biodiversity. Grazing practices need to be
limited and monitored along with creating the awareness among the grazers about conservation
and sustainable management of grasslands. Fenced vegetation plots should be designed at
regular intervals to act as seed banks in



602      J. Med. Plant. Res.



Number of species

Number of species whole plateau. Grazing practices should be synchronized with plant growth
seasons so that damage to vegetation during flowering stage can be avoided. A great deal can
be done about the ethnobotanical application of the local flora by identifying, investigating and
evaluating the utilization practices of local folklore. The most important point to be considered
is conservation of endemic flora, which has its restricted distribution in the study area and is
posed with severe threats due to overexploitation by grazing, medicinal plant harvest and harsh
environmental conditions.



REFERENCES

Dickore WB, Nusser M (2000). Flora of Nanga Parbat (N.W Himalaya,

Pakistan). An Annotated inventory of vascular plants with remarks on

vegetation dynamics. Englera, 19: 1-253

Duthie JF (1906). Catalogue of the Plants of Kumaon and Adjacent

portions of Garhwal and Tibet Based on the Collections made by

Strachey and Winterbottom during the Years 1846–1849, Lovell

Reeve and Co, Ltd, London.

Gupta RK, PC Nanda (1970). Grassland types and their ecological

succession in Western Himalaya. Proc. Intern. Grassland Congr., pp.

10-13.

Gupta RK (1977). Energy Forests on Farm and Community Lands - N.

W. Himalayan region. Indian Farming, 26(11): 84-86.

Heaney A, J Proctor (1989). Chemical elements in fitter at a range of

altitude on Volcan barva, costa Rica: Nutrients in Tropical Forest and

Sawanna Ecosystems. (Ed.): J. Proctor. Blackwell Scientific

publications, Oxford, pp. 255-271.

Hill MO, HG Gauch (1980) Detrended correspondence analysis: an

improved ordination technique. Vegetation, 42: 47-58.

Kershaw RA (1973). Quantitative and Dynamic Plant Ecology. London:

Edward Arnold.
Malik RN, SZ Husain (2006). Classification and ordination of vegetation

communities of the Lohibehr reserve forest and its surrounding areas,

Rawalpindi. Pak. J. bot., 38(3): 543-558.

Nasir E, SI Ali (1972) Flora of West Pakistan. An annotated catalogue of

vascular plants of West Pakistan and Kashmir.

Shaheen and Qureshi         603

Negi SS (1995). Cold deserts of India. Indus Publishing Company, New

Delhi.

Peer T, JP Gruber, Millingard A, Hussain F (2007) Phytosociology,

structure and diversity of the steppes vegetation in the mountains of

Northern Pakistan. Phytocoeno., 37: 1-65.

Rieley J, Page S (1990) Ecology of plant communities: A

phytosociological account of the British Vegetation. John Wiley and

sons, Inc., New York, p. 178.

Sardar MR (1997). Indigenous Production and Utilization Systems in the

High Altitude Alpine Pastures, Saif-ul-Maluk (NWFP), Pakistan, PFI,

Peshawar, p. 47.

Shinwari ZK, SS Gilani, Khan AA (2002). “Wise-practices and

experiential learning in the conservation and management of

Himalayan medicinal plants” In the regional workshop held at

Kathmandu, Nepal from 15 – 20th December 2002.

Stainton A (1998). Flowers of the Himalaya. A Supplement, Oxford

University Press.
Stewart RR (1961). The Flora of Deosai plains. Pak. J. For., 11: 225295



Tanner EVJ, PM Vitousek, Cuevas E (1998). Experimental investigation

of nutrient limitation of forest growth on wet tropical mountains. Ecol.,

79: 10-22.

Vallentine JF (2001). Grazing Management. Academic Press, San

Diego/San Francisco/New York/Boston/London/Sydney/Tokyo.

Vazquez JAG, Givnish TJ (1998). Altitudinal gradients in tropical forest

composition, structure and diversity in the sierra de Manantlan,

Jalisco, Mexico. J. Ecol., 86: 999-1020.

Vigne GT (1842). Travelsin Kashmir, Ladakh,I scardo, theC ountries

Adjoining the Mountain-courseo f the Indus, and the Himalaya, North

of the Panjab. 2 Vols. H. Colburn, London.

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Journal of medicinal plants research vol

  • 1. Journal of Medicinal Plants Research Vol. 5(4), pp. 599-603, 18 February, 2011 Available online at http://www.academicjournals.org/JMPR ISSN 1996-0875 ©2011 Academic Journals Read About Deosai Plais Read About Sheosar Lake Full Length Research Paper Vegetation types of Sheosar lake and surrounding landscape in Deosai plains of North Pakistan, Western Himalayas Hamayun Shaheen* and Rizwana Aleem Qureshi Department of Plant Sciences, Quaid-i-azam University Islamabad, Pakistan. Accepted 19 January, 2011 Sheosar Lake is located in Deosai plains of great Himalayas, Northern Pakistan at an altitude of 4142 m. Due to its exiting and isolated geographic location and diverse climatic conditions, area harbors very peculiar, highly endemic and unique vegetation. Phytosociological expeditions were carried out to study the vegetation dynamics of the area. A total of 114 plant species belonging to 28 families were reported from the area. Carex-Geranium-Bistorta and Sibbaldia-Saxifraga- Eragrostis communities were found to be the dominant associations. Primary data was analyzed by deterrended correspondence analyses (DCA) which revealed strong correlation between vegetation distribution and the moisture gradient. Regular and integrated explorations are further recommended for conservation management of endemic flora. Key words: Deosai plains, deterrended correspondence analyses, Himalayas, Sheosar Lake, vegetation dynamics.
  • 2. INTRODUCTION The Himalayas constitute one of the richest and most unusual ecosystems on earth. The Himalayan alpine areas are characterized by low productivity, high intensity of solar radiation and high degree of resource seasonality. The vegetation of this fragile biome is adapted to the extreme conditions occurring with sparse populations. Himalayan high altitude grazing pastures are very important being a wild life habitat, water catchment and a livelihood source for nomadic and transhumant inhabitants. The community structure and distribution patterns of Himalayan forests and alpine pastures have not been given due attention till the date by the plant ecologists, and hence poorly understood (Peer et al., 2007). The distribution and community structure of alpine vegetation is governed by adverse edaphic and climatic factors; mainly by rainfall and redistribution of water that decrease with the increase in altitude. Temperature is also one of the most important limiting factors controlling the distribution and community structure of Himalayan vegetation. Here the altitude has much greater effect on temperature than latitude. Mean annual temperature decrease with increase in elevation, more rapidly in summer than in winter. This altitude based temperature gradient is the vital factor shaping the vegetation types and determining their diversity and distribution (Heaney and Proctor, 1989; Tanner et al., 1998; Vazquez and Givnish, 1998). Alpine areas are characterized by scanty rainfall, high ultraviolet (UV) radiation, high wind velocity, blizzards, low temperature and snowstorms. The plants of this zone show an adaptation to these conditions and are generally dwarfed, stunted, wooly or spiny, and develop a mosaic patch of different forms. They possess an early growth initiation with a short vegetative span ranging from several days to a few months. The community as a whole usually exhibits seasonal fluctuations, and its structure and composition are strongly influenced by the extent to which periodic phenomena in the individuals are adjusted to each other (Kershaw, 1973). In Pakistan, alpine pastures cover 1050,000 hectares, which makes 1% of country area lying between snow and tree line at an average altitudinal range of 2500 to 4000 m 600 J. Med. Plant. Res. (Sardar, 1997). These pastures are used for grazing during March-April to September–October and for rest of the time these remain under snow. Western Himalayan pastures are severely degraded due to nomadic and sedentary livestock overgrazing. Due to huge population increases and frighteningly increasing urbanization practices, existing reserve forests and grazing lands are overburdened with community rights making it impossible to reduce the grazing pressure (Gupta, 1970, 1977). Grazing practices are one of theimportant determinants of vegetation distribution patterns and having most obvious impact on the floral biodiversity of an area (Vallentine, 2001). Many researchers (Vigne, 1842; Duthie, 1892; Stewart, 1961; Dickore, 1995; Negi, 1995; Sardar, 1997; Stainton, 1998; Shinwari and Gillani, 2002)
  • 3. have studied different aspects of vegetation structure and distribution patterns in alpines of western Himalayas. Phytosociology or plant sociology is an invaluable method for vegetation survey and assessment involving investigation of characteristics of plant communities using simple and rapidly employing field techniques (Rieley and Page, 1990). In the present study, an effort has been made to investigate and analyse correlation of vegetative attributes with key environmental factors using the multivariate analyses techniques. MATERIALS AND METHODS The study area lies in Deosai plains in the great Himalayan range, Northern Pakistan. The area is uninhabited grassy plateau with an average altitude of 411m. The Sheosar Lake is situated at an elevation of 4,142 m having length 2.3 km, width 1.8 km (1.2 miles) and average depth 40 m. Area exhibits very harsh climatic conditions having long and severe snowy winters from October to May. In whole winter area remains snow covered and temperatures always below the freezing point. It has a very short growing spring season from May to July. The study area has very unique geographic location lying between the western Himalayan massif and Karakoram range covering 1400 km². Deosai is also called „Roof of the earth‟ and „the land of Giants‟ . The phytosociological expeditions were carried out in the JuneJuly, 2008 to the Deosai plains. Line transect method was used to study and analyse the vegetation dynamics as well as to collect the primary data for statistical analyses. Transects were laid in selected sites having best representation of floral biodiversity and geographic extent of the area. A total of 15 transects, 10 m each were laid in the study area. Vegetation attributes including frequency, density, cover and richness were recorded along with environmental coordinates like latitude, longitude, altitude and slope using GPS. Plants from the premises of sampling points as well as isolated vegetation patches were also collected to record maximum number of species and their distribution patterns. Collected samples were pressed, dried and transported to herbarium of Quaid-I-Azam University Islamabad, Pakistan, where they were identified and classified following Stewart (1961) and Nasir and Ali (1972). Deterrended correspondence analyses (DCA) was applied to the species abundance data by using reciprocal averaging ordination (Hill, 1980). The primary data regarding species cover and abundance was analyzed to determine natural plant associations as well as to measure the variations in dynamics and distribution of species. RESULTS AND DISCUSSION A total of 114 species belonging to 28 families were recorded during the field expeditions. Compositeae was the leading representative of local flora comprising 13.15% of cover followed by Ranunculaceae with 10.52%. Cruciferae, Gramineae, Leguminosae, Scrophulariaceae, Apiaceae and Polygonaceae were the co dominant families in the study area.The study area represented a mosaic of meadow, open scree, scrub and rock vegetation types. Rich soil moisture with cold climate has resulted in the accumulation of rich humus layers enabling tall
  • 4. hygrophilous forbs like Aconogonon, Gentiana and Geranium to grow along with smaller herbs like Vicatia, Sibbaldia and Pedicularis. Saussurea, Androsace, Rhodiola, Saxifraga, Myosotis, Erigeron, Draba, Trollius, Thalictrum, Potentilla, Carex Oxytropis, Ranunculus, Leontopodium and Chorispora were the dominant species making the major framework of community structure and distribution. The distribution of vegetation is controlled by complex edaphic, climatic and anthropogenic factors like exposure, humidity and grazing intensity. Salix and Primula populations were mainly confined to permanently moist, snow covered trails. Scrub and dwarf scrub "Krummholz" of Salix karelinii were found to be attaining a height up to 100 cm mostly covering the North facing slopes having low grazing pressure. South facing slopes represented much drier conditions and a greater grazing intensity, mostly colonized by chamaephytes and drought resistant herbs like Bistorta affinis, Elymus, Silene, Oxytropis and Rhodiola. The intermediate rocky slopes were characterized by open scree plant communities. The two major plant associations developed as a result of species data analyses were as follows: Carex cruenta – Geranium himalayense – Bistorta affinis community The dominant species included C. cruneata and G. himalayense with indicator species B. affinis and Rosularia rosulata. This association was a characteristic feature of most North facing slopes having maximum soil moisture and less grazing intensity. Sibbaldia cunneata–Saxifraga flagellaris– Eragrostis community This plant community was dominated by Sibbaldia and Saxifraga species exclusively growing in crevices and low moisture places. Avena fatua and Leontopodium were among the indicator species of this community. Detrended correspondence analysis DCA results showed very clear and understandable distribution of vegetation communities along DCA axis 1. The three positively valued communities were aggregated on the left separated from the CarexGeranium-Bistorta community at the right. The 1st axis indicates soil moisture gradient as the major limiting factor controlling the structure and distribution of plant communities. The aggregation of communities in the drier region can be easily interpreted to support the assumption (Malik and Husain, 2006). Community distribution trend along the DCA axis 2 is not
  • 5. clear as several edaphic and biotic factors appear to be acting together. The species composition of Carex-GeraniumBistorta found atmesic site showed negative correlation with the moisture gradient, whereas other plant associations were restricted to drier area. Chorological spectrum The chorological spectrum of Sheosar lake flora revealed the lowest proportion of cosmopolitan species (<5%) 2 Axis 1 where as Eurasiatic elements were the top ones (27%). The endemic to Hindukush Himalayan members made 15% of the total local flora (Figure 3). Centrasiatic and Sino-Himalayan elements showed medium trends. Minor proportions of flora showed affiliations with IranoTuranian, Tibetan, Mediterranean and Circumpolar regions representing a high degree of endemism. CONCLUSION AND RECOMMENDATIONS The area still needs very detailed and comprehensive investigations regarding different vegetative attributes and their correlation with environmental as well as anthropogenic variables. A single study can not serve the whole purpose in such a large, diverse and geographically important area. Repeated and integrated explorations are recommended in all parts of Deosai plateau to explore the dynamic and variations in floral biodiversity. Grazing practices need to be limited and monitored along with creating the awareness among the grazers about conservation and sustainable management of grasslands. Fenced vegetation plots should be designed at regular intervals to act as seed banks in 602 J. Med. Plant. Res. Number of species Number of species whole plateau. Grazing practices should be synchronized with plant growth seasons so that damage to vegetation during flowering stage can be avoided. A great deal can be done about the ethnobotanical application of the local flora by identifying, investigating and evaluating the utilization practices of local folklore. The most important point to be considered is conservation of endemic flora, which has its restricted distribution in the study area and is
  • 6. posed with severe threats due to overexploitation by grazing, medicinal plant harvest and harsh environmental conditions. REFERENCES Dickore WB, Nusser M (2000). Flora of Nanga Parbat (N.W Himalaya, Pakistan). An Annotated inventory of vascular plants with remarks on vegetation dynamics. Englera, 19: 1-253 Duthie JF (1906). Catalogue of the Plants of Kumaon and Adjacent portions of Garhwal and Tibet Based on the Collections made by Strachey and Winterbottom during the Years 1846–1849, Lovell Reeve and Co, Ltd, London. Gupta RK, PC Nanda (1970). Grassland types and their ecological succession in Western Himalaya. Proc. Intern. Grassland Congr., pp. 10-13. Gupta RK (1977). Energy Forests on Farm and Community Lands - N. W. Himalayan region. Indian Farming, 26(11): 84-86. Heaney A, J Proctor (1989). Chemical elements in fitter at a range of altitude on Volcan barva, costa Rica: Nutrients in Tropical Forest and Sawanna Ecosystems. (Ed.): J. Proctor. Blackwell Scientific publications, Oxford, pp. 255-271. Hill MO, HG Gauch (1980) Detrended correspondence analysis: an improved ordination technique. Vegetation, 42: 47-58. Kershaw RA (1973). Quantitative and Dynamic Plant Ecology. London: Edward Arnold.
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