This document discusses the impact of carbon sequestration on soil and crop productivity. It provides background on global carbon emissions and pools. Soil acts as both a source and sink of atmospheric carbon through processes like photosynthesis, respiration, and decomposition. Improving soil organic carbon through practices like conservation tillage, cover crops, nutrient management, and agroforestry can increase crop yields by improving soil quality properties. Maintaining or increasing soil organic carbon levels through appropriate land management practices helps mitigate climate change while enhancing soil health and agricultural productivity.
soil organic carbon- a key for sustainable soil quality under scenario of cli...Bornali Borah
The global soil resource is already showing a sign of serious degradation (Banwart et al. 2014) which has ultimately negative impact on sustained crop yield and environmental quality. Due to intense rainfall and concurrent rise in temperature with changing climate, the fertile top soil is prone to severe degradation with depletion of SOC. Most soils in agricultural ecosystems have lost soil C ranging from 30 to 60 t C ha-1 with the magnitude of 50 to 75% loss (Lal, 2004). Hence, restoration of soil quality through different carbon management options will enhance soil health, mitigate climate change and provide sustained agricultural production.
Soil management strategies to enhance carbon sequestration potential of degra...koushalya T.N
Reclamation of degraded lands has huge potential for carbon (C) sequestration to counteract the climate change. It was estimated that about 1,964 Mha of land is degraded worldwide and in India 146.8 Mha of land is degraded ( Bai et al., 2008). The major land-degradation processes in the World and in Asia are water erosion, wind erosion, salinity, alkalinity, nutrient depletion and metal pollution. Enrichment of soil organic carbon (SOC) stocks through sequestration of atmospheric CO2 in agricultural soils and degraded lands is important because of its impacts on improving soil quality and agronomic production, and also for adaptation to mitigation of climate change. Various management strategies like conservation agriculture, integrated nutrient management, afforestation, alternate land use, plantations and amendments and use of biochar hold promise for long-term C sequestration. It can be concluded that land degradation is a serious problem in India which need to be tackled because shrinking of land resource base will lead to a substantial decline in food grain production which in turn would hamper the economic growth rate and there would also be unprecedented increase in mortality rate owing to hunger and malnutrition.
Benefits of Soil Organic Carbon - an overviewExternalEvents
The presentation was given by Mr. Niels H. Batjes, ISRIC, during the GSOC Mapping Global Training hosted by ISRIC - World Soil Information, 6 - 23 June 2017, Wageningen (The Netherlands).
Soil Organic Carbon Sequestration: Importance and State of ScienceExternalEvents
This presentation was presented during the Plenary 1, GSOC17 – Setting the scientific scene for GSOC17 of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Rattan Lal from Carbon Management and Sequestration Center – USA , in FAO Hq, Rome
Impact of soil properties on carbon sequestrationyoginimahadule
Carbon sequestration is an important global phenomenon that plays a significant role in maintaining a balanced global carbon cycle and sustainable crop production. Carbon Sequestration is the placement of CO2 into a depository in such way that it remains safely and not released back to the atmosphere.
Among the soil factors, texture plays an important role in C sequestration. The observation that the decrease in clay- and silt associated C and N upon cultivation of soils was generally less than the decrease in C and N in the particle size fraction > 20 µm confirms that clay and sift particles protect C against microbial degradation (Hassink, 1997).
Increase in SOC concentration with conservation tillage was partly responsible for the increased macroaggregation near the soil surface.( Zhang et al. 2013)
Electrical conductivity in soils affects the organic carbon content by reducing the uptake of minerals and water by the plant which ultimately results in less plant growth. A higher electrical conductivity causes less decomposition in soils which consequently reduces the accumulation of humus meanwhile, the values of acidity; percentage of organic matter, organic carbon and the sequestration of carbon in soils containing T. kotschyiwas more than the values observed in soils containing T. aphylla and the soil of the control which contained no plants.
Nitrogen applicaton at optimum rate help to sequester carbon in soil.(Jiang et al. 2019). Integrated nutrient application in long-term rice-wheat cropping system would be a suitable option with respect to its potentiality of increasing yield, nutrient availability, and sequestering soil organic carbon for sustainable soil health management in partially reclaimed sodic soils of the north Indian subcontinent. He concluded that FYM application increase passive pool of soil while green manure increase active and labile pool. (Choudhury et al. 2018)
Six et al. (2006) by various observation of different sites concludes changes in the relative abundance and activity of bacteria and fungi may significantly affect C cycling and storage, due to the unique physiologies and differential interactions with soil physical properties of these two microbial groups. It has been hypothesized that C turnover is slower in fungal-dominated communities in part because fungi in corporate more soil C into biomass than bacteria and because fungal cell walls are more recalcitrant than bacterial cell walls. Same result by Aliasgharzad et al. 2016).
Tsai et al. (2013) showed positive correlation of soil organic carbon with elevation
This presentation was presented during the Plenary 1, Opening Ceremony of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Luca Montanarella from EU Commission’s Joint Research Centre, in FAO Hq, Rome
soil organic carbon- a key for sustainable soil quality under scenario of cli...Bornali Borah
The global soil resource is already showing a sign of serious degradation (Banwart et al. 2014) which has ultimately negative impact on sustained crop yield and environmental quality. Due to intense rainfall and concurrent rise in temperature with changing climate, the fertile top soil is prone to severe degradation with depletion of SOC. Most soils in agricultural ecosystems have lost soil C ranging from 30 to 60 t C ha-1 with the magnitude of 50 to 75% loss (Lal, 2004). Hence, restoration of soil quality through different carbon management options will enhance soil health, mitigate climate change and provide sustained agricultural production.
Soil management strategies to enhance carbon sequestration potential of degra...koushalya T.N
Reclamation of degraded lands has huge potential for carbon (C) sequestration to counteract the climate change. It was estimated that about 1,964 Mha of land is degraded worldwide and in India 146.8 Mha of land is degraded ( Bai et al., 2008). The major land-degradation processes in the World and in Asia are water erosion, wind erosion, salinity, alkalinity, nutrient depletion and metal pollution. Enrichment of soil organic carbon (SOC) stocks through sequestration of atmospheric CO2 in agricultural soils and degraded lands is important because of its impacts on improving soil quality and agronomic production, and also for adaptation to mitigation of climate change. Various management strategies like conservation agriculture, integrated nutrient management, afforestation, alternate land use, plantations and amendments and use of biochar hold promise for long-term C sequestration. It can be concluded that land degradation is a serious problem in India which need to be tackled because shrinking of land resource base will lead to a substantial decline in food grain production which in turn would hamper the economic growth rate and there would also be unprecedented increase in mortality rate owing to hunger and malnutrition.
Benefits of Soil Organic Carbon - an overviewExternalEvents
The presentation was given by Mr. Niels H. Batjes, ISRIC, during the GSOC Mapping Global Training hosted by ISRIC - World Soil Information, 6 - 23 June 2017, Wageningen (The Netherlands).
Soil Organic Carbon Sequestration: Importance and State of ScienceExternalEvents
This presentation was presented during the Plenary 1, GSOC17 – Setting the scientific scene for GSOC17 of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Rattan Lal from Carbon Management and Sequestration Center – USA , in FAO Hq, Rome
Impact of soil properties on carbon sequestrationyoginimahadule
Carbon sequestration is an important global phenomenon that plays a significant role in maintaining a balanced global carbon cycle and sustainable crop production. Carbon Sequestration is the placement of CO2 into a depository in such way that it remains safely and not released back to the atmosphere.
Among the soil factors, texture plays an important role in C sequestration. The observation that the decrease in clay- and silt associated C and N upon cultivation of soils was generally less than the decrease in C and N in the particle size fraction > 20 µm confirms that clay and sift particles protect C against microbial degradation (Hassink, 1997).
Increase in SOC concentration with conservation tillage was partly responsible for the increased macroaggregation near the soil surface.( Zhang et al. 2013)
Electrical conductivity in soils affects the organic carbon content by reducing the uptake of minerals and water by the plant which ultimately results in less plant growth. A higher electrical conductivity causes less decomposition in soils which consequently reduces the accumulation of humus meanwhile, the values of acidity; percentage of organic matter, organic carbon and the sequestration of carbon in soils containing T. kotschyiwas more than the values observed in soils containing T. aphylla and the soil of the control which contained no plants.
Nitrogen applicaton at optimum rate help to sequester carbon in soil.(Jiang et al. 2019). Integrated nutrient application in long-term rice-wheat cropping system would be a suitable option with respect to its potentiality of increasing yield, nutrient availability, and sequestering soil organic carbon for sustainable soil health management in partially reclaimed sodic soils of the north Indian subcontinent. He concluded that FYM application increase passive pool of soil while green manure increase active and labile pool. (Choudhury et al. 2018)
Six et al. (2006) by various observation of different sites concludes changes in the relative abundance and activity of bacteria and fungi may significantly affect C cycling and storage, due to the unique physiologies and differential interactions with soil physical properties of these two microbial groups. It has been hypothesized that C turnover is slower in fungal-dominated communities in part because fungi in corporate more soil C into biomass than bacteria and because fungal cell walls are more recalcitrant than bacterial cell walls. Same result by Aliasgharzad et al. 2016).
Tsai et al. (2013) showed positive correlation of soil organic carbon with elevation
This presentation was presented during the Plenary 1, Opening Ceremony of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Luca Montanarella from EU Commission’s Joint Research Centre, in FAO Hq, Rome
Conservation Agriculture (CA) is a concept for resource-saving agricultural crop production system that strives to achieve acceptable profits together with high and sustained production levels while conserving the environment.
It is based on minimum tillage, crop residue retention, and crop rotations, has been proposed as an alternative system combining benefits for the farmer with advantages for the society.
Conservation Agriculture remains an important technology that improves soil processes, controls soil erosion and reduces production cost.
Potassium- Forms,Equilibrium in soils and its agricultural significance ,mech...Vaishali Sharma
The slide is conserned with the potassium fertilisers apllied in the soils. When the fertiliser applied in higher amount then it is avail in different form for plant uptake and there exist a equilibrium in soils and it has many agricultural significance and the slide also deal with brief on the mechanism of potassium fixation in the soil.
Soil Carbon & its Sequestration for Better Soil HealthBiswajitPramanick4
Carbon sequestration is the long- term storage of carbon in oceans, soils, vegetation (especially forests), and geologic formations. Although oceans store most of the Earth's carbon, soils contain approximately 75% of the carbon pool on land — three times more than the amount stored in living plants and animals.
Conservation agriculture useful for meeting future food demands and also contributing to sustainable agriculture.
Conservation agriculture helps to minimizing the negative environmental effect and equally important to increased income to help the livelihood of those employed in agril. Production.
Introduction of conservation technologies (CT) was an important break through for sustaining productivity, It seeks to conserve, improve and make more efficient use of natural resources through integrated management of soil, water, crops and other biological resources in combination with selected external inputs.
Challenges of soil organic carbon sequestration in drylandsExternalEvents
This presentation was presented during the 1 Parallel session on Theme 3.3, Managing SOC in: Dryland soils, of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Rachid Mrabet , from INRA – Morocco, in FAO Hq, Rome
Conservation Agriculture (CA) is a concept for resource-saving agricultural crop production system that strives to achieve acceptable profits together with high and sustained production levels while conserving the environment.
It is based on minimum tillage, crop residue retention, and crop rotations, has been proposed as an alternative system combining benefits for the farmer with advantages for the society.
Conservation Agriculture remains an important technology that improves soil processes, controls soil erosion and reduces production cost.
Potassium- Forms,Equilibrium in soils and its agricultural significance ,mech...Vaishali Sharma
The slide is conserned with the potassium fertilisers apllied in the soils. When the fertiliser applied in higher amount then it is avail in different form for plant uptake and there exist a equilibrium in soils and it has many agricultural significance and the slide also deal with brief on the mechanism of potassium fixation in the soil.
Soil Carbon & its Sequestration for Better Soil HealthBiswajitPramanick4
Carbon sequestration is the long- term storage of carbon in oceans, soils, vegetation (especially forests), and geologic formations. Although oceans store most of the Earth's carbon, soils contain approximately 75% of the carbon pool on land — three times more than the amount stored in living plants and animals.
Conservation agriculture useful for meeting future food demands and also contributing to sustainable agriculture.
Conservation agriculture helps to minimizing the negative environmental effect and equally important to increased income to help the livelihood of those employed in agril. Production.
Introduction of conservation technologies (CT) was an important break through for sustaining productivity, It seeks to conserve, improve and make more efficient use of natural resources through integrated management of soil, water, crops and other biological resources in combination with selected external inputs.
Challenges of soil organic carbon sequestration in drylandsExternalEvents
This presentation was presented during the 1 Parallel session on Theme 3.3, Managing SOC in: Dryland soils, of the Global Symposium on Soil Organic Carbon that took place in Rome 21-23 March 2017. The presentation was made by Mr. Rachid Mrabet , from INRA – Morocco, in FAO Hq, Rome
Effect of Global Warming on Soil Organic CarbonAmruta Raut
Currently surface Temperature are rising by about 0.2 °C (0.36 °F) per decade so how it will affect soil organic carbon level and what are the different strategies to sequester carbon explain in detail
Professor Peter Grace says carbon rich soil is "your superannuation", it's not about carbon credits, it's about productivity. He sketches the potential for rangelands to sequester carbon.
NOTE: The presentation and data therein is for information only and can only be reproduced with permission of the author.
Carbon sequestration through the use of biosolids in soils of the Pampas reg...Silvana Torri
Como citar este trabajo
Torri S, Lavado R. 2011. Carbon sequestration through the use of biosolids in soils of the Pampas region, Argentina. In: Environmental Management: Systems, Sustainability and Current Issues.Editor: H. C. Dupont, Nova Science Publishers, Inc., Hauppauge, NY 11788,ISBN: 978-1-61324-733-4.pag. 221-236, 336 p
Soil Nutrient Availability and Enzyme Activities under Wheat-Green gram Crop ...Pravash Chandra Moharana
The aim of this study was to evaluate the effect of rock phosphate (RP) enriched rice straw compost, FYM
and inorganic fertilizers on changes in nutrient availability and enzyme activities in soil during different
physiological growth stages under a wheat-green gram crop rotation in an Inceptisol. The matured RP
enriched compost contained higher bioavailable P as well as total P content compared to farmyard manure.
Data revealed that application of inorganic fertilizers and RP enriched compost or FYM either alone or in
combination resulted in significant build-up in soil organic carbon, mineral N, Olsen-P and NH4OAc-K as
well as enzyme activities compared to unfertilized control plots during different physiological growth stages
of wheat and green gram. Plot receiving 50% NPK+RP enriched compost resulted in 100.8, 95.2 and 100.0
per cent greater build-up in Olsen-P over unfertilized control in crown root initiation (CRI), flowering and
maturity stage of wheat, respectively. Irrespective of treatments, build-up of mineral N, Olsen-P and NH4OAc-
K decreased in all the growth stages of green gram as compared to values obtained in wheat. The
dehydrogenase and phosphatase activities (alkaline and acid) were higher in flowering stage than maturity
and CRI stages of wheat. While, higher enzyme activities were obtained during pod formation in green
gram. The results demonstrated that enriched compost could be prepared using low-grade RP with rice straw
and used as an alternate nutrient source for improving crop yields, maintaining soil nutrient availability and
enzyme activities.
The world is running short of time and option at social and economic front in view of high risks related with global warming and climate change, which is a result of the “enhanced greenhouse effect” mainly due to human induced release of greenhouse gases (GHGs) into the atmosphere (IPCC, 2007). The GHGs inventories are going on all over the world and every possible method to control them are being recognized and evaluated. Carbon footprint is a measure of the exclusive total amount of carbon dioxide emissions that is directly and indirectly caused by an activity or is accumulated over the life stages of a product (Pandey et al., 2011). The crop production contributes significantly to global carbon emissions at different stage of crop through the production and use of farm machinery, crop protection chemicals such as herbicides, insecticides and fungicides, and fertilizer (Hillier et al., 2012). Pathak et al.(2010) calculated the carbon footprint of 24 Indian food items and reported that in the production of these food item 87% emission came from food production followed by preparation (10%), processing (2%) and transportation (1%). Maheswarappa et al. (2011) reported that the C-sustainability index (increase in C output as % of C-based input) of Indian agriculture has decreased with time (from 7 in 1960-61 to 3 in 2008-9). Agricultural uses, including both food production and consumption, contribute the most reactive nitrogen (Nr) to the global environment. Once lost to the environment, the nitrogen moves through the Earth’s atmosphere, forests, grasslands and waters causing a cascade of environmental changes that negatively impact both people and ecosystems. Leach et al. (2012) developed a tool called N-Calculator, a nitrogen footprint model that provides information on how to reduce Nr to the environment. Therefore, Quantification of GHGs from each stage of lifecycle of a product gives complete picture of its impact on global warming and provides necessary information to develop low C technology and mitigation option not only for industrial product but also for agricultural produce. The C and N footprint for a given field will allow growers, advisors and policy makers to make informed decisions about management to optimize crop production, biodiversity and carbon footprint.
Nanoparticles, pharmaceutical and personal care products in sewage sludgePravash Chandra Moharana
During the last decade the occurrence of engineered nanoparticles (NPs), pharmaceuticals and personal care products (PPCPs) in the environment have been well documented. Nanoparticles are released from different nanomaterials used in our household and industrial commodities whereas PPCPs are a diverse group of chemicals comprising all human and veterinary drugs, diagnostic agents and cosmetics such as fragrances and sun-screen agents which enter into environment by excretion of humans and domestic animals, disposal of unused or expired PPCPs to drain and ultimately contaminate the sewage sludge and soil. Toxicity of many nanoparticles in wastewater and sludge and their fate to soil are the unanswered question (Brar et al., 2010). The phytotoxicology of nanoparticles (multi-walled carbon nanotube, aluminum, alumina, zinc and zinc oxide) on seed germination and root growth of radish, rape, ryegrass, lettuce, corn, and cucumber are reported by Lin and Xing, 2007 and Oleszczuk et al., 2011. Application of higher doses of ZnO-NPs inhibited the production of methane, respiration and also nitrification during anaerobic digestion of waste activated sludge (Liu et al., 2011; Mu and Chen, 2011). Some of the nanoparticles like Fe3O4, FeS, CeO2, etc. are used for removal of pollutants from wastewater and sludge. The pharmaceuticals like ibuprofen, naproxen, ketoprofen, diclofenac, phenazone, bezifibrate, erythromycin, sulfamethazine, trimethoprim, triclosan, musk compounds, etc. are identified in wastewater and sludge (Daughton and Ternes, 1999). These PPCPs react with other organic molecules to produce Phase I and Phase II compound which are more toxic than parent compounds. Bioremediation by fungus Trametes versicolor is one of the option to reduce pharmaceuticals to toxicity from sewage sludge (Rodríguez-Rodríguez et al., 2011).
Nutrient recycling through agricultural and industrial wastes:potential and l...Pravash Chandra Moharana
Due to intensive agriculture, the soil resource is under increasing stress as there is a big gap between annual output of nutrients from soil due to crop removals and the nutrient inputs from external resources. So, filling this gap we go for nutrient recycling of non conventional resources i.e. agricultural and industrial wastes. On basis crop production, India generate about 312.5 Mt of crop residues, such as straw of cereals, oilseeds etc can supply about 1.13, 1.41 and 3.54 Mt of NPK. It has been estimated that all animal excreta can potentially supply 17.77 Mt of plant nutrients and 150 Mt of municipal wastes generated annually in India that have nutrient potential of about 1.72 Mt of NPK. At present India produces about 8.0 Mt of poultry manure which is sufficient to fertilizer about 3.56 Mha of land annually. These wastes are composted along with addition low grade rock phosphate and waste mica improve the quality of compost. A huge amount of effluents generated from tanning, textile, distillery and paper mill industries which contain several major primary and secondary plant nutrients (N, P, K, S, Mg, Ca, etc.) as well as micronutrients and heavy metals. Application of pressmud cake, FYM and poultry litter increase soil available nutrients and long term irrigation with paper mill effluent causes soil salinity and heavy metal accumulation. Industrial byproducts like phosphogypsum, basic slag etc used as soil ameliorant.
Seminar of U.V. Spectroscopy by SAMIR PANDASAMIR PANDA
Spectroscopy is a branch of science dealing the study of interaction of electromagnetic radiation with matter.
Ultraviolet-visible spectroscopy refers to absorption spectroscopy or reflect spectroscopy in the UV-VIS spectral region.
Ultraviolet-visible spectroscopy is an analytical method that can measure the amount of light received by the analyte.
Introduction:
RNA interference (RNAi) or Post-Transcriptional Gene Silencing (PTGS) is an important biological process for modulating eukaryotic gene expression.
It is highly conserved process of posttranscriptional gene silencing by which double stranded RNA (dsRNA) causes sequence-specific degradation of mRNA sequences.
dsRNA-induced gene silencing (RNAi) is reported in a wide range of eukaryotes ranging from worms, insects, mammals and plants.
This process mediates resistance to both endogenous parasitic and exogenous pathogenic nucleic acids, and regulates the expression of protein-coding genes.
What are small ncRNAs?
micro RNA (miRNA)
short interfering RNA (siRNA)
Properties of small non-coding RNA:
Involved in silencing mRNA transcripts.
Called “small” because they are usually only about 21-24 nucleotides long.
Synthesized by first cutting up longer precursor sequences (like the 61nt one that Lee discovered).
Silence an mRNA by base pairing with some sequence on the mRNA.
Discovery of siRNA?
The first small RNA:
In 1993 Rosalind Lee (Victor Ambros lab) was studying a non- coding gene in C. elegans, lin-4, that was involved in silencing of another gene, lin-14, at the appropriate time in the
development of the worm C. elegans.
Two small transcripts of lin-4 (22nt and 61nt) were found to be complementary to a sequence in the 3' UTR of lin-14.
Because lin-4 encoded no protein, she deduced that it must be these transcripts that are causing the silencing by RNA-RNA interactions.
Types of RNAi ( non coding RNA)
MiRNA
Length (23-25 nt)
Trans acting
Binds with target MRNA in mismatch
Translation inhibition
Si RNA
Length 21 nt.
Cis acting
Bind with target Mrna in perfect complementary sequence
Piwi-RNA
Length ; 25 to 36 nt.
Expressed in Germ Cells
Regulates trnasposomes activity
MECHANISM OF RNAI:
First the double-stranded RNA teams up with a protein complex named Dicer, which cuts the long RNA into short pieces.
Then another protein complex called RISC (RNA-induced silencing complex) discards one of the two RNA strands.
The RISC-docked, single-stranded RNA then pairs with the homologous mRNA and destroys it.
THE RISC COMPLEX:
RISC is large(>500kD) RNA multi- protein Binding complex which triggers MRNA degradation in response to MRNA
Unwinding of double stranded Si RNA by ATP independent Helicase
Active component of RISC is Ago proteins( ENDONUCLEASE) which cleave target MRNA.
DICER: endonuclease (RNase Family III)
Argonaute: Central Component of the RNA-Induced Silencing Complex (RISC)
One strand of the dsRNA produced by Dicer is retained in the RISC complex in association with Argonaute
ARGONAUTE PROTEIN :
1.PAZ(PIWI/Argonaute/ Zwille)- Recognition of target MRNA
2.PIWI (p-element induced wimpy Testis)- breaks Phosphodiester bond of mRNA.)RNAse H activity.
MiRNA:
The Double-stranded RNAs are naturally produced in eukaryotic cells during development, and they have a key role in regulating gene expression .
Earliest Galaxies in the JADES Origins Field: Luminosity Function and Cosmic ...Sérgio Sacani
We characterize the earliest galaxy population in the JADES Origins Field (JOF), the deepest
imaging field observed with JWST. We make use of the ancillary Hubble optical images (5 filters
spanning 0.4−0.9µm) and novel JWST images with 14 filters spanning 0.8−5µm, including 7 mediumband filters, and reaching total exposure times of up to 46 hours per filter. We combine all our data
at > 2.3µm to construct an ultradeep image, reaching as deep as ≈ 31.4 AB mag in the stack and
30.3-31.0 AB mag (5σ, r = 0.1” circular aperture) in individual filters. We measure photometric
redshifts and use robust selection criteria to identify a sample of eight galaxy candidates at redshifts
z = 11.5 − 15. These objects show compact half-light radii of R1/2 ∼ 50 − 200pc, stellar masses of
M⋆ ∼ 107−108M⊙, and star-formation rates of SFR ∼ 0.1−1 M⊙ yr−1
. Our search finds no candidates
at 15 < z < 20, placing upper limits at these redshifts. We develop a forward modeling approach to
infer the properties of the evolving luminosity function without binning in redshift or luminosity that
marginalizes over the photometric redshift uncertainty of our candidate galaxies and incorporates the
impact of non-detections. We find a z = 12 luminosity function in good agreement with prior results,
and that the luminosity function normalization and UV luminosity density decline by a factor of ∼ 2.5
from z = 12 to z = 14. We discuss the possible implications of our results in the context of theoretical
models for evolution of the dark matter halo mass function.
Cancer cell metabolism: special Reference to Lactate PathwayAADYARAJPANDEY1
Normal Cell Metabolism:
Cellular respiration describes the series of steps that cells use to break down sugar and other chemicals to get the energy we need to function.
Energy is stored in the bonds of glucose and when glucose is broken down, much of that energy is released.
Cell utilize energy in the form of ATP.
The first step of respiration is called glycolysis. In a series of steps, glycolysis breaks glucose into two smaller molecules - a chemical called pyruvate. A small amount of ATP is formed during this process.
Most healthy cells continue the breakdown in a second process, called the Kreb's cycle. The Kreb's cycle allows cells to “burn” the pyruvates made in glycolysis to get more ATP.
The last step in the breakdown of glucose is called oxidative phosphorylation (Ox-Phos).
It takes place in specialized cell structures called mitochondria. This process produces a large amount of ATP. Importantly, cells need oxygen to complete oxidative phosphorylation.
If a cell completes only glycolysis, only 2 molecules of ATP are made per glucose. However, if the cell completes the entire respiration process (glycolysis - Kreb's - oxidative phosphorylation), about 36 molecules of ATP are created, giving it much more energy to use.
IN CANCER CELL:
Unlike healthy cells that "burn" the entire molecule of sugar to capture a large amount of energy as ATP, cancer cells are wasteful.
Cancer cells only partially break down sugar molecules. They overuse the first step of respiration, glycolysis. They frequently do not complete the second step, oxidative phosphorylation.
This results in only 2 molecules of ATP per each glucose molecule instead of the 36 or so ATPs healthy cells gain. As a result, cancer cells need to use a lot more sugar molecules to get enough energy to survive.
Unlike healthy cells that "burn" the entire molecule of sugar to capture a large amount of energy as ATP, cancer cells are wasteful.
Cancer cells only partially break down sugar molecules. They overuse the first step of respiration, glycolysis. They frequently do not complete the second step, oxidative phosphorylation.
This results in only 2 molecules of ATP per each glucose molecule instead of the 36 or so ATPs healthy cells gain. As a result, cancer cells need to use a lot more sugar molecules to get enough energy to survive.
introduction to WARBERG PHENOMENA:
WARBURG EFFECT Usually, cancer cells are highly glycolytic (glucose addiction) and take up more glucose than do normal cells from outside.
Otto Heinrich Warburg (; 8 October 1883 – 1 August 1970) In 1931 was awarded the Nobel Prize in Physiology for his "discovery of the nature and mode of action of the respiratory enzyme.
WARNBURG EFFECT : cancer cells under aerobic (well-oxygenated) conditions to metabolize glucose to lactate (aerobic glycolysis) is known as the Warburg effect. Warburg made the observation that tumor slices consume glucose and secrete lactate at a higher rate than normal tissues.
A brief information about the SCOP protein database used in bioinformatics.
The Structural Classification of Proteins (SCOP) database is a comprehensive and authoritative resource for the structural and evolutionary relationships of proteins. It provides a detailed and curated classification of protein structures, grouping them into families, superfamilies, and folds based on their structural and sequence similarities.
insect taxonomy importance systematics and classification
Impact of carbon sequestration on soil and crop productivity
1. Impact of carbon sequestration
On
soil and crop productivity
Pravash Chandra Moharana
Roll no. 4805
Division of Soil Science & Agricultural Chemistry
Indian Agricultural Research Institute
New Delhi-110 012
6. Atmosphere 748 Gt
Fossil fuels 4000 Gt
Terrestrial 2000 Gt
Soil 1550 Gt
Biota 450 Gt
Oceans 38, 000 Gt
Lal et al., 2004
World Carbon Pool
7. Role of soil in C cycling
Respiratio
n
Photosynthesi
s
SOIL
1550 Pg C
BIOTA
600 Pg C
ATMOSPHERE
750 Pg C
100 Pg/yr
80 Pg/yr
80 Pg/yr
100 Pg/yr
Humus
Soil respiration
and decomposition
Lal and Kimble., 1997
11. Soil erosion and C emission in India
Processes Flux
Total soil erosion 2.98 Pg sediments/yr
(2979 Tg sediments/yr)
Total C loss at 8–12 g/kg 23.8–35.8 Tg C/yr
C emission at 20% of
4.8–7.2 Tg C/yr
displaced C
Lal, 2004
12. Total potential of carbon sequestration in soils of
India
World : 600 – 1200 Tg C/y
Lal, 2004
13. Carbon Sequestration
It refers to the provision of long-term storage of
carbon in the terrestrial biosphere,
underground, or the oceans so that the buildup
of carbon dioxide (the principal greenhouse gas)
concentration in the atmosphere will reduce or
slow down
Lal,1995
14.
15. Soil Carbon Sequestration
A t m o s p h e r i c
C O 2
P l a n t
r e s p i r a t i o n
A n i m a l
r e s p i r a t i o n
S o i l r e s p i r a t i o n
P h o t o s y n t h e s i s
S o i l
o r g a n i s m s
S o i l
o r g a n i c
m a t t e r
C O 2
D i s s o l v e d
C O
2
i n w a t e r
L e a c h a t e
A t m o s p h e r i c
N 2
3
M i n e r a l i z a t i o n
D e n i t r i f i c a t i o n
B i o l o g i c a l
N f i x a t i o n
C a r b o n a t e
m i n e r a l s
F o s s i l f u e l s
N
2
N O
2
N
O
N H
v o l a t i l i z a t i o n
N H
4
f i x a t i o n
P l a n t
u p t a k e
F e r t i l i z e r
Carbon
Input
Carbon
Output
Soil
Carbon
Sequestration
16. Soil acts as a source as well as sink of atmospheric CO2
X
Residue, Roots,
SSooiill CC
Decomposition/
Mineralization
Controls
Abiotic
Substrate Attributes
Nutrient Availability
Soil Disturbance
Decomposer Community
CO2, CH4
DOC
Manure
Compost CO2
17. C cycle in agricultural ecosystem
Climate Soils Management
CO2
Soil MMiiccrroobbiiaall AAccttiivviittyy
SSooiill OOrrggaanniicc MMaatttteerr ((CC))
Sunlight
Harvestable Yield
19. CO2 EMISSIONS vs. CARBON SEQUESTRATION
Current loss of organic carbon to the atmosphere as
CO2 is 3.2 Pg/yr.
if all the degraded agricultural lands of the world (2
billion hectares or 2x 109 ha) having a bulk density of
1.5 Mg/m3 sequester OC @ 0.01%/yr, then the
carbon sequestered will be 3.0 Pg/yr, which is just
close to the SOC emitted to the atmosphere and can
offset the entire green house effect
[ (2x 109 ha) x (104 ha/m2) x (1m) x (1.5 Mg/m3) x (10-
4/yr) = 3.0 Pg/yr]
Lal et al.,1999
Depletion : Cinput < Coutput
Sequestration: Cinput > Coutput
20. Soil Processes Conducive to the
Enhanced Carbon Storage
1.Aggregation: Increase in stable micro-aggregates
through formation of organo-mineral complexes
encapsulates C and protects it against microbial
activities.
2.Humification: To sequester 10,000 kg of C in humus, 833
kg of N, 200 kg of P and 143 kg of S are needed
3.Translocation into the Sub-Soil: Translocation of SOC
into the sub-soil.
4.Formation of Secondary Carbonates:
5.Burial of SOC-Laden Sediments: Transport of SOC-enriched
sediments to depressional sites and/or
aquatic ecosystems
6.Plantation of Deep-Rooted Plants
24. Tillage effects on SOC and MBC after four crop cycles
Jat, 2006
of Rice-Wheat System
25. Intensification of cropping system
Winter crops
Forage in rotation
Growing legume crops
Eliminate fallow
Deep rooted crops
Legumes can fix up to 60-100 kg of N/ha annually, depending on the
species and soil type. For each legume crop grown, approximately 1 ton
of CO2 –C emission is avoided. There is also increased plant residue
input and increased soil organic carbon content.
26. Carbon pools of subhumid, semiarid tropical and arid
ecosystems under different cropping system
Swarup et al., 2000
28. Integrated nutrient management
Soil organic carbon (SOC), changes in SOC and carbon
sequestration rate in 0-45 cm soil in a long-term fertilizer experiment
under maize-wheat-cowpea cropping system
Purakayastha et al., 2008
29. Plant roots and carbon sequestration
Plant root acts as a medium for transfer of atmospheric carbon
into the soil
Root lysis and root exudates contribute significant quantities of
carbon deposited in sub-surface soil
31. Management of Land
Degradation
Tree plantings
Conservation-tillage cropping
Animal manure application
Green-manure cropping systems
Improved grassland management
Cropland-grazingland rotations
Optimal fertilization
32. Organic carbon content in soil
after six years under different
land uses
Land use Organic C (%)
0-15 cm 15-30 cm
Sole cropping 0.42 0.37
Agro forestry 0.71 0.73
Agro-horticulture 0.73 0.74
Agro-silviculture 0.38 0.56
Das et al., 1994
33. Improved Grassland Management
Degradation of permanent grasslands can occur
from accelerated soil erosion, compaction, drought,
and salinization
Strategies to sequester carbon in soil should
improve quality of grasslands
Strategies for restoration should include:
Enhancing soil cover
Improving soil structure to
minimize water runoff and soil
erosion
36. Crop yield and productivity effects of SOC pool
Fertilized
SOC Pool
Crop Yield
Unfertilized
SOC Pool
Δ Yield
37. Soil Quality and SOC Pool
SOC Pool
Soil Quality
productivity
Agronomic NUE
WUE
Microbial biomass
Nutrient Retention
Available water capacity
Aggregation
Infiltration rate
Aeration porosity
38. Role of SOM in Soil and Plant Health
Haynes and Naidu., 1998
39. Role of SOM in Soil and Plant Health
Water retention
Soil temperature and aeration
Chelation
Cation exchange
Mineralization of nutrients
Buffer action
40. Soil aggregate formation
No-Till = Lower
disturbance
Tillage = Higher
disturbance
CO2 CO2
Plant C
Fungi Fungi
Micro-aggregates
SOM SOM
Soil Macroaggregate Soil Macroaggregate
White and Rice, 2007
41. Effect of soil management systems on
soil properties in the top layer of 0-7.5
cm
Properties Conventiona
l
Integrated Organic
OC (g/kg) 5.59 7.16 9.41
Bulk density
1.18 1.12 0.93
(Mg/m3)
Aggregate
stability (%)
10.6 22.8 13.5
Nitrate N
(kg/ha)
12.5 20.3 7.9
Extractable P
(kg/ha)
41.8 52.3 45.7
Earthworms
(number/m2)
35 212 106
Glover et al., 2000
42. Microbial Biomass
Microbial biomass is positively correlated to an estimate of
the organic N available to crops in no-tillage surface soil.
1 to 5% of SOC is in microbial biomass and 2 to 6% of soil
organic N.
Microbial biomass represents a significant amount of
potentially mineralizable N.
Microorganisms produce:
Plant growth hormones
Stimulate plant growth
hormones
Compete with disease
organisms
43. Physical and biological properties influence by OM
Treatmen
ts
(from 1990 to 2007)
Total C
(g/kg)
Bulk density
g/cm
Microbial
biomass
(mg/kg)
OM 9.41 1.20 135.8
1/2OMN 7.16 1.26 98.7
NPK 5.59 1.29 74.4
NP 5.21 1.30 65.5
PK 4.85 1.32 55.8
NK 4.23 1.35 46.8
C 3.92 1.40 41.7
Gong et al., 2008
44. Response of soil organic C in different
particle size fractions
Majumder et al., 2007
45. Soil carbon sequestration and yield
increase of principal crops in India
Crop Area
(Mha)
Current yield
(kg/ha/yr)
Projected
increase
kg/ha/yr/
Mg of SOC
Total
increase in
production
106 Mg/yr
Barley 0.76 1800 20-50 0.02-0.03
Beans 9.0 400 30-50 0.3-0.5
Wheat 27.3 2640 30-50 0.8-1.4
Rice 42.5 2927 30-50 1.3 – 2.1
Maize 14.0 670 100-300 1.4 – 4.2
Sorghum
9.2 700 100-140 0.9 – 1.3
Total 6.9 – 12.5
Lal., 2005
46. Crop yield under different soil organic carbon
(from 1990 to 2007)
Treatments Total C (g/kg) Wheat yield
Kg/ha/yr
Maize yield
Kg/ha/yr
OM 9.41 3436 5994
1/2OMN 7.16 4484 6811
NPK 5.59 4609 6922
NP 5.21 4415 6544
PK 4.85 1078 1481
NK 4.23 594 870
C 3.92 568 766
Gong et al., 2008
47. Comparison of rainfed maize yield
(kg/ha) on different tillage and residue
management practices
Year Zero tillage+residue Zero tillage- residue
1996 4000 2800
1997 6200 2100
1998 5000 3000
1999 1800 1700
2000 6000 4800
2001 6200 1500
2002 6500 2000
Thomas, 2009
48. Yields variation of jute and soybean
with SOC of the treatments
Years
Manna et al., 2005
49. Conclusion
Judicious application of bulky organic manures and balanced
fertilization , reduce tillage and forage and legumes helps in
restoring the organic carbon status of soil
Cultivation of fast growing trees with arable crops under agro-forestry
systems such as agrohorticulture or agro-silviculture
systems helps in improving soil organic carbon content
SOC helps in improving physical, biological, chemical
properties soil and also improving crop productivity in long
term basis.
50. Future steps
Standardised methodologies for estimating
above and below-ground C stocks to improve the
reliability of data
Prediction of models to accommodate future
climate ,land-use changes, crop production and
their implications for CO2 mitigation