Fateme Ardalan, Maziar
Haidari, Khabat Janati, Jahedeh Tekyekha, Soma Amiri, and Azadeh Sajadi, from
the institute of Iran. wrote a Research article about, Fire, Carbon
Sequestration & Restoration in Northern Zagros Forests. Entitled, The
review of fire condition in Zagros forest and estimate carbon sequestration of
plantation by endemic species in Northern Zagros forest (Marivan Region: West
of Iran). This research paper published by the International Journal of Biosciences | IJB. an open access scholarly research journal
Biosciences. under the affiliation of the International Network For
Natural Sciences| INNSpub. an open access multidisciplinary research
journal publisher.
Abstract
Fire, as a natural
ecological disturbance factor in forest, this project located Jashniabad
village in the Marivan region, Northern Zagros forest, and western Iranian
state of Kurdistan. To this project visited the forest and interviewed to
Forest communities detected the major forest destruction in the study area. To
afforestation of burned area used the native species (Quercus spp., Pistacia
atlantica Desf, Amygdalus communis L, Cercis griffithii Boiss, Celtis
tournefortii Lam, Romex sp. and Juglans regia L.) Two
estimate of Carbon sequestration in the project of plantation in the first year
used the sampling the in the seven plantation species. Seedlings were collected
and their weights were measured by scales (gr carefully). For estimate the
carbon sequestration used this formula (Carbon sequestration (kg) = 1.63×
weight (kg)). The results of this study showed that the main forest destruction
element in the Marivan and Zagros are fire, grazing, farm operation in forest,
fuel wood and timber, mining, semi-parasite plant and non-wood forest
production, but fire is a major element of forest destruction in the marivan
region. Results showed that the quantity Carbon sequestration this (1 hectare)
in the first year in one hectare is 97.3 kg. Overall results showed that the
fire are a major element for forest destruction in the Marivan region and
plantation by native and endemic species are suitable methods for
rehabilitation of burned forest area, and one hectare of plantation absorbed
the near 100 kg of carbon from air and soil. Authors suggestion to use the
plantation by native and endemic species for rehabilitation of burned forest in
Marivan and others region from Zagros forest.
Read more : Nutrient Changesin Tetrapleura tetraptera Across Maturity Stages | InformativeBD
Introduction
With due attention to
climate conditions of Iran that 65% area includes arid and semi-aired and
degradation rapid of north and west, because of degradation of natural
resources will cause to degradation agricultural lands and human environmental
(Dastmalchi, 1998, Zabiholahii et al, 2012, Haidari et al, 2012, Haidari et al,
2013a and Askari et al, 2013a). Forests cover about 12 million ha in Iran
(Forest and Rangeland Organization, 2002; Haidari et al, 2013b, Haidari et al,
2013c), including 5 million ha in the mountainous Zagros region. The major
element of Zagros forest destruction include: fire, grazing, farm operation in
forest, fuel wood and timber, mining, semi-parasite plant and non-wood forest
production (Jazirei and Ebrahimi Rastaghi, 2003, Haidari et al, 2013d, Haidari
et al, 2013e, Bazyar et al, 2013a, Parma and Shataei, 2013). Increasing
population, low level of development and high dependence of local communities
on forests for their primary livelihood needs, are the main reasons of this
destruction. The lack of regeneration in these forests is a major concern
(Fattahi 1994, Jazirei and Ebrahimi Rastaghi, 2003, Bazyar et al, 2013b, Rezaei
et al, 2013, Askari et al, 2013c, Haidari et al, 2012b, Haidari et al, 2012c).
Fire review in Iran and
Zagros region Recurrent fires have seen an enormous increase in frequency over
the recent decades and they are the main disturbances to this ecosystem
(Luis-Calabuig et al., 2000). Disturbances such as fire, windstorms, floods,
and grazing play a role in the maintenance of species diversity that has become
well recognized in ecological theory (Mackey and Currie, 2000). Effects of Fire
on vegetation are usually the most obvious impacts of burning. Fire affects
natural ecosystems by consuming plants, altering successional patterns, and
changing vegetative resources such as timber, forage and wildlife habitats
(DeBano et al, 1978). Burning alone can result in increased forb abundance
(Wienk et al, 2004) grained abundance and under story species richness
(Laughlin et al, 2004).
Many studies have been
carried out on plant biodiversity indices in Iran and around the world. The
zagros where fire occurs in 300-400 ha annually (Anonymous, 2002).
Author proclaimed that
fire increased herbal species cover in burned area but did not effect on
biodiversity indices in temperate forest of northeast of Iran (Atrakchaiee,
2000).
The researcher studied
effect of fire on herbal layer biodiversity in a temperate forest of northern
Iran and results showed the biodiversity indices and coverage percent of shade
tolerant species in unburned area were higher then burned area (Banj Shafiei et
al, 2006).
The researcher
investigated on the preliminary results of post fire re sprouting of manna oak
(Quercus brantii Lindl.) in Zagros forests and results showed that post-fire re
sprouting is positively related to the number of pre-fire sprouts and the fire
intensity (Pourreza et al, 2009).
The researcher studied
the effect of forest fire on diameter growth of beech (Fagus orientalis Lipsky)
and hornbeam (Carpinus betulus L.) and results showed that the surface fire
didn’t effect on beech but hornbeam ring growth was increased significantly.
The correlation within ring growth width and climatic data had been recognized
before fire but there was no correlation with years after that. Thus, other
factors excluding climate such as fire could be considered as the change
reasons (Banj Shafiei et al, 2009).
The researcher studied
the Fire influence on vegetation changes of Zagros mountainous rangelands and
results showed that in burned sites density, cover percentage and forage
production of perennial grasses significantly increased while, in contrast
density and cover percentage of shrubs and annual grasses decreased. Percentage
of bare soil increased in burned sites. The Species diversity reduced in
initial years after burning but a gradual increase was observed at the end of
study period (Fattahi and Tahmasebi, 2010).
The researcher studied
the effect of fire on some soil chemical properties of oak forests in Marivan
region and results showed significant effects of fire on most chemical
attributes of surface soil including: pH, available phosphorous, electrical
conductivity and available potassium increasing. The fire caused increasing of
total nitrogen and cation exchangeable capacity in surface soil. All of
chemical properties of subsurface soil were measured higher in burned area than
control however; these differences were not significant, statistically
(Hemmatboland et al, 2010).
Reference
Askari A, Kafash Saei
E, Delpasand S, Rezaei D. 2013a, Evaluation of Crategus sp. spatial
pattern in Central Zagros Forest, International journal of Advanced Biological
and Biomedical Research 1(2), 179-185.
Abdi N, Maddah Arefi H,
Zahedi Amiri Gh. 2008. Estimation of carbon sequestration in Astragalus
rangelands of Markazi province (Case study: Malmir rangeland in Shazand
region). Iranian journal of Range and Desert Research 15(2), 169-182.
Anonymous. 2002.
Statistical Yearly Report. Management and planning Organization of Iran, 156p.
Askari Y, Parsapour MK,
hosseni Z. 2013. Modeling of Suitability Iranian Oak site for establish of
coppice regeneration in Zagros forest. International journal of Advanced
Biological and Biomedical Research (IJABBR) 1(1), 61-70.
Atrakchaieem A. 2000.
Fire effects on vegetation changes in Golestan National Park, Iran. Forestry M.
Sc. Thesis, University of Mazandaran, 85p.
Banj Shafiei A,
Akbarinia M, Jalali Gh, Alijanpour A. 2009. Effect of forest fire on
diameter growth of beech (Fagus orientalis Lipsky) and hornbeam (Carpinus
betulus L.): a case study in Kheyroud forest, Iranian Journal of Forest and
Poplar Research 17(3), 463-474.
Banj Shafiei A,
Akbarinia M, Jalali SG, Azizi P, Hosseini SM. 2006. Effect of Fire on Herbal
Layer Biodiversity in a Temperate Forest of Northern Iran. Pakistan Journal of
Biological Sciences 9(12), 2273-2277.
Bazyar M, Bonyad A,
Babaie Kafaki S. 2013a. Study of most element of forest destruction by
used the IRS-1C and LANDSAT image in the southern zagros forest (Case study:
Kohkeloeye and Boveirahmad province). International journal of Advanced
Biological and Biomedical Research (IJABBR) 1(1), 35-44.
Bazyar M, Haidari M,
Shabanian N, Haidari RH. 2013b. Impact of physiographical factors on the
plant species diversity in the Northern Zagros Forest (Case study, Kurdistan
Province, Marivan region). Annals of Biological Research 4(1), 317-324.
Biranvand A, Babaei
Kafaki S, Kiadaliri H. 2011. Investigation the Ecological Factors
Affecting Fire Spread in Forest Ecosystems (Case Study: Kakareza-Lorestan),
Journal of Renewable Natural Resources 2(2), 1-13.
Dastmalchi M. 1998.
Investigation compatibility experimental of tree species Ardabil province.
Jangal and Senoubar J. Inst. For. Ranglands Res, NO. 203, 168.
Debano LF, Conrad CE.
1978. The effect of fire on nutrients in a chaparral ecosystem. Ecology 59, 489-497. http://dx.doi.org/10.2307/1936579
Delcourt HR, Delcourt
PA. 1997. Pre-Columbian Native American use of fire on southern
Appalachian landscapes. Conservation Biology 11, 1010-1014. http://dx.doi.org/1046/j.1523-1739.1997.96338.x
Dixon RK, Brown S,
Houghton RA, Solomon AM, Trexler MC, Wisniewski J. 1994. Carbon pools and
flux of global forest ecosystems. Science 263, 185–190.
Fattahi B, Tahmasebi A. 2010.
Fire influence on vegetation changes of Zagros mountainous rangelands (Case
study: Hamadan province), Rangeland 4(2), 228-239.
Fattahi M. 1994.
Study on Zagros oak forests and the most important their destruction causes.
Institute of Forests and Rangelands Research press. Sanandaj. Iran.
Haidari M, Etemad V,
Khosropour E. 2013a. Study of tree regeneration in the grazed and
non-grazed areas in the Iran-o- Turanian Ecological Zones. International
journal of Advanced Biological and Biomedical Research (IJABBR) 1(1), 18-24.
Haidari M, Jalilvand H,
Haidari RH, Shabanian N. 2012 b. Study of Plant Biodiversity in Grazed and
Non-grazed Areas in the Iran-o-Turanian Ecological Zones (Case Study: Yazd
Province, IRAN). Annals of Biological Research 3(11), 5019-5027.
Haidari M, Namiranian
M, Gahramani L, Zobeiri M, Shabanian N. 2013c. Study of vertical and
horizontal forest structure in Northern Zagros Forest (Case study: West of
Iran, Oak forest). European Journal of Experimental Biology 3(1), 268-278.
Haidari M, Namiranian
M, Zobeiri M, Ghahramany L. 2013d. Evaluation of different sampling method
to study of tree density (tree/hectare) in the Zagros forest. International
journal of Advanced Biological and Biomedical Research (IJABBR) 1(1), 11-17.
Haidari M, Rezaei D. 2013e.
Study of plant diversity in the Northern Zagros forest (Case study: Marivan
region). International journal of Advanced Biological and Biomedical Research
(IJABBR) 1(1), 1-10.
Haidrai M, Bazyar M,
Hosseini SA, Haidari RH, Shabanian N. 2013f. Study of forest destruction by
used the diversity index in the Northern Zagros Forest (Case study: Oak
forest). International Journal of Biological & Medical Research 4(1), 2720-
2725.
Hemmatboland E,
Akbarinia M, Banej Shafiei A. 2010. The effect of fire on some soil
chemical properties of oak forests in Marivan region, Iranian Journal of Forest
and Poplar Research 18(2), 204-218.
Huston MA. 1994.
Biological diversity. Cambridge University Press, Cambridge, UK.
Jazirehi, MH, Rostaghi,
EM, 2003. Silviculture in Zagros. University of Tehran Press. Tehran. 520.
Laughlin DC, Bakker JD,
Stoddard MT, Daniels ML, Springer JD. 2004.Toward reference conditions:
Wildfire effects on flora in an old-growth ponderosa pine forest, Forest
Ecology and Management 192, 137-152. http://dx.doi.org/10.1016/j.foreco.2004.05.034
Luis-Calabuig E, Ta´
rrega R, Calvo L, Marcos E, Valbuena L. 2000. History of landscape changes
in northwest Spain according to land use and management. In: Trabaud, L. (Ed.),
Life and Environment in the Mediterranean. WIT Press, Southampton, 43–86 p.
Mackey RL, Currie DJ. 2000.
A re-examination of the expected effects of disturbance on diversity. Oikos 88,
483–493. http://dx.doi.org/10.1034/j.1600-0706.2000.880303.x
Mahmoudi Taleghani E,
Zahedi Amiri Gh, Adeli E, Sagheb-Talebi Kh. 2007. Assessment of carbon
sequestration in soil layers of managed forest, Iranian Journal of Forest and
Poplar Research 15(3), 241-252.
Medlyn BE, Berbigier P,
Clement R, Grelle A, Loustau D, Linder S, Wingate L, Jarvis PG, Sigurdsson BD,
McMurtrie RE. 2005. The carbon balance of coniferous forests growing in
contrasting climatic conditions: a model-based analysis. Agricultural
and Forest Meteorology 131, 97–124. http://dx.doi.org/10.1016/j.agrformet.2005.05.004
Mehta JP, Tiwari SC,
Bhandari BS. 1997. Phytosociology of woody vegetation under different
management regimes in Garhwal Himalaya. Journal of Tropical Forest 10, 24-34.
Metlen KL, Fiedler CE.
2005. Restoration treatment effects on the under story of Ponderosa
Pine/Douglas-Fire Forest in Western Montana, USA. Forest Ecology
Management 222, 355-369.
Nobakht A, Pourmajidian
M, Hojjati S.M, Fallah A. 2011. A comparison of soil carbon sequestration
in hardwood and softwood monocultures (Case study: Dehmian forest management
plan, Mazindaran), Iranian Journal of Forest 3(1), 12-23.
Pandey D. 1995.
Forest resources assessment 1990. Tropical forest plantation resources. FAO
Forestry Paper 128, 81 p.
Parma R, Shataee S. 2013.
Estimation of species diversity of trees and shrubs using ETM+ sensor data
(Case study of forests in Qalajeh Kermanshah province). International journal
of Advanced Biological and Biomedical Research (IJABBR) 1(1), 71-78.
Plocher AE. 1999.
Plant population dynamics in response to fire in long leaf pineturkey Oak
Barrens and adjacent Wetter communities in southeast Virginia. J.Torry Bot.
Soc 126, 213 – 225.
Pourbabaei H, Navgran
S. 2011. Study on floristic and plant species diversity of the Lebanon oak
site (Quercus libani) in the western Iran. Biocenose Journal 3(1), 15-22.
Pourreza M, Safari H,
Khodakarami Y, Mashayekhi S. 2009. Preliminary results of post fire resprouting
of manna oak (Quercus brantii Lindl.) in the Zagros forests, Kermanshah.
Iranian Journal of Forest and Poplar Research 17(2), 225-236.
Sanghoon C, Woen K, Che
S.1997. Comparison of plant community structures in cut and uncut areas at
burned area of Mt. Journal
of Korean Forestry Society 86, 509-520.
Schlesinger WH. 1997.
Biogeochemistry, an Analysis of Global Climate Change. San Diego, CA,
USA/London, UK: Academic Press.
Sheidai Karkaj E,
Barani H, Akbarlo M, Heshmati Gh. A, Khormali F. 2013. Cost comparing of
soil carbon sequestration in rangeland reclamation practices through plantation
of Agropyron elongatum and Atriplex lentiformis (Case Study: Chapr goymeh of
Gonbad). Journal of Water and Soil Conservation 20(1), 240-251.
Varamesh S, Hosseini S.
M, Abdi N, Akbarinia M. 2010. Increment of soil carbon sequestration due
to forestation and its relation with some physical and chemical factors of
soil, Iranian Journal of Forest 2(1), 25-35.
Wienk CL, Sieg CH,
McPherson GR. 2004. Evaluating the role of cutting treatments, fire and
soil seed banks in an experimental framework in Ponderosa Pine Forest of the Black
Hills. South Dakota. Forest Ecology and Management 192, 375-393. http://dx.doi.org/10.1016/j.foreco.2004.02.004
Zabiholahii S, Haidari
M, Namiranian N, Shabanian N. 2012. Effect of traditional forest
management practices in Havare khol pattern on forest structure (Case study:
Kurdistan province, Northern Zagros forest). IOSR Journal of Pharmacy and
Biological Sciences (IOSR-JPBS) 5(1), 42-47.
Zobe B.
1997. Afforestation, PLANTATIONS BY AFFORESTATION, M.Sc.
Thesis.













