Crop residue has important effects on soil quality in rice-based cropping systems. When crop residues are removed, it leads to decreased soil fertility and lower crop production. Incorporating crop residue into the soil improves various indicators of soil quality, including physical properties like aggregation and porosity, chemical properties like soil organic matter and nutrient levels, and biological properties like microbial population and enzyme activity. Proper crop residue management can help sustain soil quality and fertility in rice fields over the long term.
The portion of a plant left in the field after harvest of the crop that is (straw, stalks, stems, leaves, roots) not used domestically or sold commercially”. The non – economical plant parts that are left in the field after harvest and remains that are generated from packing sheds or that are discarded during crop processing. Organic recycling has to play a key role in achieving sustainability in agricultural production. Multipurpose uses of crop residue include, but are not limited to, animal feeding, soil mulching, bio-manure, thatching of rural homes and fuel for domestic and industrial use. Thus, crop residues are of tremendous value to the farmers. Crop residue benefit the soil physically, chemically as well as biologically.
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.
The Contingency plans cover contingency strategies to be taken up by farmers in response to major weather related aberrations such as delay in onset and breaks in monsoon causing early, mid and late season droughts, floods, unusual rains, extreme weather events such as heat wave, cold wave, frost, hailstorm and cyclone.
this slide includes recent approaches to evaluate cropping system.
It includes system profitability,relative production efficiency,land use efficienct(LUE),Calculation of LUE,energy efficiency,specific energy,Rotational intensity,Cropping intensity,Multiple cropping index(MCI),Land equivalent ratio (LER),Relative yields total (RYT),Crop equivalent yields (CEY),Relative Spread Index
The portion of a plant left in the field after harvest of the crop that is (straw, stalks, stems, leaves, roots) not used domestically or sold commercially”. The non – economical plant parts that are left in the field after harvest and remains that are generated from packing sheds or that are discarded during crop processing. Organic recycling has to play a key role in achieving sustainability in agricultural production. Multipurpose uses of crop residue include, but are not limited to, animal feeding, soil mulching, bio-manure, thatching of rural homes and fuel for domestic and industrial use. Thus, crop residues are of tremendous value to the farmers. Crop residue benefit the soil physically, chemically as well as biologically.
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.
The Contingency plans cover contingency strategies to be taken up by farmers in response to major weather related aberrations such as delay in onset and breaks in monsoon causing early, mid and late season droughts, floods, unusual rains, extreme weather events such as heat wave, cold wave, frost, hailstorm and cyclone.
this slide includes recent approaches to evaluate cropping system.
It includes system profitability,relative production efficiency,land use efficienct(LUE),Calculation of LUE,energy efficiency,specific energy,Rotational intensity,Cropping intensity,Multiple cropping index(MCI),Land equivalent ratio (LER),Relative yields total (RYT),Crop equivalent yields (CEY),Relative Spread Index
A brief study on Integrated Nutrient Management (INM). This presentation has created by me after studying many articles and research papers regarding INM. Suggestions are kindly invited.
This presentation is only with respect to the Parasitic Weed and their management tactics, falling under the category of Specificity while classifying weeds.
This presentation was delivered at the National Conference on Botany and Agriculture and is aimed to draw the attention of the audience towards the growing problem of agri. waste management in India.
A brief study on Integrated Nutrient Management (INM). This presentation has created by me after studying many articles and research papers regarding INM. Suggestions are kindly invited.
This presentation is only with respect to the Parasitic Weed and their management tactics, falling under the category of Specificity while classifying weeds.
This presentation was delivered at the National Conference on Botany and Agriculture and is aimed to draw the attention of the audience towards the growing problem of agri. waste management in India.
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restoring the soil physical structure and chemical fertility, improving soil organic C and therefore, sustaining the system productivity. Nitrogen fixers and phosphate solubilizer contribute through biological fixation of nitrogen, solubilization of fixed nutrients and enhanced uptake of plant nutrients (Gupta et al., 2003).
INM tries to reduce the need for chemical fertilizers by taking advantages of non-chemical sources of nutrients such as the manures, composts and bio-fertilizers (Gopalasundaram et al., 2012). Bio-fertilizers application not only increases plants growth and yield, but increase soil microbial population and activity; resulting in improved soil fertility (Ramesh et al., 2014). They include free-living bacteria which promote plant growth even in polluted soils. Azospirillum, Azotobacter, Pseudomonas, Bacillus and Thiobacillus are examples of these bacteria (Zahir et al., 2004). Niess (2002) reported that plant growth promoting bacteria reduced the toxicity of heavy metals and increased plant growth and yield.
Intercropping has been in practice for centuries to sustain yield, minimize risk, utilize the lag phase, and improve productivity (Rao, 2000). It reported that physico-chemical changes in soil under pure and alley cropping with Leucaena leucocephala (after six year) and found that alley cropping more suitable than pure crop (Gangwar et al., 2004).
With the increasing human population, the primary dependence upon the agrarian society to meet the food requirements is at an all-time high. To fulfil these requirements, the dependency of farming community on insecticides and pesticides is no hidden fact. Over the last few decades, the injudicious use of chemical inputs and pesticides has resulted in serious environmental concerns. Moreover, rapid industrialization and other anthropogenic activities such as the unmanaged use of agro-chemicals and dumping of sewage sludge have caused soils and waterways to be severely contaminated with various pollutants like heavy metals, organic pollutants etc. Traditional physical and chemical methods for the clean-up of pollutants are often prohibitively expensive. Perhaps one of the greatest limitations to traditional clean-up methods is the fact that in spite of their high costs, they do not always ensure that contaminants are completely destroyed. As a result, the past two decades have seen a tremendous upsurge in the search for cost-effective and environmentally sound alternatives to traditional methods for dealing with wastes. Of the technologies that have been investigated, bioremediation has emerged as the most desirable approach for cleaning up many environmental pollutants. Bioremediation is an option that offers the possibility to destroy or render harmless various contaminants using natural biological activity.
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It is about the importance of Soil carbon.The ways for enhancing the soil carbon and how these soil carbon changes over period of time under different land use systems.
Global food production now faces greater challenges than ever before due to changing climate, increasing land degradation and decreasing nutrient use efficiency. Nutrient mining is a major cause of low crop yields in parts of the developing world. Especially nitrogen and phosphorus move beyond the bounds of the agricultural field due to inappropriate management practices as well as failure to achieve good congruence between nutrient supply and crop nutrient demand (Pandian et al. 2014). Climate changes raised a serious issue of soil health maintenance for future generations. Rise in temperature and unprecedented changes in precipitation pattern lead to soil degradation by the erosion of top fertile soil, loss of carbon, nitrogen and increasing area under saline, sodic and acid soils. The climate is one of the key elements impacting several cycles connected to soil and plant systems, as well as plant production, soil quality and environmental quality. Due to heightened human activity, the rate of CO2 is rising in the atmosphere. Changing climatic conditions (such as temperature, CO2 and precipitation) influence plant nutrition in a range of ways, comprising mineralization, decomposition, leaching and losing nutrients in the soil. In order to meet the food demand of the growing population, global food production must be increased substantially over the next several decades. Sustainable intensification of agriculture, based on proven technologies, can increase food production on existing land resources. Therefore, conservation and organic agriculture, precision farming, recycling of crop residues, crop diversification in soils and ecosystems, integrated nutrient management and balanced use of agricultural inputs are the proven technologies of sustainable intensification in agriculture. More importantly, among the climate smart agricultural practices, the selection of appropriate measures must be soil or site specific for sustaining resource base for future generations. Further, presentation must be initiated to fine-tune the existing climate-smart agriculture to suit different nutrient management practices.
Dryland agriculture contributes about 60 per cent of the food to the country. The climate change and the rainfall variability affects the crops grown in these lands. The improved agricultural practices will help the farmers to take care of the crops grown and reap higher yields. The sustainability and production factors will be improved with the advanced technologies. The tillage operations, moisture conservation practices, improved varieties, farm machinery, cropping systems will help for the economic stability of the farmers.
The Deyland agriculture has to be improved with innovative research and technologies. The soil and water conservation structures need to established for higher productivity. The bore well recharge has to be done to increase the ground water table. Runoff farming need to be adopted to increase the water availability in off season crop cultivation
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Since volcanic activity was first discovered on Io from Voyager images in 1979, changes
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Inspired by David Donoho's vision, this talk aims to revisit the three crucial pillars of frictionless reproducibility (data sharing, code sharing, and competitive challenges) with the perspective of deep software variability.
Our observation is that multiple layers — hardware, operating systems, third-party libraries, software versions, input data, compile-time options, and parameters — are subject to variability that exacerbates frictions but is also essential for achieving robust, generalizable results and fostering innovation. I will first review the literature, providing evidence of how the complex variability interactions across these layers affect qualitative and quantitative software properties, thereby complicating the reproduction and replication of scientific studies in various fields.
I will then present some software engineering and AI techniques that can support the strategic exploration of variability spaces. These include the use of abstractions and models (e.g., feature models), sampling strategies (e.g., uniform, random), cost-effective measurements (e.g., incremental build of software configurations), and dimensionality reduction methods (e.g., transfer learning, feature selection, software debloating).
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Since the loophole-free Bell experiments of 2020 and the Nobel prizes in physics of 2022, critics of Bell's work have retreated to the fortress of super-determinism. Now, super-determinism is a derogatory word - it just means "determinism". Palmer, Hance and Hossenfelder argue that quantum mechanics and determinism are not incompatible, using a sophisticated mathematical construction based on a subtle thinning of allowed states and measurements in quantum mechanics, such that what is left appears to make Bell's argument fail, without altering the empirical predictions of quantum mechanics. I think however that it is a smoke screen, and the slogan "lost in math" comes to my mind. I will discuss some other recent disproofs of Bell's theorem using the language of causality based on causal graphs. Causal thinking is also central to law and justice. I will mention surprising connections to my work on serial killer nurse cases, in particular the Dutch case of Lucia de Berk and the current UK case of Lucy Letby.
Professional air quality monitoring systems provide immediate, on-site data for analysis, compliance, and decision-making.
Monitor common gases, weather parameters, particulates.
Crop residue management in rice based cropping system
1. Hriday Kamal Tarafder
and
Dr. P. K. Mani
1
Department of Agricultural Chemistry and Soil Science
Faculty Of Agriculture
Bidhan Chandra Krishi Viswavidyalaya
Management of Crop Residue
and Its Effect on Soil Quality in Rice Based
Cropping System
2. Crop residue is defined as the vegetative crop material
left on the field after a crop is harvested, pruned or
processed.
The removal of crop residues leads to low soil fertility
and thereby decreased crop production.
The straw of most cereal crop contains about 35,10 and
80% of the total N, P and K taken up by the crop.
(Barnard and Kristoferson,1985)
3. Crops Asia Africa S. America World
R-straw 771804 25968 24153 844782
R-husk 154361 5194 4831 168956
Wheat 379788 27395 25539 946734
Barley 34097 6753 2141 208229
Sugarcane 53855 8561 41880 125227
Cotton 6378 315 69 6801
Oats 2424 342 1604 51604
Corn 166205 38729 54626 604031
Table1: Residue production (x 103t) by rice and different crops grown in rotation
with rice in the tropics in 1998
Global Availability of Crop Residue
Source: Larson et al., (1978), Bharday (1995), Beri and Sidhu
(1996)
4. Crop Residue
(mt)
Nutrients * (103) tones
N P2O5 K2O N+P2O5+ K2O
Paddy 225.9 1220 542 2417 4179
Wheat 98.9 534 237 1058 1824
Pearl millet 12.0 62 28 124 214
Maize 11.5 59 26 116 201
Sorghum 10.9 65 29 128 222
Barley 2.6 14 6 2747 47
Others 4.1 10 43 75
Table 2: Estimated cereal residues and nutrient present in the cereal residue of
major crop of India
Availability of Crop Residue in India
Beri et al., (1998)
6. Advantage:
It facilitate timely
planting of the following
crops.
It clears the land
quickly of residues
before the next crop.
It kills soil borne
deleterious pests and
pathogens.
Disadvantage:
It cause significantly
air pollution
Kills beneficial soil
insects and micro-
organism
Loss of soil organic
matter (SOM).
7. Used for
livestock feed,
fuel,
building materials,
livestock bedding,
bedding for vegetables cultivation and
mulching for orchards and other crops.
8. It is a practice that leaves straw residues from a previous
crop on the soil surface without any form of incorporation.
It helps to protect the fertile surface soil against wind
and water erosion. This method is prevalent in no-till or
conservation tillage practice where at least 30% of soil
surface is covered with crop residue.
9. Crop residue is incorporated completely or partially
into soil mostly by ploughing.
Aboveground portion chopped into small size and
can be incorporated by power-tiller.
Incorporation of straw increase soil organic matter
and soil N,P and K content as compared to other
management option.
10. Immobilization of mineral nutrients
Phytotoxicity associated with crop
residue incorporation into the soil
11. Figure 1: Effect of pre-decomposition period of rice straw on
mineral N (NH4 + N03) dynamics in soil
(Yadvinder-Singh et al., 2004)Soil amended with 100 mg N kg-1 and incubated at
75% field capacity moisture regime at 30°C
12. Figure 2: Temporal changes in volatile organic acid concentrations in the soil
solution collected at 100 mm soil depth as affected by added rice
straw.
(Sharma et al., 1989)
How to overcome the problem of Phytotoxicity?
14. Soil quality is…
“ the capacity of a specific kind of soil to
function, within natural or managed
ecosystem boundaries, to sustain plant
and animal productivity, maintain or
enhance water and air quality, and
support human health and
habitation.”
(Karlen et al., 1997)
15. Soil Quality Indicators
Physical
Chemical
Biological
Organic Matter
Chemical
PhysicalBiological
OM
22. Crop residues influence soil pH through
accumulation of CO2 and organic acids during
decomposition
A sharp decrease in soil pH of flooded soils due
to application of rice straw has been recorded by
Murty and Sing (1976).
Soil Reaction
23. Straw incorporation hastened and
intensified soil reduction and also increase pH
and E.C of acid soils
(Beye et al.,1978)
Decreased soil pH and E.C of alkaline soils
under submergence
(Yodkeaw and Datta,1989)
24. Yadvinder-Singh et al. (2004) reported that rice residues
incorporation increased organic carbon content of sandy loam
soil more significantly than straw burning or removal after 7
years.
Table 5: Effect of crop residue management on organic carbon content of soil
*Beri et al.,1995,;**Yadvinder-Singh et al.,2004
Type of Crop Residue
and Soil
Duration
(Yr)
Residue
Management
Organic Carbon
(%)
Rice Straw in Wheat
And Wheat Straw In
Rice ;
Sandy Loam*
10
Removed 0.38
Burned 0.43
Incorporated 0.47
Rice Straw in Wheat
Wheat in Rice
In Rice-wheat
Rotation ;
Sandy Loam**
7
Removed 0.38
Burned 0.39
Incorporated 0.50
Soil organic matter(SOM)/ Soil organic carbon(SOC)
25. Within 3 years of incorporation of rice straw at 6-7 t ha-1, total N
content in soil increased by 0.021% over the straw removal
treatment.
Table 6: Effect of straw management on the nutrient status of
Mahaas clay of five cultivars
(Ponnamneruma.1984)
Treatment Organic C
(%)
Total N
(%)
Olsen P
(Mg /Kg)
Exchangeable
K
(Mg/Kg)
Removed 1.81 0.167 9 10.5
Burned 1.94 0.173 11 12.5
Incorpora
ted
2.17 0.182 12 11.6
Soil Macro and Micronutrient
26. Table 7: Effect of crop residues on soil chemical
indicator
SS: Sorghum Stover; GL: Glyricidia Lopping NR: No Residue
(Sharma et al.,2005)
Trea
tme
nt
pH OC N P K Ca Mg S Zn Fe Cu Mn B
SS 6.3 6.2 216 46 208 4.5 1.4 8.8 1.2 10.1 0.8 25.3 0.9
GL 6.2 6.4 251 46 247 4.7 1.4 6.9 1.3 9.6 0.7 27.4 1.3
NR 6.1 4.0 227 38 201 4.6 1.4 6.1 1.2 9.5 0.8 24.6 1.3
28. Table 8: Microbial population as affected by residue
management in Rice-Wheat rotation
Population Burning Removal Incorporation
After rice
Bacteria(*105) 59.6 15.6 115.4
Fungi(*103) 69.0 13.5 143.0
After wheat
Bacteria(*105) 16.2 13.9 126.6
Fungi(*103) 34.5 33.2 133.6
Sidhu et al., (1995)
29. The enzyme activity in the soil environment is
considered important in contributing the overall
soil microbial activity and soil quality. (Jordan et
al.,1995)
Enzymes are involved in the dynamics of soil
nutrient cycling and energy transfer.
Different crop residues incorporation were
significantly higher the enzymes activity than the no
residues. (Bandick and Dick, 1999)
30. Table 9: Changes of soil enzyme activities after I5 years of
cultivation with rice-wheat copping sequence
(Ghosal, 2004)
Treatment Dehydroge
-nage
Acid
Phosphatase
Alkaline
phosphatase
Urease Arylsulph-
atase
Control 22.87 75.69 54.49 9.04 7.76
NPK 20.34 76.08 47.11 10.42 9.52
NPK+PS 24.82 85.01 57.45 12.14 9.96
Fallow 30.40 69.02 56.44 14.43 9.32
31. Microbial biomass is a small (1-5% by weight) but active
fraction of soil organic matter.
Soil microbial biomass acts as a reservoir of plant nutrients
(like N,P and S) and its availability .
After straw incorporation MBC increase by 2-5 fold in 10
days and reached highest by 30 days.
MBC increased by 45 % and N by 60% in residue retention
over residue removal. (Kushwaha et al.,2000)
32. Table 10: Carbon, Nitrogen and biomass C in surface soil
under different residue management
(Monneveux et al.,2006)
Treatment Organic C(%) Total N(%) Biomass
C(µg/g)
No residue 1.92b 0.14b 47.4c
Maize residue 2.01a 0.13a 71.5
Maize and
Jackbean
residue
2.01a 0.16a 114.9
33. Table 11: Microbial biomass C (MBC), mineralizable C (minC), basal
soil respiration (BSR) and microbial quotient (MQ) in soils
Treatments at P ≤ 0.05 by Duncan’s multiple-range test
Majumder et al., 2008
Treatment MBC Min C
(0-24 days)
BSR( 10-24 d) MQ
(g C Kg-1) g CO2-C kg-1C d-
1
Kg minCKg-1
TOC
Control 0.28d 1.15c 0.21c 0.023c
NPK 0.41c 1.65b 0.31b 0.029b
NPK+PS 0.48ab 1.76ab 0.31b 0.032a
At soil depth of 0 to 0.2m under different treatments after 19 yr of rice-wheat cropping
34. 1. Crop residue for reclamation of
salt affected soil
2. Biological N₂ Fixation
3. Weed Control
35. Rice straw incorporation decreased the
precipitation of Ca and carbonate
Increased removal of Na in drainage water
Decreased the pH and EC of soil
36. (Yoo et al.,1990) reported that surface application
of rice straw increased flood water pH to an
optimum level for N2-fixing organism, and thereby
increased the N2-fixtion by heterotrophic bacteria
and blue green algae.
Roper(1983)observed that a positive correlation
between(r=+0.98) between nitrogenase activity and
wheat straw decomposition.
37. Crop residues can suppress weeds
in many ways reported by Kumar and
Goh (2000) for example.
Through there physical presence on
the soil surface as mulch and by
restricting solar radiation reaching
below the mulch layer.
By direct suppression caused by
allelopathy.
By controlling N availability.
Burning of residue can help in effective
removal of weed seed and weeds.
38. Crop residue incorporation improve physical,
chemical and biological properties of soil.
In long-tem incorporation of crop residue
increased the productivity.
Overall, incorporation of crop residues appears to
be a better management option.
Incorporation should be done at least 10 d and
preferably 30 d before the establishment of
succeeding crop.
CONCLUSION