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Silviculture in Shorea robusta in West Bengal (INDIA )
Introduction:-
 Forests cover over 11 million hectare in India and
Nepal which occurs on the southern slopes of
Himalaya and distributed in Bangladesh.
 Sal forest silviculture has been evolving since the
beginning of 20th century.
 Sal trees used for timber production, grazing,
collection of fodder, fuelwood , litter and many
other products.
 Broadly Sal's natural range lies between the
longitude of 75 degree and 95 degree East and
latitudes of 20 degree to 32 degree North.
 It extends from few meters to 1500 m above mean
sea level. Natural zone of Sal forests (shaded dots for Sal forests, after
Stainton, 1972 ; FAO, 1985 ).
Ecology and productivity of Sal:-
Stand structure:-
 45m height, 25 m clear bole and a girth of 8m.
 Canopy reaches a height of 30-35m and trees have a girth of
4m in favorable localities.
Edaphic factors:-
 Grows on wide range of soil types, except in sandy, gravely soils
adjoining rivers and in waterlogged area.
 It can grow on alluvial to lateritic soils (pH 5.1 – 6.8) and with carbon
content between 0.11 and 1.8%.
 Precipitation ranges from 1000- 2000 mm.
 Tolerates maximum temperature 49 degree and minimum -1 degree .
Phenology:-
 Depends on edaphic factors and microclimate.
 Produce seeds every year but a good seed year normally after third
year.
 Leaf starts fall in the mid of February to mid of July.
Progression and retrogression of dry Sal forest (based on Maithani et al., 1989 ).
Silviculture practices:- It is an art and science of managing forests for
specific objectives outlined by a landowner. (Smith et al. 1997)
Coppice system:-
Simple coppice system
Coppice with standards
Coppice with reserves.
Regeneration:-
Sal regenerates from seed or by coppicing sprouting from root
suckers.
Tree of both coppice and seed origin produce fertile seeds
(there is no difference in the vigor of the seedlings from
coppice or seed origin).
During increase in age, the standing biomass increased in the
Sal plantation and natural stands and non-photosynthetic :
photosynthesis ratio also increased.
Artificial regeneration:-
 Clear felled coups by direct sowing.
 Need moist ground.
 Each Sal line consists of 3 rows of seeds, the rows being
15cm apart and 8 cm dibbled.
 In south west Bengal, Sal lies in degraded condition over
a large area and its regenerated by the method of
coppicing.
 Liable to damage by drought.
 Vulnerable to damage by large number of
fungi.
 The serious attacks by Hoplocerambyx
spinicornis beetle have been reported from
various part of country.
Injury, damages:-
Conclusion:-
 The degradation of Sal forests resulted from heavy and haphazard looping, grazing and fire.
 Ecological processes stand development clearly show rich diversity at the ground level, but decreasing
diversity with height and ultimately Sal dominance at the top canopy.
 Edaphic factors, regeneration, growth characteristics, allocations, and structure are contributors to ecological
processes.
 Leaf shedding creates opportunities to regenerate many species of ground flora.
 Anthropogenic factors are influenced by the livelihoods of the population living in and around Sal forests.
References:-
• Fu, Q.H. 1994. Dipterocarp trees in Hinan Island, South China. Trop. For.30, 55-59. retrieved from :- https://books.google.com.au/books?id=8EQCyZAZ9-
cC&pg=PA6&lpg=PA6&dq=dipterocarp+trees+in+Hainan+Island,+South+China.+Trip&source=bl&ots=_yJ2xnkACK&sig=ACfU3U33qafYAwj1omwsDq
4uS8ZVtUAY-g&hl=en&sa=X&ved=2ahUKEwjm8Pjem9npAhXMz.
• Jackson,J.K. 1994. Manual OF Afforestation in Nepal. Forest research and survey centre, Kathmandhu. Retrieved from :-
https://books.google.com.au/books?id=G9x-
8pK3K64C&pg=PA128&dq=Manual+OF+Afforestation+in+Nepal.+Forest+research+and+survey+centre,+Kathmandu.&hl=en&sa=X&ved=0ahUKEwi_1I
PXnNnpAhXowTgGHUKfA1wQ6AEIKzAA#v=onepage&q=Manual%20OF%20Afforestation%20in%20Nepal.%20Forest%20research%20and%20survey
%20centre%2C%20Kathmandu.&f=false.
• Pokhriyal, T.c., Ramola, B.C. and Raturi, A.S. 1987. Soil moisture regime and nitrogen content in natural sal forest (Shorea robusta). Indian For. 113,300-
306. Retrieved from :- https://www.semanticscholar.org/paper/Soil-Moisture-Regime-and-Nitrogen-Content-in-Sal-(-Pokhriyal-
Ramola/3a3e4413d0e324fdd5d67d7401542946e06a5c34.
• Rana, B.S., Singh, S.P. and Singh, R.P.(1988). Biomass and productivity of central Himalayan sal (Shorea robusta) forest. Trop. Ecol.29,1-7. retrieved from
:-
https://books.google.com.au/books?id=8byxDwAAQBAJ&pg=PA172&lpg=PA172&dq=Biomass+and+productivity+of+central+Himalayan+sal+(Shorea+r
obusta)+forest&source=bl&ots=jpHZJxT-
Jk&sig=ACfU3U3cs0zIxqMIpgDIhgH1a7vMFEdJIQ&hl=en&sa=X&ved=2ahUKEwi09df3ntnpAhUazjgGHR5GB_IQ6AEwBnoECAsQAQ#v=onepage&q
=Biomass%20and%20productivity%20of%20central%20Himalayan%20sal%20(Shorea%20robusta)%20forest&f=false.
• Yadav, V.K., Khare, P.K. And Mishra, G.P. (1986). Effect of tree girth on seed viability and germination in sal. Trop. 2, 160-163. retrieved from :-
https://www.researchgate.net/publication/281609791_Seed_Germination_and_Seedling_Survival_Percentage_of_Shorea_robusta_Gaertnf_in_Buffer_Areas_
of_Similipal_Biosphere_Reserve_Odisha_India.
• Hao,L., Cao, B., Wang, F, and Yzaki, Y.(1994). Chinese wattle tannin adhesives suitable for producing exterior grade plywood in China. Holz Rob Werks.
52, 113-118. retrieved from :- https://www.semanticscholar.org/paper/Chinese-wattle-tannin-adhesives-for-exterior-grade-Zhao-
Cao/626539513e2201be78fd559f17e25cb02156cc90.

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Silviculture of sal tree

  • 1. Silviculture in Shorea robusta in West Bengal (INDIA )
  • 2. Introduction:-  Forests cover over 11 million hectare in India and Nepal which occurs on the southern slopes of Himalaya and distributed in Bangladesh.  Sal forest silviculture has been evolving since the beginning of 20th century.  Sal trees used for timber production, grazing, collection of fodder, fuelwood , litter and many other products.  Broadly Sal's natural range lies between the longitude of 75 degree and 95 degree East and latitudes of 20 degree to 32 degree North.  It extends from few meters to 1500 m above mean sea level. Natural zone of Sal forests (shaded dots for Sal forests, after Stainton, 1972 ; FAO, 1985 ).
  • 3. Ecology and productivity of Sal:- Stand structure:-  45m height, 25 m clear bole and a girth of 8m.  Canopy reaches a height of 30-35m and trees have a girth of 4m in favorable localities. Edaphic factors:-  Grows on wide range of soil types, except in sandy, gravely soils adjoining rivers and in waterlogged area.  It can grow on alluvial to lateritic soils (pH 5.1 – 6.8) and with carbon content between 0.11 and 1.8%.  Precipitation ranges from 1000- 2000 mm.  Tolerates maximum temperature 49 degree and minimum -1 degree .
  • 4. Phenology:-  Depends on edaphic factors and microclimate.  Produce seeds every year but a good seed year normally after third year.  Leaf starts fall in the mid of February to mid of July. Progression and retrogression of dry Sal forest (based on Maithani et al., 1989 ).
  • 5. Silviculture practices:- It is an art and science of managing forests for specific objectives outlined by a landowner. (Smith et al. 1997) Coppice system:- Simple coppice system Coppice with standards Coppice with reserves.
  • 6. Regeneration:- Sal regenerates from seed or by coppicing sprouting from root suckers. Tree of both coppice and seed origin produce fertile seeds (there is no difference in the vigor of the seedlings from coppice or seed origin). During increase in age, the standing biomass increased in the Sal plantation and natural stands and non-photosynthetic : photosynthesis ratio also increased.
  • 7. Artificial regeneration:-  Clear felled coups by direct sowing.  Need moist ground.  Each Sal line consists of 3 rows of seeds, the rows being 15cm apart and 8 cm dibbled.  In south west Bengal, Sal lies in degraded condition over a large area and its regenerated by the method of coppicing.
  • 8.  Liable to damage by drought.  Vulnerable to damage by large number of fungi.  The serious attacks by Hoplocerambyx spinicornis beetle have been reported from various part of country. Injury, damages:-
  • 9. Conclusion:-  The degradation of Sal forests resulted from heavy and haphazard looping, grazing and fire.  Ecological processes stand development clearly show rich diversity at the ground level, but decreasing diversity with height and ultimately Sal dominance at the top canopy.  Edaphic factors, regeneration, growth characteristics, allocations, and structure are contributors to ecological processes.  Leaf shedding creates opportunities to regenerate many species of ground flora.  Anthropogenic factors are influenced by the livelihoods of the population living in and around Sal forests.
  • 10. References:- • Fu, Q.H. 1994. Dipterocarp trees in Hinan Island, South China. Trop. For.30, 55-59. retrieved from :- https://books.google.com.au/books?id=8EQCyZAZ9- cC&pg=PA6&lpg=PA6&dq=dipterocarp+trees+in+Hainan+Island,+South+China.+Trip&source=bl&ots=_yJ2xnkACK&sig=ACfU3U33qafYAwj1omwsDq 4uS8ZVtUAY-g&hl=en&sa=X&ved=2ahUKEwjm8Pjem9npAhXMz. • Jackson,J.K. 1994. Manual OF Afforestation in Nepal. Forest research and survey centre, Kathmandhu. Retrieved from :- https://books.google.com.au/books?id=G9x- 8pK3K64C&pg=PA128&dq=Manual+OF+Afforestation+in+Nepal.+Forest+research+and+survey+centre,+Kathmandu.&hl=en&sa=X&ved=0ahUKEwi_1I PXnNnpAhXowTgGHUKfA1wQ6AEIKzAA#v=onepage&q=Manual%20OF%20Afforestation%20in%20Nepal.%20Forest%20research%20and%20survey %20centre%2C%20Kathmandu.&f=false. • Pokhriyal, T.c., Ramola, B.C. and Raturi, A.S. 1987. Soil moisture regime and nitrogen content in natural sal forest (Shorea robusta). Indian For. 113,300- 306. Retrieved from :- https://www.semanticscholar.org/paper/Soil-Moisture-Regime-and-Nitrogen-Content-in-Sal-(-Pokhriyal- Ramola/3a3e4413d0e324fdd5d67d7401542946e06a5c34. • Rana, B.S., Singh, S.P. and Singh, R.P.(1988). Biomass and productivity of central Himalayan sal (Shorea robusta) forest. Trop. Ecol.29,1-7. retrieved from :- https://books.google.com.au/books?id=8byxDwAAQBAJ&pg=PA172&lpg=PA172&dq=Biomass+and+productivity+of+central+Himalayan+sal+(Shorea+r obusta)+forest&source=bl&ots=jpHZJxT- Jk&sig=ACfU3U3cs0zIxqMIpgDIhgH1a7vMFEdJIQ&hl=en&sa=X&ved=2ahUKEwi09df3ntnpAhUazjgGHR5GB_IQ6AEwBnoECAsQAQ#v=onepage&q =Biomass%20and%20productivity%20of%20central%20Himalayan%20sal%20(Shorea%20robusta)%20forest&f=false. • Yadav, V.K., Khare, P.K. And Mishra, G.P. (1986). Effect of tree girth on seed viability and germination in sal. Trop. 2, 160-163. retrieved from :- https://www.researchgate.net/publication/281609791_Seed_Germination_and_Seedling_Survival_Percentage_of_Shorea_robusta_Gaertnf_in_Buffer_Areas_ of_Similipal_Biosphere_Reserve_Odisha_India. • Hao,L., Cao, B., Wang, F, and Yzaki, Y.(1994). Chinese wattle tannin adhesives suitable for producing exterior grade plywood in China. Holz Rob Werks. 52, 113-118. retrieved from :- https://www.semanticscholar.org/paper/Chinese-wattle-tannin-adhesives-for-exterior-grade-Zhao- Cao/626539513e2201be78fd559f17e25cb02156cc90.