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\title{Potentiality of Carbon Sequestration in Six Year Ages Young Plant from University Campus of Aurangabad}
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             \author[1]{Rasal G.  B}

             \author[2]{Dr. Chavan B.  L.}

             \affil[1]{  Dr. B. A. M. University, Aurangabad.}

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\date{\small \em Received: 30 October 2011 Accepted: 22 November 2011 Published: 3 December 2011}

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\begin{abstract}
        


Carbon sequestration in urban sectors and forest areas is of great attention due to its  concerns about global climate change. In the present investigation aboveground carbon sequestration  potential of six year young age Emblica   officinalis, Mangifera indica, Tamarindus indica, Achras sapota,  Annona retiaculata and Annona squamosa species from the university campus of Aurangabad is  measured. The aboveground biomass rate of carbon sequestered was estimated using ash method. The  percentage of carbon content in the aboveground and below ground biomass i.e. leaves, stem, branches,  bark and root of Emblica officinalis were 43.67%, 52.89%, 53.91%, 53.59% and 55.68% respectively, in  Mangifera indica were 49.28%, 50.65%, 50.43%, 52.11 and  53.88% carbon respectively, in Tamarindus  indica were 53.47%, 57.53%, 56.84%, 55.85% and 54.63% carbon respectively, in Achras sapota were  53.63%, 52.4%, 53.72%, 48.42% and 49.52% carbon respectively, Annona retiaculata were 53.67, 57.24%,  55.24 53.08% and 51.62% respectively, Annona squamosa there were 52.08%, 55.09%, 55.33%, 56.01%  and 52.04 respectively. The total above ground biomass carbon stalk per hectare as estimated for  Emblica officinalis was 33.07 Kg C ha-1, in Mangifera indica it was 30.6 Kg C ha-1 and in Tamarindus  indica it was 36.96 Kg C ha-1 and in Achras sapota were 12.86 Kg C ha-1 in Annona retiaculata was 83.1  Kg Cha-1 and for Annona squamosa it was 73.5 Kg C ha-1 in University campus.  

\end{abstract}


\keywords{Aboveground biomass, belowground biomass, carbon sequestration potential, climate change, carbon stock.}

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\let\tabcellsep& 	 	 		 
\section[{INTRODUCTION}]{INTRODUCTION}\par
Carbon dioxide (CO 2 ) is a major contributing gas to the green house effect. It is one of the dominant greenhouse gases among them. The Kyoto Protocol prepared by the United Nations in the Framework of Convention on Climate Change stipulates Clean Development Mechanisms (CDM) and its Joint Implementation whereby storage of carbon in various terrestrial sinks may be acceptable for insertion in national greenhouse gas inventories of each nation. The increasing carbon emission is of major concerns all over the world and it has been well addressed in Kyoto protocol \hyperref[b14]{(Ravindranath et al., 1997;}\hyperref[b3]{Chavan and Rasal, 2010)}. The rate of carbon storage increases in young tree species, while it declines after full growth as the stand ages \hyperref[b7]{(Jana, et al., 2009)}. Carbon sequestration is a natural method for the removal of carbon from the atmosphere by storing it in the biosphere \hyperref[b4]{(Dhruba, 2008}; \hyperref[b3]{Chavan and Rasal, 2010)}. Biomass is defined as the total amount of aboveground living organic matter in trees expressed as oven-dry tons per unit area that reduces the concentration from atmospheric concentration of carbon dioxide \hyperref[b1]{(Brown, 1997;}\hyperref[b6]{FORDA and JICA, 2005;}\hyperref[b13]{Ravindranath and Ostwald, 2008)}. The atmospheric carbon dioxide is captured and stored in plants, soils, oceans, or atmosphere in the forms of biomass by photosynthesis process.\par
The amount of carbon sequestered continuously by a tree increases substantially over the time and age of tree till it matures. The process of carbon capture in photosynthesis is influenced by different factors including the tree age, leaf area and photosynthetic efficiency. The increasing carbon emission is of major concerns all over the world; it has been well addressed in Kyoto protocol \hyperref[b14]{(Ravindranath et al., 1997;}\hyperref[b3]{Chavan and Rasal, 2010)}. The rate of carbon storage increases in young tree species, while it declines after full growth as the stand ages \hyperref[b7]{(Jana, et al., 2009)}. Above Ground Biomass (AGB) of tree includes all living biomass of all its parts above the soil, while Below Ground Biomass (BGB) includes all the plant biomass of live roots excluding the fine roots of sizes <2mm diameter \hyperref[b13]{(Ravindranath and Ostwald, 2008)}. Carbon sequestration in growing forests is known to be a costeffective option for mitigation of global warming and global climatic change. The objective of this study is to measure carbon sequestered from selective tree species of Emblica officinalis, Mangifera indica, Tamarindus indica, Achras sapota, Annona retiaculata and Annona squamosa grown in the University campus in Aurangabad city, Maharashtra in India. 
\section[{II.}]{II.} 
\section[{METHODOLOGY a) Site and study area}]{METHODOLOGY a) Site and study area}\par
The study area selected in present investigation for the estimation of above ground biomass and below ground biomass and carbon sequestration was the the latitude 19 o 53'47"N and longitude 75 o 23'54"E. The university campus is lousy green and covers about 140 hectares area under the plantation program for selected tree species. The tree species Emblica officinalis, Mangifera indica, Tamarindus indica, Achras sapota, Annona retiaculata and Annona squamosa selected for present investigation are from the plots grown on the university campus. The weather of Aurangabad is dry and moderately extreme. The average day temperature ranges from 27.7 0 C to 38.0 0 C. It falls from 26.9 0 C to 20.0 0 C during night. Relative humidity is extremely low for major part of the year and ranges between 30\% and 50\%, while it is highest 85\% during monsoon. The average rainfall is about 90 cm. It is rather variable from year to year (ESRAM, 2009). b) Estimation of carbon sequestered in different parts of six year tree species\par
The tree biomass includes the total of Above Ground Biomass (AGB) and Below Ground Biomass (BGB). The above ground biomass studied includes all above ground materials covering stem, braches, leaves, bark and below ground biomass consist coarse roots and stumps. The estimation of biomass in the plant was performed by measuring the tree height and diameter of plant species. Weight of the wood biomass has been calculated by multiplying the volume of biomass and specific gravity (SG) of the plant. The specific gravity (SG) considered is the ratio of oven dry weight and green volume of plant.\par
The organic carbon storage in selected tree species of Emblica officinalis, Mangifera indica, Tamarindus indica, Achras sapota, Annona retiaculata and Annona squamosa was estimated by Ash Method as described elsewhere \hyperref[b0]{(Allen, et al., 1986;}\hyperref[b9]{Negi, et al., 2003;}\hyperref[b7]{Jana, et al., 2009)}. The leaves, stem, sub branches, bark and root of each species were separated to estimate carbon by Ash method. The fresh weight of each part of all species washed with distilled water and dried with tissue paper immediately was taken then oven dried for moisture removal at 80 0 C for 24 hrs. Oven dried sample were taken in pre-weighed crucible. The crucibles were placed in the Muffle furnace adjusted at 400 0 C, ignition was carried out for 2.30 hrs.\par
The crucible was cooled slowly inside the desiccators.\par
After cooling the crucible with ash were weighed and percentage of organic carbon were calculated as formulae given by Allen et al,  {\ref (1986)}.?\% = (100 ? ???\%) × 0.58 ? ? ? ? ? . ? . . (1)\par
Where, C is the organic carbon; W1is weight of crucibles, W2 is weight of oven-dried grind samples with Crucibles, and W3 the weight of ash with Crucibles.\par
In the present study we have estimated the aboveground biomass stocks, belowground biomass and carbon stocks taking volume of biomass and specific gravity (SG) of the tree, as described by many researchers \hyperref[b11]{(Rajput et al., 1996;}\hyperref[b7]{Jana et al., 2009;}\hyperref[b9]{Negi et al., 2003)}. ?? = ???? ??? ???ð??"?? ????? ?????? ? ? ? ? ? ? ? ? ? ? .\textbf{(2} 
\section[{RESULTS AND DISCUSSION}]{RESULTS AND DISCUSSION}\par
The estimation of the above biomass in the selected tree species was performed by estimating carbon percentage and by knowing the tree height, diameter, and girth size. Biomass carbon content: The Aboveground biomass (AGB) and Belowground biomass (BGB) of the tree such as leaves, stems, branches (including subbranches), bark and root have been collected and dried at laboratory. The results of biomass analysis by ash method are presented in Figures. Total carbon stalk of a tree has been evaluated by the sum of all the carbon contents of leaves, stem, sub-branches and bark of the tree. The carbon concentration of different tree parts was rarely measured directly, but generally assumed to be 50\% of the dry weight \hyperref[b8]{(Losi et al., 2003;}\hyperref[b7]{Jana et al.,2009)}. The content of carbon in woody biomass any component of forest on average is around 50\% of dry matter \hyperref[b10]{(Paladinic et al., 2009)}. The percentage of carbon in fresh biomass and in each component of the tree, as well as in the whole tree were calculated based on percentage of carbon in the dry biomass of the aboveground and belowground of all components of the leaves, stem, branches, bark, and root. Based on these results, the capacity to stored carbon in individual parts of the tree, in the whole tree and in fresh and dry biomass was compared. It is observed for the percentage of carbon content in the aboveground and below ground biomass i.e. leaves, stem, branches, bark and root of Emblica officinalis were 43.67\%, 52.89\%, 53.91\%, 53.59\% and 55.68\% respectively. The highest carbon percentage was shown in branches, bark and root it was 21\% belowground biomass than the aboveground. The carbon percentages in the components of six year young Emblica officinalis tree parts (Bar chart) and proportion of whole tree components (Pie diagram) (Fig. \hyperref[fig_1]{1}).   and proportion of whole tree components (Pie diagram) (Fig. \hyperref[fig_3]{3}). The percentage of carbon content in the ABG and BGB i.e. leaves, stem, branches, bark and root of Achras sapota were 53.63\%, 52.4\%, 53.72\%, 48.42\% and 49.52\% carbon respectively. The highest carbon percentage was observed in stem in ABG than BGB plant parts. The carbon percentages in the components of six year young Achras sapota tree parts (Bar chart) and proportion of whole tree components (Pie diagram) (Fig. \hyperref[fig_4]{4}). It is observed for the percentage of carbon content in the aboveground and below ground biomass i.e. leaves, stem, branches, bark and root of Annona retiaculata were 53.67, 57.24\%, 55.24 53.08\% and 51.62\% respectively. The highest carbon percentage was observed in stem in AGB than BGB plant parts (Fig. \hyperref[fig_4]{4}). The carbon percentages in the components of six year young Annona retiaculata tree parts (Bar chart) and proportion of whole tree components (Pie diagram) (Fig. \hyperref[fig_5]{5}).  The carbon percentage in components of ABG and BGB i.e. leaves, stem, branches, bark and root of Annona squamosa there were 52.08\%, 55.09\%, 55.33\%, 56.01\% and 52.04 respectively. The highest carbon percentage was observed in bark in AGB than BGB plant parts. The carbon percentages in the components of six year young Annona retiaculata tree parts (Bar chart) and proportion of whole tree components (Pie diagram) (Fig. \hyperref[fig_6]{6}). The estimation of total amount of stored carbon in a tree should be based on biomass of components of whole tree. Using data collected from a typical tree, the fresh biomass of the tree components were determined, while the dry biomass of the component was estimated using sample analysis. The specific gravity, total biomass and total carbon content after six years of age in Emblica officinalis, Mangifera indica, Tamarindus indica, Achras sapota, Annona reticulata and Annona squamosa is shown in Table \hyperref[tab_1]{1}. It is evident that the total of aboveground biomass and Belowground biomass content together as in Emblica officinalis, Mangifera indica, Tamarindus indica, Achras sapota, Annona reticulata and Annona squamosa for per hectare observed were 63.31 Kg ha -1 , 58.14 Kg ha -1 , 67.32 Kg ha -1 , 23.65 Kg ha -1 , 153 Kg ha -1 and 135 Kg ha -1 respectively (Table \hyperref[tab_1]{1} \& Fig.  {\ref 7}).\par
As per Table \hyperref[tab_1]{1} \& fig.  {\ref 8} the total of aboveground biomass and belowground biomass together as sequestered carbon stalk per hectare as estimated for Emblica officinalis was 33.07 Kg C ha -1 , in Mangifera indica it was 30.6 Kg C ha -1 , in Tamarindus indica it was 36.96 Kg C ha -1 , in Achras sapota it was 12.86 Kg C ha -1   , in Annona retiaculata it was 83.1 Kg C ha -1 and in Annona squamosa, it was 73.5 Kg C ha -1 .\begin{figure}[htbp]
\noindent\textbf{}\includegraphics[]{image-2.png}
\caption{\label{fig_0})}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{1}\includegraphics[]{image-3.png}
\caption{\label{fig_1}Fig. 1 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{2}\includegraphics[]{image-4.png}
\caption{\label{fig_2}Fig. 2 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{3}\includegraphics[]{image-5.png}
\caption{\label{fig_3}Fig. 3 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{4}\includegraphics[]{image-6.png}
\caption{\label{fig_4}Fig. 4 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{5}\includegraphics[]{image-7.png}
\caption{\label{fig_5}Fig. 5 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{6}\includegraphics[]{image-8.png}
\caption{\label{fig_6}Fig. 6 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{}\includegraphics[]{image-9.png}
\caption{\label{fig_7}}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{78}\includegraphics[]{image-10.png}
\caption{\label{fig_8}Fig. 7 :Fig. 8 :}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{} \par 
\begin{longtable}{P{0.24479999999999996\textwidth}P{0.07479999999999999\textwidth}P{0.0272\textwidth}P{0.0136\textwidth}P{0.2856\textwidth}P{0.17\textwidth}P{0.034\textwidth}}
\multicolumn{4}{l}{Carbon percentage in Emblica officinalis}\tabcellsep \multicolumn{2}{l}{Emblica officinalis}\\
54\tabcellsep \tabcellsep \tabcellsep \tabcellsep Root\tabcellsep Leaves\\
52\tabcellsep \tabcellsep \tabcellsep \tabcellsep 21\%\tabcellsep 17\%\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep Stem\\
50\tabcellsep \tabcellsep \tabcellsep \tabcellsep Bark\tabcellsep 20\%\\
48\tabcellsep \tabcellsep \tabcellsep \tabcellsep 21\%\tabcellsep Branches\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep 21\%\\
46\tabcellsep \tabcellsep \tabcellsep \tabcellsep \\
Leaves\tabcellsep \multicolumn{3}{l}{Stem Branches Bark}\tabcellsep Root\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep 2011\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \multicolumn{2}{l}{Tamarindus indica}\\
54\tabcellsep \tabcellsep \tabcellsep \tabcellsep \multicolumn{2}{l}{Root}\tabcellsep Leaves\\
52\tabcellsep \tabcellsep \tabcellsep \tabcellsep \multicolumn{2}{l}{20\%}\tabcellsep 19\%\\
50\tabcellsep \tabcellsep \tabcellsep \tabcellsep Bark\tabcellsep Stem\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep 20\%\tabcellsep 21\%\\
48\tabcellsep \tabcellsep \tabcellsep \tabcellsep \multicolumn{2}{l}{Branches}\\
46\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep 20\%\\
Leaves\tabcellsep Stem\tabcellsep Branches\tabcellsep Bark\tabcellsep Root\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep C )\\
\tabcellsep \tabcellsep \tabcellsep \tabcellsep \tabcellsep (\end{longtable} \par
  {\small\itshape [Note: DecemberPotentiality of Carbon Sequestration in Six Year Ages Young Plant from University Campus of Aurangabad]} 
\caption{\label{tab_0}Carbon percentages in Tamarindus indica}\end{figure}
 \begin{figure}[htbp]
\noindent\textbf{1} \par 
\begin{longtable}{P{0.32623239436619716\textwidth}P{0.11672535211267607\textwidth}P{0.13767605633802818\textwidth}P{0.1316901408450704\textwidth}P{0.13767605633802818\textwidth}}
Tree species\tabcellsep Specific\tabcellsep Biomass\tabcellsep Biomass\tabcellsep Carbon\\
\tabcellsep gravity\tabcellsep (Kg/tree)\tabcellsep (Kg ha -1 )\tabcellsep (Kg C ha -1 )\\
Emblica officinalis\tabcellsep 0.63\tabcellsep 0.067\tabcellsep 63.31\tabcellsep 33.07\\
Mangifera indica\tabcellsep 0.56\tabcellsep 0.038\tabcellsep 58.14\tabcellsep 30.6\\
Tamarindus indica\tabcellsep 0.50\tabcellsep 0.051\tabcellsep 67.32\tabcellsep 36.96\\
Achras sapota\tabcellsep 0.54\tabcellsep 0.057\tabcellsep 23.65\tabcellsep 12.86\\
Annona reticulata\tabcellsep 0.43\tabcellsep 0.102\tabcellsep 153\tabcellsep 83.1\\
Annona squamosa\tabcellsep 0.50\tabcellsep 0.090\tabcellsep 135\tabcellsep 73.5\end{longtable} \par
 
\caption{\label{tab_1}Table 1 :}\end{figure}
 			\footnote{© 2011 Global Journals Inc. (US)} 			\footnote{( C ) 2011 December University campus of Aurangabad, which is located at} 			\footnote{Global ) 2011 December ( C Potentiality of Carbon Sequestration in Six Year Ages Young Plant from University Campus of Aurangabad} 		 		\backmatter  			 
\subsection[{CONCLUSION}]{CONCLUSION}\par
The total carbon content of from Dr. B. A. M. University area were The total of AGB and BGB together as carbon stalk per hectare as estimated for Emblica officinalis was 33.07 Kg C ha -1 , in Mangifera indica it was 30.6 Kg C ha -1 , in Tamarindus indica it was 36.96 Kg C ha -1 , in Achras sapota it was 12.86 Kg C ha -1 , in Annona retiaculata it was 83.1 Kg C ha -1 and in Annona squamosa, it was 73.5 Kg C ha -1 respectively.			 			  				\begin{bibitemlist}{1}
\bibitem[Losi et al. ()]{b8}\label{b8} 	 		‘Analysis of alternative methods for estimating carbon stock in young tropical plantations’.  		 			C J Losi 		,  		 			T G Siccama 		,  		 			R Condit 		,  		 			J E Morales 		.  	 	 		\textit{Eco.Manag}  		2003. Elsevier for For. 184 p. .  	 
\bibitem[Negi et al. ()]{b9}\label{b9} 	 		‘Carbon allocation in different components of some tree species of India: A new approach for carbon estimation’.  		 			J D S Negi 		,  		 			R K Manhas 		,  		 			P S Chauhan 		.  	 	 		\textit{Current Science}  		2003. 85  (11)  p. .  	 
\bibitem[Ravindranath et al. ()]{b14}\label{b14} 	 		\textit{Carbon flow in Indian forests, submitted to the Ministry of Environment and Forest},  		 			N H Ravindranath 		,  		 			B S Somashekhar 		,  		 			M Gadgil 		.  		1997.  	 
\bibitem[Ravindranath and Ostwald ()]{b13}\label{b13} 	 		\textit{Carbon Inventory Methods Handbook for Greenhouse Gas Inventory, Carbon Mitigation and Round wood Production Projects},  		 			N H Ravindranath 		,  		 			M Ostwald 		.  		2008. Springer. 29.  	 
\bibitem[Dhruba ()]{b4}\label{b4} 	 		\textit{Carbon Sequestration Potential and uses of Dendrocalamus strictus},  		 			B G C Dhruba 		.  		2008. Nepal.  		 			to Tribhuwan University, Institute of Forestry 		 	 	 (A Thesis) 
\bibitem[Ranabhat et al. ()]{b12}\label{b12} 	 		‘Carbon sequestration potential of Alnus nepalensis in the Mid-hill of Nepal: A case study from Kaski district’.  		 			S Ranabhat 		,  		 			K D Awasthi 		,  		 			R Malla 		.  	 	 		\textit{Banko Janakari}  		2008. 18  (2)  p. .  	 
\bibitem[Jana et al. ()]{b7}\label{b7} 	 		‘Comparative Assessment of Carbon Sequestration Rate and Biomass Carbon Potential of Young Shorea robusta and Albizzia lebbek’.  		 			B K Jana 		,  		 			S Biswas 		,  		 			M Majumder 		,  		 			P K Roy 		,  		 			A Mazumdar 		.  	 	 		\textit{International Journal of Hydro-Climatic Engineering Assoc. Water and Enviro -Modeling}  		2009. p. .  	 
\bibitem[Environmental Status Report, Municipal Corporation ()]{b5}\label{b5} 	 		\textit{Environmental Status Report, Municipal Corporation},  		2009. Aurangabad.  		 			ESRAM 		 	 
\bibitem[Brown ()]{b1}\label{b1} 	 		\textit{Estimating Biomass and Biomass change of Tropical Forests: a Primer},  		 			S Brown 		.  		1997. Rome, Italy.  	 
\bibitem[FAO, Forestry Paper-134]{b2}\label{b2} 	 		\textit{FAO, Forestry Paper-134},  		165.  	 
\bibitem[Forda ()]{b6}\label{b6} 	 		 			Jica Forda 		.  		\textit{Manual of Biomass survey and Analysis},  				2005.  	 
\bibitem[Paladinic et al. ()]{b10}\label{b10} 	 		‘Forest biomass and sequestered carbon estimation according to main tree components on the forest stand scale’.  		 			E Paladinic 		,  		 			D Vuletic 		,  		 			I Martinic 		,  		 			H Marjanovic 		,  		 			K Indir 		,  		 			M Benko 		,  		 			V Novotny 		.  	 	 		\textit{Periodicum Biologorum}  		2009. 111  (4)  p. .  	 
\bibitem[Allen et al. ()]{b0}\label{b0} 	 		‘Method in Plant Ecology’.  		 			S E Allen 		,  		 			H M Grimshaw 		,  		 			A P Rowland 		.  	 	 		\textit{America}  		P.D. Moore and Chapman (ed.)  		1986. Blackwell Scientific Publications. p. .  	 	 (Chemical Analysis) 
\bibitem[Rajput et al. ()]{b11}\label{b11} 	 		 			S S Rajput 		,  		 			N K Shukla 		,  		 			V K Gupta 		,  		 			J D Jain 		.  		\textit{Timber Mechanics: Strength Classification and Grading of Timber. ICFRE Publication-38},  				 (New Forest, Dehradun)  		1996.  	 
\bibitem[Chavan and Rasal ()]{b3}\label{b3} 	 		\textit{Sequestered standing carbon stock in selective tree species grown in University campus at},  		 			B L Chavan 		,  		 			G B Rasal 		.  		2010. Aurangabad, Maharashtra, India. IJEST. 2 p. .  	 
\end{bibitemlist}
 			 		 	 
\end{document}
