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Sequestration and storage of carbon by trees in and around University campus of Aurangabad city in Maharashtra, India.
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Sequestration and storage of carbon by trees in and around University campus of Aurangabad city in Maharashtra, India.
1.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 01 | Jan -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 598 Sequestration and storage of carbon by trees in and around University campus of Aurangabad city in Maharashtra, India. Potadar Vishnu R1, and Satish S Patil2 Research student, Department of Environmental Sciences, Dr. Babasaheb Ambedkar Marathwada University Aurangabad vishnupotadar@gmail.com Professor, Department of Environmental Sciences, Dr. Babasaheb Ambedkar Marathwada University Aurangabad sushshrey@rediffmail.com Abstract:Trees from the urban regions currently store carbon, which can be released into the atmosphere after the death of tree, and capture carbon as they grow. A major challenge is the lack of correct and spatially explicit estimates of tree carbon storage over the entire urbanized area. The study was carried out in and around university campus of Aurangabad city to know the CO2 sequestration from the selected ten tree species. Assessment of the carbon sequestration of urban trees was carried out through the biomass estimation and quantification. For the estimation of total CO2 sequestration DBH and height measured. Wood densities were obtained from world agroforestry centre. It is found that highest CO2 3916. 81 kg/tree captured by Swietenia mahagoni followed by Pithocellobium dulce which is captured 1401.18 kg of CO2 per tree. Total above ground biomass 3463.10, total below ground biomass 900, total biomass 4363.50, total carbon 2181.75 kg/tree. Total tree count is 835 out of which Roystonea regia found 206 tree count which is maximum. It is found that total CO2 sequestered by the selected area is 565.32 tonnes. Carbon sequestration is a way to mitigate the accumulation of greenhouse gases in the atmosphere released by the burning of fossil fuels and other anthropogenic activities. KEYWORDS: - biomass, tree, CO2 sequestration, gas, fuels 1. INTRODUCTION More than half of the population at the global level now lives in urban regions, and this figure will continue to increase at a rate of 4% a decade by 2050 [1]. Carbon sequestration is one of the important processes of storage of CO2 or other forms of carbon to mitigate environmental issues like global warming, green house effect and its one of the important clause of Kyoto Protocol, through biological, chemical or physical processes; CO2 is sequestered from the atmosphere. The Kyoto Protocol to the UN Framework Convention on the Climate Change has provided a vehicle for considering the various effects of carbon sinks and sources, as well as addressing issues concerned to fossil fuels emission. Growing concern about the climate change and concerned problems led to the research quantifying the overall effects of trees from the urban area on atmospheric carbon dioxide (CO2 ) [4,5,6,7,8,9]. Trees from Urban area also affect temperatures of air and building energy use, and consequently alter carbon release from numerous urban sources [2]. Thus, urban trees potentially influence the climate at the local level, carbon cycles, energy use and the climate change [10, 11, 12, 13, 14]. Urban trees affect climate change, but these trees are often disregarded because their environmental services are not so well understood or quantified. Trees act as a sink for carbon dioxide (CO2) by fixing carbon during the photosynthesis and storing carbon as the biomass. The clear long-term CO2 origin dynamics of the forests change through time as trees grow, die, and decay. Human influences on forests can further affect CO2 source dynamics of urban forests through such components as fossil fuel emissions and harvesting of biomass [3]. 2. MATERIALS AND METHODS 2.1 Location The study area comprises of 2126 hectares of area which is mainly from B.A.M. University campus and Jaisingpura, Pahadsingpura etc. The district is from 19 to 20 degrees north longitude and 74 to 76 degrees east latitude. Aurangabad city is situated on the river bank Kham a tributary of the Godavari river. The entire city is situated at the latitude of 19o53’50” N and longitude of 75o22’46” E. Aurangabad District is located mainly in the Godavari river basin and partly in the Tapi river basin. The city is surrounded by the hills of the Vindhya ranges and the river Kham passes through it.
2.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 01 | Jan -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 599 2.2 Measurement of diameter at breast height (DBH) and tree height: To estimate the biomass of different trees, non-destructive method was used. The biomass of the tree was estimated on the basis of diameter at breast height (DBH) and tree height. DBH can be determined by measuring tree Girth at Breast Height (GBH), approximately 1.3 meter above the ground. The GBH of trees having the diameter greater than 10 cm were measured directly by the measuring tape [21]. The tree height measured by the Theodolite instrument. 2.3 Above ground biomass (AGB) of trees: The above ground biomass of the tree includes whole shoot, branches, flowers, leaves and fruits. It is calculated using the following formula.[22]. AGB kg = volume of tree (m3) x wood density Kg/m3 V = π r2H Where H = Height of the tree in meter, V= volume of the cylindrical shaped tree in m3, r = radius of the tree in meter, Radius of the tree is calculated from GBH of tree. Height was measured with the help of the instrument Theodolite. The wood densities were obtained from the website www.worldagroforestycentre.org. The standard average density of 0.6 gm/cm was applied wherever the density value is not available for tree species [20]. 2.4 Estimation of the Below Ground Biomass (BGB) The Below Ground Biomass (BGB) includes all biomass of live roots excluding fine roots having < 2 mm diameter. The below ground biomass was calculated by multiplying AGB by 0.26 factors as the root: shoot ratio. BGB is calculated by following formula [21,20, 23]. BGB (Kg/tree) = AGB (Kg/tree) or (ton/tree) x 0.26 Table 1: Wood densities of tree species Sr. No. Tree Species (Scientific Name) Local name Wood density in g/cm3 1 Pithecellobium dulce Vilayati chinch 0.6657 2 Polyalthia longifolia Ashok 0.5635 3 Pongamia pinnata Karanj 0.6198 4 Psidium guajava Peru 0.6713 5 Punica granatum Dalimb 0.771 6 Roystonea regia palm tree 0.66 7 Santalum album Chandan 0.9367 8 Sesbania sesban Shevari 0.43 9 Spathodea campanulata Pichkari 0.3303 10 Swietenia mahagoni Mohogony 0.66 3. RESULTS AND DISCUSSION Humans constantly interact with the natural environment to create some differences in the tree cover. Costs of maintaining the cover of vegetation and attitudes toward the trees in urban landscape, both related to ambient environmental factors, alter the desire and ability of individuals to incorporate trees in the urban landscape. Tree cover can be increased by allowing space for the vegetation cover, planting, and inspiring natural regeneration. Measurements of the tree cover provide important basic structural data used to model urban tree cover functions such as air pollution control and carbon dioxide capture [19]. Understanding the relationship among the urban trees, people, and environment can facilitate probable urban designs that might increase the environmental and social benefits from trees. Large trees also preserve approximately 1000 times maximum carbon than smaller trees [19,20]. It may be one of the crucial green region in the urban and industrial sectors. Carbon capture rates vary by species, soil, climate, topography and most important is management practice [13]. Environmentalists have highlighted the role of urban forests as a place of social integration as they provide recreation and relief to the urban population from their hectic life. More research work is required on the overall effects of trees, soils and its proper management in the urban areas. Carbon storage by tree species in woodlands at national level was 20.2 billion tonnes in 2008 [20]. Table 2: Shows Biophysical measurements with AGB and BGB Sr . N o. Scientific name DBH (Mete rs) Heigh t (Mete rs) Volu me (m3) AGB (kg/tr ee) BGB (kg/tr ee) 1 Pithecello bium dulce 0.363 8.79 0.91 606.6 4 157.7 3 2 Polyalthia longifolia 0.194 7.88 0.23 131.2 2 34.12 3 Pongamia pinnata 0.189 5.88 0.16 101.7 0 26.44 4 Psidium guajava 0.192 5.99 0.17 116.0 5 30.17 5 Punica granatum 0.142 4.19 0.07 50.97 13.25 6 Roystonea regia 0.317 8.46 0.67 400.4 7 104.1 2
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 01 | Jan -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 600 7 Santalum album 0.17 4.49 0.10 91.79 23.86 8 Sesbania sesban 0.148 4.25 0.07 31.50 8.19 9 Spathodea campanul ata 0.295 10.50 0.72 237.0 0 61.62 1 0 Swietenia mahagoni 0.464 15.22 2.57 1695. 76 440.9 0 Average 0.247 7.56 0.56 346.3 0 90.04 Total 2.474 75.64 5.67 3463. 10 900.4 0 Table 3: Shows TB, C, CO2, Tree count, Total CO2 Sr . N o. Scientific name TB (kg/tr ee) C (kg/tr ee) CO2 (kg/tr ee) Tre e cou nt Total CO2 (Tonn es) 1 Pithecello bium dulce 764.3 6 382.1 8 1401. 19 156 218.5 86 2 Polyalthia longifolia 165.3 4 82.67 303.1 0 40 12.12 4 3 Pongamia pinnata 128.1 4 64.07 234.9 1 205 48.15 6 4 Psidium guajava 146.2 2 73.11 268.0 5 156 41.81 5 5 Punica granatum 64.22 32.11 117.7 2 40 4.709 6 Roystonea regia 504.6 0 252.3 0 925.0 0 206 190.5 50 7 Santalum album 115.6 5 57.83 212.0 1 7 1.484 8 Sesbania sesban 39.69 19.85 72.76 6 0.437 9 Spathodea campanul ata 298.6 2 149.3 1 547.4 2 8 4.379 1 0 Swietenia mahagoni 2136. 66 1068. 33 3916. 82 11 43.08 5 Average 436.3 5 218.1 7 799.8 9 83.5 56.53 0 Total 4363. 50 2181. 75 7998. 96 835 565.3 20 Carbon capture and sequestration is a theoretical approach to control and mitigate the contribution of emissions of fossil fuels to global warming, based on capturing carbon dioxide from large point sources such as the fossil fuel power plants. The carbon dioxide might then be stored away from the atmosphere permanently. As urban areas discharge maximum amount of emissions of carbon, tree creates an impact on carbon emissions through changing in climates at micro level, albedo, use of energy, and maintenance of emissions which require to be added with tree storage and capture estimates to improve a more complete evaluation of the role of trees of the urban area on climate change [20]. Graph showing CO2 sequestration The study was conducted in the Aurangabad city to estimate the above ground biomass, below ground biomass, total biomass, carbon dioxide, carbon from selective ten tree species. Swietenia mahagoni has sequestered 3916.81 kg/tree of CO2 which is highest compared to other tree species from the study area. It is due to high DBH and height of the tree. At the same time AGB 1695.76, BGB 440.89, total biomass 2136.65, carbon 1068.32 which is highest in the Swietenia mahagoni which has only 11 tree count. Sesbania sesban sequestered lowest CO2 72.75 kg/tree compared to other trees which is may be due to lowest DBH i.e. 0.148 meters, total biomass sequestered 39.69 kg/tree. Total tree count of the study area is 835. Maximum 206 trees found of Roystonea regia and only 6 trees found of Sesbania sesban from the study area. Total AGB 3463.10, total BGB 900, Total biomass 4363.50, Total carbon 2181.75, total CO2 sequestered is 7998.96kg/tree and total CO2 from all tree species from the study area is 565.32 tonnes. Large healthy trees having the diameter more than 77 cm sequester approximately 90 times more carbon as compared to the small healthy trees species which have the diameter less than 8 cm [19]. Large trees also store nearly 1000 times maximum carbon than smaller trees [20, 19]. 0.0 1000.0 2000.0 3000.0 4000.0 1401.2 303.1234.9268.0117.7 925.0 212.072.8 547.4 3916.8
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 01 | Jan -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 601 REGRESSION ANALYSIS To estimate the closeness and relationships various parameters a regression analysis was performed with the help of SPSS 16.0 software. Model Summary Mode l R R Square Adjuste d R Square Std. Error of the Estimate 1 .949a .900 .871 .27519 a. Predictors: (Constant), Height, DBH Coefficientsa Model Unstandardized Coefficients Standardize d Coefficients t Sig.B Std. Error Beta 1 (Constant ) -1.097 .229 - 4.79 1 .00 2 DBH 3.169 2.321 .443 1.36 6 .21 4 Height .116 .072 .522 1.61 0 .15 2 a. Dependent Variable: Volume Where, t = Statistics R= Multiple correlation coefficient; R2 and adjusted R2 = Coefficient determination of variablesB= Regression coefficient Above table shows that strong correlation coefficient between DBH with volume and the height whereas adjusted R2 shows 87 % variability between the Volume with DBH and Height. Above statistical table shows that volume is significant with DBH. As increase in DBH its metabolic and the growth necessities would also increase. 4. CONCLUSION Trees from urban area play crucial roles in reduction of the atmospheric carbon dioxide levels. In the present research work calculation of AGB, BGB, TB, carbon and carbon dioxide sequestration potential rate often tree species was done by nondestructive method. Theodolite instrument was used for height measurement. Wood densities were obtained from the World Agroforestry Centre for the measurement of carbon sequestered by trees. Carbon stock was determined for Pithecellobium dulce, Polyalthia longifolia, Pongamia pinnata, Psidium guajava, Punica granatum, Roystonea regia, Santalum album, Sesbania sesban, Spathodea campanulata, Swietenia mahagoni tree species in and around university campus of Aurangabad city. Results show that Swietenia mahagoni has the better carbon sequestration potential rate which sequestered 3916.81 kg/tree of CO2 whereas Sesbania sesban has the least sequestration rate which sequestered 72.75 kg/tree of CO2 as compared to other species. Total tree count is 835. Total carbon sequestered 2181.75. Total carbon dioxide from all the tree species sequestered 7998.96 kg/tree. Carbon dioxide sequestered by the trees 565.32 tonnes. More field measurements are needed in urban regions to help improve carbon accounting and other functions of urban forest ecosystems. Before applying the approach of urban tree management, quantification of organic carbon in the urban region by nondestructive method will be helpful. REFERENCES [1] United Nations (2015). World Urbanization Prospects: The 2014 Revision. NewYork, NY: United Nations Department of Economic and Social Affairs, Population Division. [2] Nowak, D.J. (1993). Atmospheric carbon reduction by urban trees. Journal of Environmental Management 37 (3), 207-217. [3] Nowak, D.J. (2010). Urban biodiversity and climate change. In: Muller, N., Werner, P., Kelcey, J.G. (Eds.), Urban Biodiversity and Design. Wiley-Blackwell Publishing, Hoboken, NJ, pp. 101-117. [4] McPherson EG (1998). Atmospheric carbon dioxide reduction by Sacramento’s urban forest. J Arboric 24(4):215–223 [5] Jo HK (2002). Impacts of urban greenspace on offsetting carbon emissions for middle Korea. J Environ Manage 64(2):115–126 [6] Nowak DJ, Crane DE (2002). Carbon storage and sequestration by urban trees in the USA. Environ Pollut 116(3):381–389 [7] Escobedo F, Varela S, Zhao M, Wagner JE, Zipperer W (2010) Analyzing the effi cacy of subtropical urban forests in offsetting carbon emissions from cities. Environ Sci Policy 13(5):362–372 [8] Stoffberg GH, van Rooyen MW, van der Linde MJ, Groeneveld HT (2010) Carbon sequestration estimates of indigenous street trees in the City of
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 01 | Jan -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 602 Tshwane, South Africa. Urban For Urban Green 9(1):9–14 [9] Zhao M, Escobedo F, Staudhammer C (2010) Spatial patterns of a subtropical, coastal urban forest: implications for land tenure, hurricanes and invasives. Urban For Urban Green. doi: 10.1016/j. ufug.2010.01.008 [10] Abdollahi, K.K., Ning, Z.H., Appeaning, A. (2000). Global Climate Change and the Urban Forest. GCRCC and Franklin Press, Baton Rouge, pp. 31-44. [11] Wilby, R.L., Perry, G.L.W. (2006). Climate change, biodiversity and the urban environment: a critical review based on London UK. Progress in Physical Geography 30 (1), 73-98. [12] Gill, S.E., Handley, J.F., Ennos, A.R., Pauleit, S. (2007). Adapting cities for climate change: the role of the green infrastructure. Built Environment 33 (1), 115-133. [13] EPA (2010). Environmental co-benefits of sequestration practices. Internet file http;//www. epa.gov/sequestration/fag.html. [14] Lal, R., Augustine, B. (2012). Carbon Sequestration in Urban Ecosystems. Springer, New York, p. 385. [15] Nowak, D.J., 1994. Atmospheric carbon dioxide reduction by Chicago’s urban forest. In: McPherson, E.G., Nowak, D.J., Rowntree, R.A. (Eds.), Chicago’s Urban Forest Ecosystem: Results of the Chicago Urban Forest Climate Project. USDA Forest Service General Technical Report NE-186, Radnor, PA, pp. 83–94. [16] Potadar Vishnu R, and Satish S Patil. (2016). Carbon Storage and Sequestration by Trees in and Around University Campus of Aurangabad City, Maharashtra. International Journal of Innovative Research in Science, Engineering and Technology Vol. 5, Issue 4, April 2016 ISSN (Online) : 2319-8753 [17] Hangarge L. M., D. K. Kulkarni, V. B. Gaikwad, D. M.Mahajan and NishaChaudhari (2012). Carbon Sequestration potential of tree species in SomjaichiRai (Sacred grove) at Nandghur village, in Bhor region of Pune District, Maharashtra State, India. Annals of Biological Research, (7): 3426- 3429. [18] Bandana Gupta and Sanjay Sharma (2014). Estimation of Biomass and Carbon Sequestration of Trees in Informally Protected Areas of Rajouri, J&K, India International Research Journal of Environment Sciences ISSN 2319–1414 Vol. 3(6), 56-61, June (2014) Int. Res. J. Environment Sci. [19] K.G. MacDicken, (1997). A Guide to Monitoring Carbon Storage in Forestry and Agro forestry Projects, Winrock International Institute for Agriculture Development, USA, pp. 13-14. [20] A.N. Djomoa, , A., Ibrahimab, J. Saborowskic, , and J. Gravenhorsta, (2010). Allometric equations for biomass estimations in Cameroon and pan moist tropical equations including biomass data from Africa, Forest Ecology and Management, 260, pp 1873-1885.
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