1. Introduction
In India, a number of exotic pulpwood tree species such as
Eucalyptus, Casuarina, Leucaena, and
Populus are currently promoted by industrial sectors that require specific agro- climatic conditions for better growth and targeted yield
[1] | Chauhan RS, Jadeja DB, Thakur NS, Jha SK, Sankanur MS (2018). Selection of Candidate Plus Trees (CPTs) of Malabar Neem (Meliadubia Cav.) for Enhancement of Farm Productivity in South Gujarat. International Journal of Current Microbiology and Applied Sciences 7(05): 3582-3592. https://doi.org/10.20546/ijcmas.2018.705.414 |
[1]
. By contrast,
Dalbergia sissoo,
Gmelina arborea,
Melia dubia and
Neolamarkia cadamba are some of the indigenous, relatively fast- growing alternative pulpwood species that could be adaptable to a wide range of agro-climatic conditions
[2] | Thakur NS, Mohanty S, Hegde HT, Chauhan RS, Gunaga RP et al. (2019). Performance of Meliadubia under Cymbopogon spp. based agroforestry systems, Journal of Tree Sciences 38(1): 28-34. https://doi.org/10.5958/2455-7129.2019 |
[2]
. Among these indigenous tree species,
Melia dubia, due to its amenable nature in agroforestry systems and without causing any deleterious effects on under storied agricultural crops, is often advocated for inclusion in agroforestry
[3] | Parmar AG, Thakur NS, Gunaga R (2018). Meliadubia Cav. leaf litter allelochemicals have ephemeral allelopathic proclivity. Agroforestry systems 93(4): 1347- 1360. https://doi.org/10.1007/s10457-018-0243-5 |
[3]
. From an industrial point of view,
Melia dubia is one of the highly suitable raw materials for the pulp and paper industry, considering its high pulp recovery and fibre strength
[4] | Saravanan V, Parthiban KT, Kumar P, Marimuthu P (2013). Wood characterization studies on Meliadubia Cav for pulp and paper industry at different age gradation. Research Journal of Recent Science 2: 183-188. |
[4]
. Further, the inclusion of
Melia dubia in agroforestry has been found to be superior to exotic plantations in terms of economic returns and ecological restoration
[5] | Prajapati DR, Thakur NS, Gunaga RP, Patel VR, Mevada RJ, Bhuva DC (2020). Growth performance of Meliadubia in sole and Meliadubia- sorghum sudan grass silvi- pasture systems: sorghum sudan grass intercropping implications. International Journal of Current Microbiology and Applied Sciences 9(4): 726-732. https://doi.org/10.20546/ijcmas.2020.904.086 |
[5]
.
Spatial arrangement of plantations plays an important role in increasing the growth and yield of trees. The choice of planting density is the primary silvicultural decision, which influences the total stand volume, quality, and quantity of wood products throughout the rotation, as they compete for above-ground factors like sunlight, aeration and below-ground factors like space, water, and nutrients
[6] | Patil HY, Karatangi G, Kirankumar, Mutanal SM (2017). Growth and productivity of Meliadubia under different plant density. International Journal of Forestry and Crop Improvement 8(1): 30-33. https://doi.org/10.15740/HAS/IJFCI/8.1/30-33 |
[6]
. Furthermore, the influence of stand density on above and below ground biomass of
Melia dubia is associated with many uncertainties, which prevent clear management recommendations for small landholders. Economically, however, the production optimization should be based on the value of the products, particularly wood assortments. While
Melia dubia has a coppicing nature, more economic benefits will be pronounced in the second harvest, as around 60% of the plantation establishment cost is spent on plantation establishment such as land development, cost of planting material, and planting expenses. An optimal stand density will considerably reduce the establishment cost.
Therefore, to improve land utilization in semiarid zones under small and marginal land-holding patterns, spatial arrangement is to be optimized based on the purpose for which plantations are grown. For example, the timber and plywood industry needs attention to individual tree size rather than the total volume of plantations with 8-year rotational period. On the other hand, industries like pulp and paper concerned with the volume of wood rather than the size of individual trees with a rotational period of 3 to 5 years. However, studies on the influence of different stand densities on the pulpwood production of Melia dubia are rare so far, necessitating a comprehensive investigation in this regard.
Tree plantations also play a key role in restoring the fertility of soils, especially under semiarid conditions
[7] | Sumit, Arya S, Nanda K, Jangra M, Shivam (2024). Enhancing soil health and sustainability: the impact of Meliadubia based agro forestry in a semi- arid region of Haryana, India. International Journal of Plant and Soil Science 36(4): 369-377. https://doi.org/10.9734/IJPSS/2024/v36i44490 |
[7]
. For semiarid conditions, tree growth and biomass production are often controlled by factors such as climate and soil quality. The soils of semiarid regions usually contain low organic carbon, thus providing a great opportunity to sequester the atmospheric CO
2, and thereby restore soil fertility.
Melia dubia-based forest system has the potential to improve soil fertility
i.e. stabilizing soil physico-chemical properties and increasing nutrient contents by recycling available natural resources
[7] | Sumit, Arya S, Nanda K, Jangra M, Shivam (2024). Enhancing soil health and sustainability: the impact of Meliadubia based agro forestry in a semi- arid region of Haryana, India. International Journal of Plant and Soil Science 36(4): 369-377. https://doi.org/10.9734/IJPSS/2024/v36i44490 |
[8] | Qudir M, Oster JD, Schubert S, Nobel AD, Sahrawat KL (2007). Phytoremediation of sodic and saline sodic soils. Advances in Agronomy 96: 197–247. https://doi.org/10.1016/S0065-113(07)96006-X |
[9] | Carvalho AFD, Fernandes-FilhoEI, Daher M, Gomes LC, Cardoso IM et al. 2020. Microclimate and soil and water loss in shaded and unshaded agroforestry coffee systems. Agroforestry Systems. https://doi.org/10.1007/s10457-020-00567-6 |
[7-9]
. Planted forests are the widely accepted means of carbon sequestration, and for that reason, they offer a unique opportunity to combine the dual goals of climate change adaptation and mitigation
[10] | Narendar, Arya S, Nanda K, Yadav S, Singh T, Ranawat JS (2023). Potential of Meliadubia- wheat based agroforestry system to cope up with climate change. Environment Conservation Journal 24(2): 162-169. https://doi.org/10.36953/ECJ.13672402 |
[10]
.
The present study is based on the hypotheses that (1) higher stand densities increase competition among trees, reducing pulpwood yield, but maximizing carbon sequestration, (2) under lower stand densities, the pulpwood yield will increase due to the utilization of full natural resources while maintaining positive impacts on soil fertility (3) harvesting trees with larger diameters under low stand densities will increase productivity, reduce cost and save time, as fewer trees are required to harvest. The objectives of this study were to optimize tree density for Melia dubia pulpwood plantation, to find the effect of various stand densities (ranging from 2000 to 4444 trees per hectare) on pulpwood yield, improving soil fertility, and to assess carbon sequestration in a semiarid region.
2. Materials and Methods
2.1. Experimental Location and Soil Properties
Precision silvicultural experiment on
Melia dubia was carried out during January 2018 to December 2020 in the Plantation Research Block of Tamil Nadu Newsprint and Papers Limited (TNPL; N11°03.448’, E 077° 59.444’). The study location is classified as a semiarid region based on the prevailing temperature and annual rainfall
[11] | Seenivasan R, Prasath V, Mohanraj R (2014). Restoration of sodic soils involving chemical and biological amendments and phytoremediation by Eucalyptus camaldulensis in a semiarid region. Environmental Geochemistry and Health. https://doi.org/10.1007/s10653-014-9674-8 |
[11]
. The mean monthly rainfall and temperatures are shown in
Figure 1, indicating high to moderate temperatures throughout the year, with maximum rainfall occurs in the month of November. The physico-chemical and chemical properties of the experimental soil are depicted in
Table 1. The pH indicates slight alkalinity (7.59), and EC (0.17 dS m
-1) shows non-salinity nature of the soil. Total soil cations (TC) of 14.92 C mol (P
+)/ kg are considered low in status. The soil organic carbon content and available nutrients denote a low fertility level. The particle size distribution reveals a sandy loam texture, and the soil taxonomic classification was keyed out as
typic Ustorthents.
Figure 1. Mean annual rainfall and maximum and minimum temperatures recorded at the experimental site during the years 2018-2020. Error bars indicate standard deviations.
2.2. Experimental Details
Meliadubia clone GK-10, which has superior genetic features, is fast-growing and high-yielding was used in our experiment. The experiment was laid out in a randomized block design (RBD) and replicated three times. The details of different spacing adopted (which are the stocking levels widely practiced in commercial plantations of
Melia dubia in South India), plot area for each spacing treatment, number of trees per plot and tree density at different spacing are shown in
Table 2. Planting was carried out during January 2018 as per the spacing treatments, and after the establishment of plants, a fertigation dose of 150: 75: 150 NPK kg ha
-1 was applied in six equal splits to all the plots, irrespective of the spacings adopted. Necessary silvicultural operations were carried out throughout the experimental period. The pulpwood was harvested in January 2021 i.e. in 36 month- old plantation.
Table 1. Soil characteristics of the study location.
Parameters | Symbol | Units | Value |
Textural class | - | - | Sandy loam |
Bulk density | BD | Mg m3 | 1.52±0.04 |
pH | pH | - | 7.59±0.14 |
Electrical Conductivity | EC | dS m-1 | 0.17±0.02 |
Organic Carbon | SOC | mg kg-1 | 0.35±0.06 |
Total Cations | TC | C mol (P+) kg-1 | 14.92±0.28 |
KMnO4- N | Av-N | ppm | 79.46±1.79 |
Olsen- P | Av-P | ppm | 6.02±1.12 |
NH4OAc- K | Av-P | ppm | 172.62±4.24 |
Available Zn | Av-Zn | ppm | 9.57±1.07 |
Available Cu | Av-Cu | ppm | 4.27±0.41 |
Available Mn | Av-Mn | ppm | 7.26±0.36 |
Available Fe | Av-Fe | ppm | 7.92±0.27 |
Table 2. Spacing treatments / stand density evaluated in the Melia dubia plantation.
Treatment | Spacing | Plot area (m2) | Number of trees/ plot | Stand density (trees/ ha) |
S1 | 1.5 m × 1.5 m | 243 | 108 | 4444 |
S2 | 2.0 m × 2.0 m | 192 | 48 | 2500 |
S3 | 2.0 m × 2.5 m | 168 | 34 | 2000 |
S4 | 3.0 m × 1.5 m | 162 | 36 | 2222 |
2.3. Biometric Observations
The biometric observations,
viz. tree height and girth at breast height (GBH) at 36 months after planting, were measured to estimate the tree volume. All the trees were marked at 1.37 m from ground level, and the GBH was measured using a tailor’s tape and expressed in cm. The volume of standing trees was estimated using the formula according to Chaturvedi and Khanna
[12] | Chaturvedi AN, Khanna IS (1984). Forest mensuration. International Book distributers, Dehradun, Uttarakhand (India). |
[12]
and expressed in cubic meters (m
3):
Where V= volume of standing trees; r = radius at breast height; h=total height of the tree.
The monthly litter fall biomass (LFB) of the stand was collected starting from January 2019 to December 2020, from the subplots measuring 1m × 1m, demarcated within the treatment plots, and sorted into leaves, twigs and bark. The collected litter components were homogenized as per the treatment plots, and dried to a constant weight, weighed with the help of a weighing balance, and converted into kg ha-1 dry matter production (DMP).
Pulpwood yield, above-ground biomass (AGB) and below-ground biomass (BGB) estimation were done using the destructive sampling method in triplicate. Three representative trees in each plot were felled at ground level using a mechanical chainsaw (STIHL, India). The pulpwood yield was measured by weighing the harvested trees with the desired wood dimension (˃ 8 cm diameter) and converted into t ha-1 for all stand densities. Fresh weights (FW) of the above- ground tree components were recorded immediately after felling, which are considered AGB. After felling, the root portion of the trees was excavated and weighed as BGB. The AGB and BGB were converted into DMP after drying to a constant weight and expressed in t ha-1.
2.4. Soil Analysis
Soil samples collected at the standard depth of 0–45 cm were composited for each stand density. The bulk density of the soil samples was determined by the gravimetric method, which involves the division of total soil volume by the mass of oven dry soil, as suggested by Gupta and Dakshinamoorthy
[13] | Gupta R, Dakshinamoorthy C (1980). Procedure for physical analysis of soil and collection of agrometeorological data. Indian Agricultural Research Institute, New Delhi, pp 293. |
[13]
. Soil pH and EC (1: 2.5 soil: water ratio) were measured by the potentiometric method (LI120, ELICO pH meter, India) and a conductivity meter (611, Deep Vision, India) respectively, as advocated by Jackson
[14] | Jackson M (1973). Methods of chemical analysis: Prentice Hall of India (Pvt.) Ltd., New Delhi. |
[14]
. Soil organic carbon concentration was estimated by digesting 1 g of soil with 10 ml of 1N K
2Cr
2O
7, 20 ml of H
2SO
4, 10 ml of H
3PO
4, 10 ml of NaF, and titrating with 0.5N Fe(NH
4)
2(SO
4)
2.6H
2O
[15] | Walkley A, Black IA (1934). An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil Science 37(1): 29-38. http://dx.doi.org/10.1097/00010694-193401000-00003 |
[15]
. Available nitrogen was estimated by the alkaline KMnO4-Kjeldahl distillation method, in which 20 g of soil was distilled with 100 ml each of 0.32% KMnO
4 + 2.5% NaOH, the liberated ammonia was trapped in a boric acid- double indicator solution, and ammonia was quantified by titrating with 0.02N H
2SO
4 [16] | Subbiah G, Asija AL (1956). A rapid procedure for estimation of available nitrogen in soils. Current Science 125: 259–260. |
[16]
. The available phosphorus in 1.0 g of soil was extracted with 0.5 M NaHCO
3 (Olsen’s extract; Olsen et al., 1954) and measured using a spectrophotometer (Visican 167, Systronics, India) at 882 nm after the blue color developed with reagent A (12 g of [(NH
4)
6Mo
7O
24.4H
2O] and 0.2908 g of [K(SbO)C
4H
4O
6.1/2H
2O] in 2000 ml of 2.5 M H
2SO
4) and reagent B (1.056 g of C
6H
8O
6 dissolved in reagent A)
[17] | Olsen SR, Cole CV, Watanabe FS, Dean LA (1954). Estimation of available phosphorus in soils by extraction with sodium bicarbonate. United States Department of Agriculture Circulation 939, US Government Printing Office, Washington DC. |
[17]
. The available K was extracted by centrifuging 5 g of soil with 25 ml of neutral normal NH
4OAc at 2000 rpm for 10 minutes, and the K content was measured using a flame photometer (Model 1385, Deep Vision, India) as per the procedure by Tandon
[18] | Tandon HLS (2005). Methods of analysis of soils, plants, waters, fertilizers and organic manures. Fertilizer Development and Consultation Organization, New Delhi, India. |
[18]
. For the estimation of soil exchangeable cations (Ca
2+, Mg
2+, Na
+ and K
+) and available micronutrients (Zn
2+, Cu
2+, Mn
2+, and Fe
2+), 0.5 g of soil was digested with 20 ml of HNO
3 + 3 ml of H
2O
2 at 180 ± 5°C for 15 minutes in a microwave digestion unit (Ethos Easy, Milestone, Italy). The digested solutions were filtered, made up to a volume of 50 ml with ultrapure water and measured for exchangeable cations and available micronutrients using microwave plasma-Atomic Emission Spectrometry (MP 4200, Agilent Technologies, USA). The exchangeable cations and available micronutrients in the soil were expressed in C mol (P
+) kg
-1 of soil and mg kg
-1 of soil, respectively.
2.5. Estimation of C Sequestration Potential
The planted forests are considered C sinks as they directly sequester through photosynthesis and indirectly through biochemical reactions in the soil. For that reason, this study included the investigation of the C sequestration in different stand densities. The AGB, BGB and LFB were converted into fixed carbon by multiplying them by 0.50
[19] | Brown S, Lugo AE (1982). The storage and production of organic matter in tropical forests and their role in the global carbon cycle. Biotropica 14, 161–187. |
[19]
, and expanded to tha
-1. The carbon stock in the soil (Cs) was estimated using the formula of Post and Kwon
:
Where Cs = soil organic carbon stock (t ha-1); Cc = soil organic carbon concentration (g kg-1); D = soil depth (cm); BD = bulk density (g cm-3).
The carbon sequestration potential of
Melia dubia plantation was calculated by adding the carbon stocks in AGB + BGB + LFB + Cs
[21] | Du, H., Zeng, F., Peng, W., Wang, K., Zhang, H., Liu, L., Song, T. (2015). Carbon storage in eucalyptus plantation chronosequence in Southern China, Forests, 6, 1763-1778. https://doi.org/10.3390/f6061763 |
[21]
.
2.6. Statistical Analysis
The quantitative data were checked for normality and analyzed using univariate analysis of variance (ANOVA) to find the effect of different tree densities on tree growth parameters, pulpwood yield, above-ground and below-ground dry matter production and the carbon sequestration potential of Melia dubia plantation. Post hoc analysis was performed with Duncan’s multiple range test (P ˂ 0.05) when there was a significant difference among the variables. Results obtained from soil analysis in relation to different tree densities were subjected to principal component analysis (PCA) by performing the extraction in varimax rotation with Kaiser normalization, where the components were extracted for eigenvalues ˃1. All statistical analyses were conducted using SPSS version 29 (SPSS Inc., Chicago, USA).
3. Results and Discussion
3.1. Effect of Stand Density on Growth and Pulpwood Yield of Melia dubia Plantation
The influence of different stand densities on the growth parameters, stand volume, and pulpwood yield of
Melia dubia plantation is shown in
Table 3. The maximum height of individual trees was recorded at a tree density of 4444 trees per hectare (S1) with the spacing of 1.5 m × 1.5 m (
P ˂ 0.05). All other spacings were found statistically non-significant. It is because high stand density allows individual trees to have minimal branches with less crown density, which favors vertical growth of the trees rather than medial growth
[22] | Sharma D, Kumar A, Thakur S, Sagar N (2018). Initial growth performance of improved genotypes of Meliadubia in low hills of Himachal Pradesh. International Journal of Chemical Studies 6(6): 1847-1849. |
[22]
. The wider spacing of 3.0 m × 1.5 m with 2222 trees per hectare recorded the significantly highest GBH (
P ˂ 0.05) as compared to other treatments. The treatments S2 (2500 trees ha
-1) and S3 (2000 trees ha
-1) were statistically similar in recording higher tree GBH (
P ˂ 0.05). It is obvious that the GBH of individual trees always has a strong negative correlation with stand density
[23] | Andrzej W, Mariusz B, Agnieszka, Piotr SM (2018). Relationship between stand density and value of timber assortments: a case study for scots pine stands in north-western Poland. New Zealand Journal of Forestry Science. https://doi.org/10.1186/s40490-018-0117-7 |
[23]
. Generally, trees grow faster at lower stand density in terms of radial growth, and specific tree geometry primarily governs the uptake of water and nutrients from the soil and the capture of sunlight
[6] | Patil HY, Karatangi G, Kirankumar, Mutanal SM (2017). Growth and productivity of Meliadubia under different plant density. International Journal of Forestry and Crop Improvement 8(1): 30-33. https://doi.org/10.15740/HAS/IJFCI/8.1/30-33 |
[6]
. This may vary among genera and species within a genus under a particular climate. In the present study,
Melia dubia with 2222 trees ha
1 produced more cumulative volume compared to the near tree densities of 2000 trees ha
-1 (S3), and 2500 trees ha
-1 (S2), suggesting an ideal stocking level under semiarid climate for pulpwood production. The increment in tree GBH with wider spacing was due to reduced competition among trees in above-ground factors like sunlight, aeration and belowground factors like space for rooting, nutrient and water absorption
[24] | Henskens F, Battaglia M, Cherry M, Beadle CL (2001). Physiological basis of spacing effects on tree growth and form in Eucalyptus globulus. Trees Structure and Function 15: 365–377. https://doi.org/10.1007/s004680100114 |
[25] | Syed A, Vasudev KL, Devagiri GM, Ramakeishna H, Kumar N (2023). Growth performance of Meliadubia in the agroforestry in the central dry zone of Karnataka. International Journal of Biochemistry Research 7(2): 478- 481. https://doi.org/10.33545/26174693.2023.v7.i2Sg.254 |
[24, 25]
. These associations of increased height with high stand density and increased GBH with low stand density plantations have been reported on various tree species: Niessan
et al.
[26] | Niessan TM, Midmore DJ, Keeler AG (2001). Biophysical and economic trade-offs of intercropping timber with food crops in the Philippine uplands. Agricultural System 67: 49-69. https://doi.org/10.1016/S0308-521X(00)00049-4 |
[26]
in
Paraserianthes falcataria; Prasad
et al.
[27] | Prasad JVNS, Korwar GR, Rao KV, Mandal U (2011). Optimum stand density of Leucaenaleucocephala for wood production in Andra Pradesh, Southern India. Biomass and Bioenergy 35(1): 227-235. https://doi.org/10.1016/j.biombioe.2010.05.012 |
[27]
in
Leucaena leucocephala and Andrzej
et al.
[23] | Andrzej W, Mariusz B, Agnieszka, Piotr SM (2018). Relationship between stand density and value of timber assortments: a case study for scots pine stands in north-western Poland. New Zealand Journal of Forestry Science. https://doi.org/10.1186/s40490-018-0117-7 |
[23]
in
Pinus roxburghii). The significantly highest stand volume was recorded with the stand density of 4444 trees per hectare (
P ˂ 0.05), implying that stand volume is higher with high- density plantations and
vice versa. The increment in individual GBH is attributed to wider spacing, but the cumulative stand volume is attributed to the number of trees per unit area, suggesting a trade-off between individual tree growth and stand volume.
Table 3. Effect of stand density on growth and pulpwood yield of Melia dubia plantation.
Spacing | Individual tree height (m) | Individual tree GBH (cm) | Cumulative volume (m3) | Pulpwood yield (t ha-1) |
S1 | 9.04±0.68a | 22.99±0.84c | 0.60±0.03c | 89.04±3.54c |
S2 | 8.68±0.52b | 26.12±0.91b | 0.71±0.02b | 104.79±3.74b |
S3 | 8.70±0.74b | 26.89±0.54ab | 0.69±0.03ab | 103.42±4.54b |
S4 | 8.72±0.80b | 27.65±0.68a | 0.76±0.02a | 110.19±2.92a |
The pulpwood yield with the specified wood dimension in different stand densities is recorded in the order of S4 ˃ S2 ˃ S3 ˃ S1(
P ˂ 0.05). From
Table 2, it can also be observed that S2 with a tree density of 2500 trees per hectare is statistically on par with S3, with a tree density of 2000 trees ha
-1. The results of the present study support the hypothesis that site quality ultimately determines the productivity of tree species within certain stand densities and individual tree volumes
[23] | Andrzej W, Mariusz B, Agnieszka, Piotr SM (2018). Relationship between stand density and value of timber assortments: a case study for scots pine stands in north-western Poland. New Zealand Journal of Forestry Science. https://doi.org/10.1186/s40490-018-0117-7 |
[23]
, suggesting that a tree density ranging from 2000 to 2500 trees per hectare is optimal for raising
Melia dubia plantations. A similar finding of increased wood productivity with stand density to a range of 2000 - 2500 trees per hectare in the
Melia dubia plantation was reported by Prajapathi
et al.
[5] | Prajapati DR, Thakur NS, Gunaga RP, Patel VR, Mevada RJ, Bhuva DC (2020). Growth performance of Meliadubia in sole and Meliadubia- sorghum sudan grass silvi- pasture systems: sorghum sudan grass intercropping implications. International Journal of Current Microbiology and Applied Sciences 9(4): 726-732. https://doi.org/10.20546/ijcmas.2020.904.086 |
[5]
, Patil
et al.
[6] | Patil HY, Karatangi G, Kirankumar, Mutanal SM (2017). Growth and productivity of Meliadubia under different plant density. International Journal of Forestry and Crop Improvement 8(1): 30-33. https://doi.org/10.15740/HAS/IJFCI/8.1/30-33 |
[6]
, and Syed
et al.
[25] | Syed A, Vasudev KL, Devagiri GM, Ramakeishna H, Kumar N (2023). Growth performance of Meliadubia in the agroforestry in the central dry zone of Karnataka. International Journal of Biochemistry Research 7(2): 478- 481. https://doi.org/10.33545/26174693.2023.v7.i2Sg.254 |
[25]
. However, within this range, our results indicate that a stand density of 2222 trees ha
-1 is ideal for
Melia dubia pulpwood plantations in low-nutrient soil under semiarid conditions.
3.2. Effect of Stand Density on Post Harvest Soils of Melia dubia Plantation
Figure 2. Effect of stand density on the soil physico- chemical characteristics: a) soil pH; b) soil EC; c) soil organic carbon; d) total cations. Data are presented as mean ± SD (n = 3). Different alphabets in the corresponding parameters are significantly different according to DMRT atP ˂ 0.05.
The pH of the post- harvest
Melia dubia planted soil in some stand densities was found to be reduced as compared to the initial soil pH of 7.76 (
Figure 2). While the reduction ranged from 2.11% in S4 (2222 trees ha
-1) to 3.82% in S1 (4444 trees ha
-1), the soil pH remained unaltered with the stand density of 2000 trees per hectare (S3). Litter decomposition, soil respiration (CO
2 emission), microbial respiration, and root respiration resulted in a reduction in soil pH
. More reduction with high stand density may be ascribed to higher below-ground biomass production
[28] | Diaz MJ, Garcia MM, Eugenio ME, Tapias R, Fernandez M, Lopez F (2007). Variations in fiber length and some pulp chemical properties of Leucaena varieties. Industrial crop and products 26: 142-150. https://doi.org/10.1016/j.indcrop.2007.02.003 |
[28]
. More than a twofold increase in soil EC was observed in the plots with higher stand densities of 4444 trees ha
-1 and 2500 trees per hectare. An increase of about 88% was observed with 2222 trees ha
-1 and the least increment of 29% with 2000 trees per hectare was recorded with regard to soil EC. This can be ascribed to the fact that our experimental soil was non-saline and no excess salts were present to leach out from the soil system in initial stages. In later stages, the release of salts by weathering the native minerals due to raised plantations (rhizo-acidification and solubilization) contributed to increasing the soil EC
[11] | Seenivasan R, Prasath V, Mohanraj R (2014). Restoration of sodic soils involving chemical and biological amendments and phytoremediation by Eucalyptus camaldulensis in a semiarid region. Environmental Geochemistry and Health. https://doi.org/10.1007/s10653-014-9674-8 |
[11]
. The significantly highest SOC of 0.70 mg kg
-1 was recorded in the soil under the highest stand density (S1; 4444 trees per hectare), implying that a strong positive correlation exists between SOC and the number of trees per unit area (
Figure 1). The growth increment of the
Melia dubia plantation contributed to the buildup of soil organic carbon indirectly through increased root biomass
[10] | Narendar, Arya S, Nanda K, Yadav S, Singh T, Ranawat JS (2023). Potential of Meliadubia- wheat based agroforestry system to cope up with climate change. Environment Conservation Journal 24(2): 162-169. https://doi.org/10.36953/ECJ.13672402 |
[21] | Du, H., Zeng, F., Peng, W., Wang, K., Zhang, H., Liu, L., Song, T. (2015). Carbon storage in eucalyptus plantation chronosequence in Southern China, Forests, 6, 1763-1778. https://doi.org/10.3390/f6061763 |
[10, 21]
.
Likewise, the total cations consisting of Ca
++, Mg
++, Na
+, and K
+ were also increased in the post harvest soil due to the planting of
Melia dubia. Similarly, in the organic carbon content of the soil, the highest cationic increment in the soil was observed with S1 (4444 trees ha
-1), and the least increment was noticed with S3 (2000 trees ha
-1). Generally, tree plantations with a deep root system acidify the soil rhizosphere and solubilize/ release the fixed cations in the exchangeable sites, resulting in increased exchangeable cations
. The increase in the soil organic carbon content also enhances the exchangeable cations in the soil as the ion exchange capacity of the soil is very strongly related to soil organic matter content
[29] | Solly EF, Weber V, Zimmermann S, Walthert L, Hagedorn F, Schmidt MWI (2020). A critical evaluation of the relationship between the effective cation exchange capacity and soil organic carbon content in Swiss forest soils. Frontiers in Forests and Global Change 3: 98. https://doi.org/10.3389/ffgc.2020.00098 |
[29]
. Further, the phenological behavior of
Melia dubia being deciduous helps in the conservation of moisture in soil which aids in the weathering of minerals and mineralization of organic compounds
[9] | Carvalho AFD, Fernandes-FilhoEI, Daher M, Gomes LC, Cardoso IM et al. 2020. Microclimate and soil and water loss in shaded and unshaded agroforestry coffee systems. Agroforestry Systems. https://doi.org/10.1007/s10457-020-00567-6 |
[9]
. All these reactions in the
Melia dubia planted soil system resulted in more cationic ion release and made it in an exchangeable form.
As depicted in
Table 4, the content of all the nutrients in post-harvest soils has increased when compared with their initial values. The highest soil N, P, and K contents were found in the plot with a low tree density of 2000 trees per hectare (S3; (
P ˂ 0.05). A spur in microbial activity because of the litter fall and root biomass facilitated nutrient recycling within the system, which contributed to increased soil N content
[30] | Ngoran A, Zakra N, Ballo K, Kouam EC, Zapt AF, Hofman G, Cleemant OV (2006). Litter decomposition of Acacia auriculiformis and Acacia mangium under coconut trees on quaternary sandy soils in Ivory Coast. Biology and Fertility of Soils 43: 102−106. https://doi.org/10.1007/s0374-005-0065-2 |
[30]
. This phenomenon was evidenced by a decrease in pH (acidification), an increase in EC (mineralization), and an increase in organic carbon content (decomposition) of the soil. The increased availability in
Melia dubia plantation can be ascribed to the production of glucose in root exudates and the solubilization of fixed forms of phosphates
. The minimal loss of K ions through leaching and fixation of excess K ions in the exchangeable sites might be the reason for enhanced K availability in our experimental soil. In general, around 70- 80% of the applied K is retained on-site through belowground root biomass and litter fall in the plantation crops
[6] | Patil HY, Karatangi G, Kirankumar, Mutanal SM (2017). Growth and productivity of Meliadubia under different plant density. International Journal of Forestry and Crop Improvement 8(1): 30-33. https://doi.org/10.15740/HAS/IJFCI/8.1/30-33 |
[6]
. It can be observed that there is an increase in the available micronutrients of the post-harvest soil in all the plots as compared to their initial values. The increments ranged from 8.3 to 13.9% in Zn, 8.1 to 10.9% in Cu, 4.5 to 7.4% in Mn and 3.5 to 6.1% in Fe, respectively. However, differences between the various stand densities were not statistically significant (
P ˂ 0.05) in this regard. The stabilization of soil pH and increased SOC contributed to the increase in available micronutrients of the soil
[32] | Dhaliwal SS, Naresh RK, Mandal A, Singh R and Dhaliwal MK (2019). Dynamics and transformation of micronutrients in agricultural soils as influenced by organic matter build-up: a review. Environmental and Sustainability Indicators 1-2: 100007. https://doi.org/10.1016/j.indic.2019.100007 |
[32]
.
Table 4. Effect of various stand densities on the available nutrients in the post-harvest soils of Melia dubia plantation.
Stand density | KMnO4-N (ppm) | Olsen-P (ppm) | NH4OAc-K (ppm) | Av-Zn (ppm) | Av-Cu (ppm) | Av-Mn (ppm) | Av-Fe (ppm) |
S1 | 79.38c | 7.08c | 171.00c | 10.36a | 4.62a | 7.58a | 8.20a |
S2 | 84.81bc | 8.05b | 176.27bc | 10.59a | 4.66a | 7.64a | 8.29a |
S3 | 92.94a | 9.64a | 187.48a | 10.90a | 4.73a | 7.80a | 8.40a |
S4 | 86.07b | 8.39b | 180.80b | 10.67a | 4.69a | 7.72a | 8.36a |
Figure 3. Loading plots of principal component analysis (PCA). BD- bulk density; OC- organic carbon; EC- electrical conductivity; ExgCa- exchangeable Ca; ExgMg- Exchangeable Mg; ExgNa- exchangeable Na; ExgK- exchangeable K; all other plant nutrients denote their available forms in the soil.
Principal component analysis (PCA) provides loading plots to assess the influence of different tree densities on soil fertility parameters (
Figure 3). Accordingly, the soil pH and bulk density (BD) were negatively correlated with the number of trees per unit area. A substantial increase in soil electrical conductivity, organic carbon, and exchangeable cations (Ca
++, Mg
++, Na
+ and K
+) was observed and positively correlated with the stand density of
Melia dubia plantation. The available major (N, P, and K) and micro (Zn, Cu, Mn, and Fe) were also increased or stabilized with the plantation despite appreciable biomass production. As discussed earlier, the production of below ground root biomass and mineralization of organic matter including litter fall facilitated to the improvement of soil fertility parameters. The findings of our present study are in accordance with the results of Sumit
et al.
[7] | Sumit, Arya S, Nanda K, Jangra M, Shivam (2024). Enhancing soil health and sustainability: the impact of Meliadubia based agro forestry in a semi- arid region of Haryana, India. International Journal of Plant and Soil Science 36(4): 369-377. https://doi.org/10.9734/IJPSS/2024/v36i44490 |
[7]
in increasing the overall soil fertility (enhancing soil physico-chemical properties and available nutrients) under
Melia dubia based agroforestry system in semiarid climate conditions.
3.3. Effect of Stand Density on Carbon Sequestration Potential of Melia dubia Plantation
Planted forests absorb atmospheric CO
2 through photosynthesis and primarily store it in the form of aboveground and belowground- biomass, in addition to fixing in the soil, making it a nature-based solution to mitigate global warming. Further, the optimization of stand density will provide climate-smart forestry, where carbon storage is enhanced further
[33] | Bai, Y. and Ding, G. (2024). Estimation of changes in carbon sequestration and its economic value with various stand density and rotation age of Pinus massoniana plantations in China. Scientific Reports 14, 16852. https://doi.org/10.1038/s41598-024-67307-z |
[33]
.
Melia dubia is one excellent tree species that could be adopted to trap atmospheric carbon, in addition to the economic benefits from biomass, particularly in semiarid regions
[7] | Sumit, Arya S, Nanda K, Jangra M, Shivam (2024). Enhancing soil health and sustainability: the impact of Meliadubia based agro forestry in a semi- arid region of Haryana, India. International Journal of Plant and Soil Science 36(4): 369-377. https://doi.org/10.9734/IJPSS/2024/v36i44490 |
[7]
.
Figure 4. Carbon sequestration in Melia dubia plantation at different stand densities. Error bars indicate standard deviations (n = 3). Different alphabets in the corresponding parameters are significantly different at P ˂ 0.05 according to DMRT.
In the present study, the highest above- and below- ground DMP were recorded in the stand density of 4444 trees per hectare at the pulpwood rotational period of three years. All other densities were statistically on par in producing stem and root DMP (
P ˂ 0.05;
Figure 4). The highest leaf DMP was recorded with the treatment S1, but remained non-significant compared to all other spacings. This might be because, under semiarid irrigated conditions,
Melia dubia trees effectively utilized the energy exerted through photosynthesis for the accumulation of above and below- ground biomass. The significantly highest total carbon sequestration (TCS) was found with S1, followed in the order of S2 ˃ S4 ˃ S3, suggesting that carbon sequestration in
Melia dubia-based plantations has a strong positive correlation with stand density rather than individual tree growth. However, in the case of large-scale pulpwood plantations, the economic returns and associated environmental benefits such as carbon sequestration will be more pronounced by adopting the desired tree density level. Such carbon stock assimilation can have additional benefits in carbon offset programs and climate mitigation mechanisms
[34] | Sugumarn MP, Porkodi G, Kalaichelvi K, Atchaya S, Thangeswari S (2024). Evaluating the impact of elevated temperature on Melia dubia: insights into climate change resilience and adaptation. International Journal of Environment and Climate Change 14(3): 139- 148. https://doi.org/10.9734/IJECC/2024/v14i34026 |
[34]
.