This document summarizes the key points about crop residue management. It begins with definitions of crop residue and discusses the importance of crop residues as a source of organic matter and plant nutrients. It then discusses different types of crop residues including field residues and process residues. The potential uses of crop residues are outlined, including as animal feed, household purposes, composting, biofuels, and improving soil properties. Methods of recycling crop residues like surface mulching, in-situ incorporation, and composting are described. Tables show the effects of different crop residue management practices on soil physical, chemical and biological properties.
Definition and introduction of fertilizer use efficiency , Causes for Low and Declining Crop Response to Fertilizers and FUE.Methods to increase fertilizer use efficiency.
Definition and introduction of fertilizer use efficiency , Causes for Low and Declining Crop Response to Fertilizers and FUE.Methods to increase fertilizer use efficiency.
Diagnosis and Recommendation Integrated System is a new approach to interpreting leaf or plant analysis and a comprehensive system which identifies all the nutritional factors limiting crop production and increases the chances of obtaining high crop yields by improving fertilizer recommendations.
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.
Diagnosis and Recommendation Integrated System is a new approach to interpreting leaf or plant analysis and a comprehensive system which identifies all the nutritional factors limiting crop production and increases the chances of obtaining high crop yields by improving fertilizer recommendations.
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.
Effect of Crop Residue Management in Rice-Wheat Cropping System.pptxPRAVEEN KUMAR
The rice-wheat cropping system is India’s most widely adopted cropping system on an estimated area of around 12 m ha.
In India about 700 m tons of crop residue are being produced per year.
Approximately 250 m tons of residues are produced annually in rice-wheat cropping system in Indo-Gangetic plains.
Crop residue means anything which is leftover the harvested crop after the removal of economic produce from the crop plants.
Crop residue is defined as the vegetative crop material left on the field after a crop is harvested.
It is primary source of C and have significant effect physical, chemical and biological properties of soils.
ISSN 2321 – 9602
It appears that you are providing information about the publication process of IAJAVS International Journal of Advanced Veterinary and Animal Science. it seems to prioritize a fast publication schedule while maintaining rigorous peer review of the journals in research.
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.
To achieve sustainable agricultural production it is imperative to explore alternative integrated soil and nutrient management systems with minimum environmental degradation. Integrated Nutrient Management (INM) aims at maintenance or adjustment of soil fertility and plant nutrient supply to an optimum level for sustaining the desired crop productivity through optimization of benefit from all possible sources of plant nutrients in an integrated manner (Roy and Ange, 1991). Continuous and imbalanced use of fertilizers under intensive agricultural cultivation had adverse impact on the soil. Use of bio and organic fertilizers and adherence to ecofriendly land management practice enhances crop production and sustains soil fertility (Sailaja and Usha, 2002). Keeping these in view, INM practice is seen as a viable option in restoring the soil physical structure and chemical fertility, improving soil organic C and therefore, sustaining the system productivity. Sources such as nitrogen fixers, phosphate solubilizers, mycorrhize and other beneficial organisms contribute to enhance efficient 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.
Apart from this, agroforestry interventions through integration of suitable trees, soil improvement through cover cropping, soil and water conservation measures etc can be potential INM strategies that can be practiced to sustain yield, minimize risk, utilize the lag phase, and improve productivity (Rao, 2000). The success of INM depends on the judicious use of the right combination of INM component suitable for a particular land use system.
Soil Health definition and relationship to soil biology
Characteristics of healthy soil
Assessment of soil health
Framework for evaluating soil health
Indicators
Types of indicators
Biological indicators
Role of biological indicators
Effect of Biofertilizers and their Consortium on Horticultural CropsSourabhMohite
The presentation includes detailed information about the mode of action of different biofertilizers including plant growth-promoting rhizobacteria. By the use of different biofertilizers, we can minimize the quantity of chemical fertilizers and other agrochemicals. use of biofertilizers enhances plant growth with increased yield and quality sustainably. it also includes some case studies which confirm the beneficial use of biofertilizers and PGPR.
Conservation agriculture is based on maximizing yield and to achieve a balance of agricultural, economic and environmental benefits.
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
Effect of mulch on organic tomato cultivationSubhayan Das
EFFECT OF MANURES & MULCHING ON CONSERVATION OF SOIL & WATER ALONG WITH CROP PRODUCTIVITY OF TOMATO IN GANGETIC ALLUVIUM UNDER SHIMUL BASED AGRISILVICULTURE SYSTEM
Judicious use of bio-wastes can re-carbonize the biosphere, restore degraded soils and improve soil health, produce biofuels and other value addition industrial byproducts, and improve the environment. In this context, the importance of recycling bio-wastes (e.g., agricultural, municipal and industrial) to restore soil organic carbon (SOC) concentration and stock and improve soil health cannot be over-emphasized. Crop residues, 510-836 Tg yr-1. are a major source of Carbon, plant nutrients, biofuels and industrial raw materials.There is a strong need of enhancing the awareness about proper disposal and use of bio-wastes through environmental education.
Similar to Crop Residue Management for Soil Health Enhancement (20)
For the determination of Ca+ Mg both together, the versenate titration method is most popularly used in which EDTA (Ethelyne diamine tetra acetic acid) disodium salt solution is used to chelate them.
The two cations can also be precisely estimated in water sample using atomic absorption spectrophotometer (AAS) but for all practical purposes versenate titration method is good enough.
Calcium alone can also be estimated by versenate method using ammonium purpurate (murexide) indicator and thus Mg can be obtained by deduction of Ca from Ca+Mg content.
Calcium estimation can be done on flame photometer also but the precision is not very high. The formation of Ca and Mg complexes is at pH 10 is achieved by using ammonium hydroxide-ammonium chloride buffer.
Presence of high percentage of exchangeable sodium in soils produced alkali conditions- high pH and poor soil structure. Reclamation of such soils involves the use of gypsum in the form of powder. A useful and rough measure of exchangeable Ca (plus Mg) in soils and the amounts of gypsum required to replace the sodium as an initial step in soil reclamation consists of adding a given amount of saturated solution of gypsum to a weighed amount of soil and by versenate titration, determining the combined Ca and Mg left in solution at equilibrium. The amount of Ca adsorbed by the soil (initial Ca in solution – Ca +Mg in solution after equilibration with soil) is a measure of the gypsum requirement of the soil.
Carbonate and bicarbonate ions in the sample can be determined by titrating it with against standard sulphuric acid (H2SO4) using phenolphthalein and methyl orange as indicators.
Potassium in solution is atomized to flame and the flame excites atom of potassium causing them to emit radiation at specific wavelength. The amount of radiation emitted is directly proportional to concentration of the solution and it is measured in a flame photometer with suitable filter, which transmits only potassium wavelength (768 nm red filter).
Organic carbon in organic matter is oxidized by known but excess of chromic acid. The excess chromic acid not reduced by organic matter is determined by back titration with standard ferrous sulphate solution, using diphenylamine or ferroin indicator. The organic carbon content in soil is calculated from the chromic acid utilized (reduced) by it.
Determination of soil available nitrogen by Alkaline
permanganate method (Subbiah and Asija, 1956).
Nitrogen is necessary for all forms of life. It is most important
essential plant nutrient for crop production as it is constituted the building blocks of almost all the plant structures.
This ppt is about the distribution of wasteland and problem soils. Those lands are wastelands which are ecologically unstable,
whose topsoil has nearly been completely lost, and
which have developed toxicity in the root zones or growth of most plants, both annual crops and trees”.
Sulfur is a chemical element with symbol S and atomic number 16 with atomic mass 32.065.
It is abundant, multivalent, brittle, yellow, tasteless, odourless and non-metallic element.
Sulfur is the tenth most common element by mass in the universe, and the fifth most common on Earth.
In the Bible, sulfur is called brimstone .
Today, almost all elemental sulfur is produced as a by product of removing sulfur-containing contaminants from natural gas and petroleum.
Most soil sources of S are in the organic matter and therefore concentrated in the top soil or low layer.
Under normal conditions, sulfur atom forms cyclic octatomic molecules with a chemical formula S8.
Sulphur is the most abundent and widely distributed element in the nature and found both in free as well as combined states.
Integrated Nutrient Management refers to the maintenance of soil fertility and of plant nutrient supply at an optimum level for sustaining the desired productivity through optimization of the benefits from all possible sources of organic, inorganic and biological components in an integrated manner
Integrated nutrient management (INM) involves efficient and judicious use of all the major components of plant nutrient sources for sustaining soil fertility, health and productivity
Integrated approach for plant nutrition is being advocated because single nutrient approach often reduces fertilizer use efficiency and consequently creates problem fertilizers can help in enhancing and maintaining stability in production with least degradation in chemical and physical properties of the soil.
A healthy soil is a living, dynamic ecosystem that performs many vital functions.
A healthy soil produces a healthy feed for consumption. Improved soil health often is indicated by improvement on physical, chemical and microbiological environment.
Introduction of high yielding varieties, irrigation and use of high analysis fertilizer without proper soil tests, accelerated the mining of native soil nutrient resources.
Under intensive cultivation without giving due consideration to nutrient requirement has resulted in decline in soil fertility and consequent productivity of crops
Vegetables are rich source of energy and nutrition.
The development of Plant Nutrient Management to increase the quantity of plant nutrients in farming systems and thus crop productivity is a major challenge for food security and rural development.The depletion of nutrient stocks in the soil is a major but often hidden form of land degradation. On the other hand, excessive application of nutrients or inefficient management means an economic loss to the farmer and can cause environmental problems, especially if large quantities of nutrients are lost from the soil-plant system into water or air.
Increasing agricultural production by improving plant nutrition management, together with a better use of other production factors is thus a complex challenge. Nutrient management implies managing all nutrient sources - fertilisers, organic manures, waste materials suitable for recycling nutrients, soil reserves, biological nitrogen fixation (BNF) and bio-fertilizers in such a way that yield is not knowingly increased while every effort is made to minimise losses of nutrients to environment
Plant need water, air, light, suitable temperature and 17 essential nutrients for growth and development in the right combination. When plant suffers from malnutrition, exhibits symptoms of being unhealthy reliable nutrient recommendations are dependent upon accurate soil tests and crop nutrient calibrations based on extensive field research. An important part of crop production is being able to identify and prevent plant nutrient deficiencies. Optimization of pistachio productivity and quality requires an understanding of the nutrient requirements of the tree, the factors that influence nutrient availability and the methods used to diagnose and correct deficiencies. Several methods for nutritional diagnosis using leaf tissue analysis have been proposed and used, including the critical value (CV), the sufficiency range approach (SRA), and the diagnosis and recommendation integrated system (DRIS). de both soil and tissues analysis. Renewed and intensified efforts are in progress to identify nutrient constraints using latest diagnostic tools and managing them more precisely through intervention of geospatial technologies (GPS, GIS etc.). There have been consistent concerns about the relegated fertilizer use efficiency, warranting further the revision of ongoing practices, and adoption of some alternative strategies. Diagnosis of nutrient constraints and their effective management has, therefore, now shifted in favour of INM.
Indian agriculture feels the pain of fatigue of green revolution.
In the past 50 years, the fertilizer consumption exponentially increased from 0.5 (1960’s) to 24 million tonnes (2013) that commensurate with four-fold increase in food grain output (254 million tonnes) In order to achieve a target of 300 million tonnes of food grains and to feed the burgeoning population of 1.4 billion in 2025, the country will require 45 million tonnes of nutrients as against a current consumption level of 23 million tonnes. The sustainable agriculture and precision farming both are the urgent issues and hence the suitable agro-technological interventions are essential (e.g., nano and biotechnology) for ensuring the safety and sustainability of relevant production system.
Indian agriculture is passing through difficult times due to erractic weather conditions, especially drought and excessive rainfall, there by resulting into wide spread distress among farmers.
The average income of an agricultural household during July 2012 to June 2013 was as low as Rs.6,426.
As many as 22.50% of the farmers live below poverty line, the country also witnessed a sharp increase in the number of farmers suicides due to losses from farming and low farm income.
Farming in India is becoming hard and unsuccessful due to several causes like unexpected rainfalls,droughts, increased cost of cultivation due to pests and diseases, decrease in productivity of land, unavailability of water etc..
Farmers get very low income for their produce due to prevailing market prices that are very unstable.
Decline in Agriculture productivity and Income has a serious effect on rural house holds, and other economic, social as well as sustainability indicators.
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Biological screening of herbal drugs: Introduction and Need for
Phyto-Pharmacological Screening, New Strategies for evaluating
Natural Products, In vitro evaluation techniques for Antioxidants, Antimicrobial and Anticancer drugs. In vivo evaluation techniques
for Anti-inflammatory, Antiulcer, Anticancer, Wound healing, Antidiabetic, Hepatoprotective, Cardio protective, Diuretics and
Antifertility, Toxicity studies as per OECD guidelines
2. Presented by
Mr. Chavhan Govind Daulatrao
Reg. No. :-2018A/104M
Research Guide
Dr. P. K. Rathod
Asst. Prof. Dept. of SSAC,
COA, Golegaon
Seminar incharge
Dr. Syed Ismail
Head, Dept. of SSAC,
COA, Parbhani
SUBMITTED TO
HEAD
DEPARTMENT OF SOIL SCIENCE AND AGRIL. CHEMISTRY
COLLEGE OF AGRICULTURE,
V.N.M.K.V., PARBHANI
2019-2020
3. Crop residue:-
“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.
Introduction
4. A tremendous natural resource and not a waste.
Crop residues are excellent source of organic matter and plant
nutrients.
Incorporation of crop residues alters the soil environment, which
in turn influences the microbial population and activity in the soil
and subsequent nutrient transformations.
Increasing prices of chemical fertilizers and declining soil health
has attention on the need of recycling of organic residues in crop
production.
5. 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.
6. Crop Residue Management
Crop residue management:
Use of the non-commercial portion of the plant or crop for
protection or improvement of the soil.
CRM, a cultural practice that involves fewer and/or less intensive
tillage operations and preserves more residue from the previous crop, is
designed to help protect soil and water resources and provide additional
plant nutrients and environmental benefits.
7. Need of Crop Residue Management :
Effective nutrient management involving available organic source
including wastes and crop residue.
The deficit of nutrients to meet crop demand has to come from
source other than chemical fertilizers.
Demand for fertilizer will increase by 10 to 15 mt in near future.
So in order to meet these demands effectively on alternative way like
CRM in need to be addressed sincerely.
8. What is residue good for :
-As a soil amendment.
Soil Structure
Erosion control
Soil temperature
Microbial activity
Nutrient cycling
Reducing evaporation
Water holding capacity
9. Types of crop residues:
There are different types of agricultural crop residues.
1. Field/harvest residues:
The materials left in the field after the crop has been
harvested.
Example: Straw, Stubble, Stover, Haulms, Leaves.
These are ploughed directly into the soil.
Good management of field residues improves soil physical,
chemical and biological properties.
10. 2. Process residues:
The materials left after the crop is processed in to a usable
resource.
Example: Groundnut shells, husk, bagasse, molasses, oil
cakes, cobs of Maize, Sorghum, Bajra.
These can be used as animal fodder and soil amendment,
fertilizers and in manufacturing.
11. Types of Agricultural Crop Residues
Process Residues
Groundnut shell
Oil cakes
Cobs of Maize,
Sorghum & Bajara
Field / Harvest Residue
eg. Straws, Stubble,
Stover, Haulms, Leaves.
12. Potential uses of crop residues
1) Crop residues as feed for live-stock
2) Crop residues as household purpose
3) Crop residues as compost:
4) Crop residues for mushroom cultivation
5) Crop residues as bio-fuel
6) Crop residues as biochar production
7) Crop residues as surface mulch
8) Crop residues as source of plant nutrients
13. Crop Residue Utilization in Agriculture
In situ incorporation Crop Residue as surface mulch Composting from crop residues
Soil Cover Crops Green manuring As animal feed
14. Methods of Crop Residues
Recycling :
As a surface mulch.
In situ incorporation of residues
in soil.
Composting from cop
residues.
Composting
Surface
mulch
In-situ
incorporation
Recycling
15. Crop Residues as a Surface Mulch :
Mulch influences reflectivity of heat and water transmission
characteristics of mulched soil.
Mulch also improves the soil water storage capacity and
reduces evaporation losses.
Beneficial effect of crop residue mulch on soil is moisture
conservation and moderate soil temperature.
Crop residue is an effective mean of runoff, erosion and
transport of sediment to stream.
16. In situ incorporation of crop
residues in soil:
Crop residues are incorporated in soil before
sowing of succeeding crop.
Period available for decomposition of crop
residues is important so as to insure
availability of nutrients.
Crop residues having wide C:N ratio
decomposes slowly in the soil.
Decomposition is highly influenced by soil
properties, temperature and moisture regime.
Residues available for
in situ recycling
17. In situations, disallowing adequate decomposition period for the soil
incorporated residues; the residues should be managed through
composting during the crop season
Composting is a process that works to speed up the natural decay
of organic material by providing the ideal conditions for detritus-
eating organisms to thrive, according to the United States
Department of Agriculture (USDA).
Composting from cop residues:
18. Soil structure
Bulk Density & porosity
Hydraulic conductivity
Soil temperature
Soil moisture
Effect of crop residue management on physical
properties of soil
19. Organic carbon
Soil pH
Cation Exchange Capacity
Available N, P and K
Available Micronutrient.
Effect of crop residue management on chemical properties of
soil
20. It provides energy for growth & activities of microbes & substrates
for microbial Biomass.
Provide suitable environment for Biological N – fixation.
Enzymes (dehydrogenase and alkaline phosphatase) activities
increase in soil.
Increase in microbial population.
Humus formation.
Effect of crop residue management on biological properties
of soil
21. Table No.1: Effect of rice residue management on physico-chemical
properties of soil at harvest.
(Source: Chandra et al. (2018) Thesis Submitted to the Indira Gandhi Krishi Vishwavidyalaya, Raipur, Chhattisgarh).
Treatment
Bulk density
(Mg m-3)
pH
EC
(dS m-1)
OC (%)
T1: Rice Stubble + Zero tillage
1.37 7.24 0.23 0.30
T2: Rice Stubble Burn (@ 5 t ha-1) +
Conventional tillage
1.30 7.62 0.27 0.40
T3: Rice Stubble + Rice Biochar
(@ 2 t ha-1) + Conventional tillage
1.34 7.28 0.25 0.56
T4:Rice Stubble + Trichoderma
(@ 10 kg ha-1) + Conventional
tillage
1.36 7.36 0.30 0.48
T5: Rice Stubble + 5% Urea Spray +
Conventional tillage
1.33 7.19 0.25 0.44
T6: Rice Stubble + Trichoderma
(@ 10 kg ha-1) + FYM (@ 2 t ha-1) +
Conventional tillage
1.34 7.00 0.32 0.55
SE m ± 0.01 NS NS 0.03
CD at 5 % 0.04 NS NS 0.09
22. Table No: 2 Soil physical properties as influenced by tillage and residue
management practices in soybean-wheat cropping system
(at the end of two cropping cycles).
(Source: Monsefi et al. (2014) International Journal of Plant Production 8 (3). Location: Delhi.)
Treatment Bulk density (Mg m-3) Hydraulic conductivity (cm h-1)
Infiltration
rate (cm h-1)
Soyabean Wheat 0 -15 cm 16 -30 cm 0 -15 cm 16-30 cm
CT CT 1.69 1.70 1.061 0.934 1.124
CT ZT 1.67 1.71 1.019 0.841 1.021
ZT ZT 1.68 1.70 1.024 0.896 0.782
CT+WS ZT 1.67 1.69 1.051 0.921 0.986
CT ZT+SR 1.66 1.71 1.001 0.882 1.039
CT+WS ZT+SR 1.69 1.73 1.966 0.854 1.102
ZT+WS CT 1.68 1.71 1.016 0.845 1.214
ZT CT+SR 1.66 1.67 1.008 0.911 1.189
ZT+WS CT+SR 1.66 1.69 0.969 0.872 1.014
ZT+WS ZT 1.67 1.68 0.976 0.901 0.659
ZT ZT+SR 1.68 1.70 1.008 0.872 0.598
ZT+WS ZT+SR 1.68 1.71 1.026 0.869 1.064
Initial 1.64 1.012 1.024
23. Table No: 3 Effect of incorporation of crop residue on physico-chemical
properties of soil green gram - sunflower sequence.
T1 Control, T2 RDF green gram , T3 incorporation of cotton stalk @ 41 ha-1 + 50% N of RDF, T4 incorporation of cotton stalk @ 41kg ha-1 + 100
% N of RDF, T5 incorporation of cotton stalk @ 41 ha-1 + 125 % N + 100 % P through RDF, T6 - incorporation of sunflower straw @ 41 ha-1 +
50% N of RDF, T7 incorporation of sunflower straw @ 4 t ha-1 + 100 % N of RDF, T8 incorporation of sunflower straw @ 4 t ha-1 + 125 % N +
100% P of RDF, T9 incorporation of farm waste (including grasses) @ 4 t ha-1 + 50 % N of RDF, T10 incorporation of farm waste (including
grasses) @4 t ha-1 + 100% N of RDF, T11 incorporation of farm waste (including grasses) @ 4 t ha-1 + 125 % N + 100% P of RDF
(Source: Krishnaprabhu et. al. (2017) Journal of Pharmacognosy and Phytochemistry. 8(3): 324-327.
Treatment
Bulk density
(Mg m-3)
pH EC (dS m-1) Org. C (g kg-1)
T1 1.28 8.01 0.29 4.0
T2 1.27 8.07 0.29 4.4
T3 1.26 8.04 0.28 4.2
T4 1.25 7.99 0.29 4.4
T5 1.25 7.97 0.25 4.4
T6 1.27 7.97 0.28 4.5
T7 1.24 7.99 0.27 4.6
T8 1.24 7.95 0.26 4.8
T9 1.25 7.97 0.27 4.2
T10 1.27 7.99 0.28 4.1
T11 1.26 8.05 0.28 4.2
SE (m) ± 0.015 0.01 0.06 0.06
CD at 5 % - - - -
24. Table No: 4 Cumulative effect of crop residue in combination with
organics, inorganics and cellulolytic organisms on soil physical
properties.
(Source: Bellakki et. al. (2007). Journal Of Indian society of soil science. 48(2):393-395. Location: Bijapur, Karnataka)
Treatment
BD
(Mg m-3)
IR (cm h-1)
Water stable
aggregates of >0.25mm
Moisture retention (%) at
0.33 bar 15 bar
T1 Sorghum stubbles @ 5 t ha-1 1.23 0.93 51.25 31.42 14.24
T2 stubbles + subabul loppings (50:50)
@ 5 t ha-1
1.27 0.92 51.46 31.85 14.88
T3 stubbles + subabul loppings (25:75)
@ 5 t ha-1
1.30 0.78 50.63 31.29 14.67
T4 Sorghum stubbles @ 5 t ha-1 +
10 kg N ha-1
1.28 0.83 49.62 30.82 14.13
T5 Sorghum stubbles @ 5 t ha-1 +
20 kg N ha-1
1.31 0.90 50.77 30.68 15.10
T6 Sorghum stubbles @ 5 t ha-1+
30 kg N ha-1
1.32 0.83 49.50 30.94 14.80
T7 Sorghum stubbles @ 5 t ha-1+
cellulolytic organism-A
1.20 0.76 51.42 31.13 14.30
T8 Sorghum stubbles @ 5 t ha-1+
cellulolytic organism-B 1.21 0.93 50.25 30.40 13.85
T9 RDF 1.35 0.53 47.18 29.62 14.00
T10 Control 1.31 0.45 46.77 28.35 13.84
CD at 5 % 0.23 0.28 3.17 1.61 0.60
25. Table No: 5 Effect of crop residue management in Rice-Wheat system on
soil physico-chemical properties
(Source: Sharma et. al. (2018). Current Journal of Applied Science and Technology. Location: Bhagalpur, Bihar.)
Indicators
Crop Residue Management practices
Removed Burned Incorporated
Incorporated +
Green manuring
CD
(P=0.05)
Bulk density (M gm-3) 1.57 1.59 1.48 1.46 0.02
Infiltration rate (cm h-1) 0.32 0.32 0.38 0.41 0.01
Aggregate stability (%) 9 10 14 14 0.04
pH 6.7 6.7 6.8 6.8 NS
EC (dS m-1) 0.20 0.21 0.27 0.28 0.01
OC (%) 0.40 0.38 0.58 0.62 0.14
Avail. N (kg ha-1) 175 178 205 230 2.82
Avail. P (kg ha-1) 20 18 32 34 0.46
Avail. K (kg ha-1) 190 188 264 265 0.84
26. Table No: 6 Effect of crop residue management in Rice-Wheat rotation
on physico-chemical properties of soil .
(Source: Thorat et al. (2015) JNKVV Res J. 49(2):125-136. Location: Jabalpur, M.P.)
Parameter Initial status Retained Incorporation Removed Burnt
pH 7.83 7.65 7.35 7.40 7.65
Water stable aggregate 51.9 57.4 56.9 46.3 38.2
OC (%) 0.46 0.53 0.58 0.43 0.47
Avail. N (kg ha-1) 64.6 89.0 83.0 32.0 21.0
Avail. P (kg ha-1) 25.8 39.0 42.0 21.0 29.0
Avail. K (kg ha-1) 52.1 67.0 69.0 48.0 55.0
27. Table No: 7 Nutrients content in grain and straw of wheat as affected by
different residue management practices and nitrogen levels
(pooled results of two year).
(Source: Shah et al. (2006) An international j. of life sci.10:385-389. Location: Nawsari, Gujarat)
Treatments
N (%) P (%) K (%)
Grain Straw Grain Straw Grain Straw
R0 Control 1.74 0.46 0.36 0.18 0.35 0.69
R1 WSI @ 5 t/ha at 30 DBS 1.89 0.49 0.37 0.18 0.36 0.73
R2 WSI @ 5 t/ha + 20 kg N/ha
at 30 DBS
1.93 0.50 0.38 0.19 0.37 0.74
R3 WSI @ 5 t/ha + 20 kg
P2O5 kg/ha at 30 DBS
1.88 0.51 0.38 0.19 0.38 0.74
R4 WSI @ 5 t/ha + 20 kg N and
20 kg P2O5 /ha at 30 DBS
1.93 0.53 0.39 0.20 0.40 0.75
R5 FYM 10 t/ha 1.83 0.49 0.37 0.19 0.37 0.72
CD at 5 % 0.085 0.031 0.016 0.08 0.022 0.032
28. Table No: 8 Effect of rice residue management on microbial Biomass
Carbon (μg g⁻1 soil) of soil at different days after sowing.
Treatments
Microbial biomass carbon (μg g-1 soil)
30 DAS 60 DAS 90 DAS At harvest
T1: Rice Stubble + Zero tillage 138.10 157.10 193.84 128.10
T2: Rice Stubble Burn (@ 5 t ha-1) +
Conventional tillage
126.36 145.36 194.21 113.03
T3: Rice Stubble + Rice Biochar
(@ 2 t ha-1) + Conventional tillage
155.68 174.68 204.40 145.68
T4:Rice Stubble + Trichoderma
(@ 10 kg ha-1) + Conventional tillage
162.61 181.61 225.50 152.61
T5: Rice Stubble + 5% Urea Spray +
Conventional tillage
151.71 170.71 195.40 141.71
T6: Rice Stubble + Trichoderma
(@ 10 kg ha-1) + FYM (@ 2 t ha-1) +
Conventional tillage
171.96 189.96 214.58 158.63
SE (m) ± 8.13 8.57 9.59 8.48
CD at 5 % 25.61 27.01 30.22 26.72
(Source: Chandra et al. (2018) Thesis Submitted to the Indira Gandhi Krishi Vishwavidyalaya, Raipur, Chhattisgarh).
29. Table No: 9 Effect of rice residue management on CO2 evolution
(mg CO2 per 100 gram) at different days after sowing.
Treatments
CO2 evolution (mg CO2 100 g-1)
30 DAS 60 DAS 90 DAS At harvest
T1 : Rice Stubble + Zero tillage 28.57 30.47 32.17 19.37
T2 : Rice Stubble Burn (@ 5 t ha-1) +
Conventional tillage
31.80 34.40 35.57 27.87
T3 : Rice Stubble + Rice Biochar
(@ 2 t ha-1) + Conventional tillage
34.40 38.20 40.50 30.60
T4 : Rice Stubble + Trichoderma (@ 10
kg ha-1) + Conventional Tillage
37.17 43.10 46.47 33.00
T5 : Rice Stubble + 5% Urea Spray +
Conventional tillage
31.67 33.63 34.30 25.97
T6 : Rice Stubble + Trichoderma
(@ 10 kg ha-1) + FYM (@ 2 t ha-1) +
Conventional tillage
36.50 40.70 43.47 31.93
SE (m) ± 0.88 0.83 0.92 1.26
CD at 5 % 2.76 2.60 2.89 3.96
(Source: Chandra et al. (2018) Thesis Submitted to the Indira Gandhi Krishi Vishwavidyalaya, Raipur, Chhattisgarh).
30. Table No: 10 Effect of different treatments on physical properties of soil
at harvest of safflower
Treatment
Bulk
Density
(M gm-3)
Hydraulic
conductivity
(cm hr-1)
Infiltration
rate
(cm hr-1)
Max. water
holding
capacity (%)
Water stable
aggregate of >
0.25 mm (%)
T1 100% RDF NPK without incorporation of crop residue 1.51 0.15 1.23 51.35 46.23
T2 Incorporation of crop residue @2 t ha-1 1.50 0.20 1.41 52.48 47.81
T3
PSB 10 kg ha-1 + crop residue @ 2 t ha-1 + Alkali water
irrigation passed through gypsum bed (30 cm
thickness) for safflower only
1.40 0.24 1.66 53.70 49.25
T4
50% RDF NPK with incorporation of crop residue
@ 2 t ha-1
1.43 0.28 1.69 55.69 47.10
T5 50% RDF NPK + PSB 10 kg ha-1 1.45 0.18 1.36 51.98 49.85
T6 50% RDF NPK + PSB 10 kg ha-1 + crop residue
@ 2 t ha-1
1.42 0.30 1.72 57.15 51.26
T7
50% RDF NPK + PSB 10 kg ha-1 + crop residue @ 2 t
ha-1 + Alkali water irrigation passed through gypsum
bed (30 cm thickness) for safflower only
1.39 0.33 1.78 58.44 52.75
Initial value 1.51 0.14 1.25 50.90 47.00
SE 0.034 0.017 0.028 0.64 0.56
CD at 5% 0.098 0.048 0.080 1.81 1.57
Source: Bhowate et. al.(2005) International Journal of Current Microbialogy & App.Sci. 6(9):3717-3730. Location: Ramzanpur, M.H.
31. Table No: 11 Effect of different treatments on NPK uptake by green gram
kg ha-1
Treatments
N uptake (Kg ha-1) P uptake (Kg ha-1) K uptake (Kg ha-1)
Grain Straw Grain Straw Grain Straw
T1
100% RDF NPK without incorporation of
crop residue
24.49 31.52 4.42 4.34 10.75 33.46
T2 Incorporation of crop residue @2 t ha-1 11.21 16.65 1.65 1.62 4.31 16.81
T3
PSB 10 kg ha-1 + crop residue @ 2 t ha-1 +
Alkali water irrigation passed through
gypsum bed (30 cm thickness) for
safflower only
14.96 22.40 2.47 2.45 6.10 23.91
T4
50% RDF NPK with incorporation of crop
residue @ 2 t ha-1
18.55 24.04 2.99 2.77 7.75 25.24
T5 50% RDF NPK + PSB 10 kg ha-1 16.21 13.89 2.75 3.11 6.32 24.15
T6 50% RDF NPK + PSB 10 kg ha-1 + crop
residue @ 2 t ha-1
20.04 27.57 3.44 3.49 8.49 29.19
T7
50% RDF NPK + PSB 10 kg ha-1 + crop
residue @ 2 t ha-1 + Alkali water irrigation
passed through gypsum bed (30 cm
thickness) for safflower only
23.71 28.73 4.15 3.81 10.43 30.53
SE (m)± 0.54 0.78 0.14 0.20 0.22 0.80
C.D. at 5 % 1.53 2.33 0.40 0.64 0.69 2.26
Source: Bhowate et. al.(2005) International Journal of Current Microbialogy & App.Sci. 6(9):3717-3730. Location: Ramzanpur, M.H.
32. Table No: 12 NPK content (%) in Safflower as influenced by different
treatments.
Source: Bhowate et. al.(2005) International Journal of Current Microbialogy & App.Sci. 6(9):3717-3730. Location: Ramzanpur, M.H.
Treatments
N (%) P (%) K (%)
Grain Straw Grain Straw Grain Straw
T1 100% RDF NPK without incorporation of crop residue 2.39 1.37 0.68 0.23 0.89 1.72
T2 Incorporation of crop residue @2 t ha-1 2.05 1.21 0.50 0.13 0.75 1.51
T3
PSB 10 kg ha-1 + crop residue @ 2 t ha-1 + Alkali water
irrigation passed through gypsum bed
(30 cm thickness) for safflower
2.20 1.25 0.55 0.16 0.80 1.60
T4
only 50% RDF NPK with incorporation of crop residue
@ 2 t ha-1
2.18 1.27 0.57 0.18 0.83 1.62
T5 50% RDF NPK + PSB 10 kg ha-1 2.24 1.26 0.53 0.20 0.83 1.65
T6 50% RDF NPK + PSB 10 kg ha-1 + crop residue
@ 2 t ha-1
2.31 1.33 0.60 0.19 0.86 1.68
T7 50% RDF NPK + PSB 10 kg ha-1 + crop residue @ 2 t
ha-1 + Alkali water irrigation passed through gypsum
bed (30 cm thickness) for safflower only
2.37 1.35 0.64 0.21 0.87 1.70
SE (m) ± 0.01. 0.014 0.011 0.014 0.014 0.016
C.D. at 5 % 0.030 0.041 0.031 0.040 0.041 0.045
33. Table No: 13 Effect of different treatments on grain and straw yield of
green gram and safflower
Source: Bhowate et. al.(2005) International Journal of Current Microbialogy & App.Sci. 6(9):3717-3730. Location: Ramzanpur, M.H.
Treatment
Green gram (q ha-1) Safflower (q ha1)
Grain Straw Seed Straw
T1
100% RDF NPK without incorporation of
crop residue
9.04 11.72 16.14 14.94
T2 Incorporation of crop residue @2 t ha-1 4.45 4.27 9.56 8.76
T3 PSB 10 kg ha-1 + crop residue @ 2 t ha-1 +
Alkali water irrigation passed through
gypsum bed (30 cm thickness)
5.87 5.96 11.15 11.67
T4
50% RDF NPK with incorporation of crop
residue @ 2 t ha-1
7.11 9.89 14.29 12.08
T5 50% RDF NPK + PSB 10 kg ha -1 6.26 9.82 13.36 12.45
T6
50% RDF NPK + PSB 10 kg ha-1 + crop
residue @ 2 t ha-1
7.65 10.50 14.71 13.45
T7 50% RDF NPK + PSB 10 kg ha-1 + crop
residue @ 2 t ha-1 + Alkali water irrigation
passed through gypsum bed
8.85 11.66 15.55 13.81
SE (m) ± 0.20 0.38 0.42 0.37
C.D. at 5 % 0.56 1.08 1.24 1.04
34. Table No: 14 Impact of ISTM on soil organic carbon and available
nitrogen
( Source: Manjunath et al. (2015) Advances in Crop Science Tech. 3(1). Location: Mandya, Karnataka.)
Year
Organic carbon (%)
Difference in OC over
years (%)
Available N
(Kg ha-1)
Difference in
Avail. N over years (%)
ISTM Check ISTM Check ISTM Check ISTM Check
Before 0.42 0.44 - - 312.4 324.8 - -
Rabi 2008 0.45 0.42 6.3 -4.3 319.6 306.4 2.3 -5.7
Rabi 2009 0.50 0.40 11.3 -4.1 330.5 297.3 3.4 -3.0
Rabi 2010 0.58 0.40 16.0 -1.5 347.3 284.7 5.1 -4.2
Average 0.49 0.41 11.2 -3.3 327.4 303.3 3.6 -4.3
35. Table No: 15 Impact of ISTM on soil available phosphorus and
potassium
Year
Available P2O5
(Kg ha-1)
Difference in
Avail. P2O5 over
years (%)
Available K2O
(Kg ha-1)
Difference in
Avail. K2O over
years (%)
ISTM Check ISTM Check ISTM Check ISTM Check
Before 31.8 31.2 - - 232.5 244.6 - -
Rabi 2008 34.2 29.6 7.4 -5.1 248.3 236.8 6.8 -3.2
Rabi 2009 37.0 29.2 8.3 -1.4 277.1 228.4 11.6 -3.5
Rabi 2010 40.6 27.6 9.8 -5.5 319.2 230.3 15.2 0.8
Average 35.9 29.4 8.5 -4.0 269.3 235.0 11.2 -2.0
( Source: Manjunath et al. (2015) Advances in Crop Science Tech. 3(1). Location: Mandya, Karnataka.)
36. Table No: 16 Effect crop residue management in rice-wheat system on
soil microbial and enzymatic activity.
Indicators
Crop residue management practices
C.D.
(P=0.05)Removed Burned Incorporated
Incorporated +
Green manure
Bacteria (*106) 14.5 2.6 28.36 32.25 2.04
Fungi(*103) 58 11 105 125 15.83
Phosphatase activity
(Mg p-NP g-1h-1)
121 124 172 178 2.33
Dehydrogenase
activity
(mg TPFg-1 24 h-1)
32 29 55 65 1.07
(Source: Sharma et. al. (2018). Current Journal of Applied Science and Technology. Location: Bhagalpur, Bihar.)
42. Conclusion:
Crop residue management increase the organic matter
content in soil.
It improves the microbial activity in the soil.
It promote the utilization of agricultural raw material.
Crop residue must be used for conservation agriculture
for sustainable agriculture and healthy soil.
It improves soil physical, chemical and biological health.
43. Reduces the cost of cultivation.
Crop residue management helps to reduce environmental
pollution by reducing crop residue burning.
Judicious use of chemical fertilizer & organic residues
could bring considerable improvement in productivity of
various crops.