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CONCEPT NOTE
An agricultural extension project attempting
to double the rice yield of paddy rice
Gordon Hirst
September 2016
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page1
One ton per rai
Concept note
Contents:
1. Synopsys
2. Program targets
3. Data: Farm statistics
4. Methodology
5. Experiment programs
6. Timeline
7. Greenhouse gas mitigation
8. Project participants
References
Pictures
1. Synopsis:
According to FAO (Food and Agriculture Organization of United Nations) recent reports, rice demand in Asia is
currently outstripping supply and it is forecast for this trend to continue 1,2
. This problem is acerbated by static and
even falling productivity of rice per unit area in some parts of South East Asia. This inversion is due to numerous
and often interrelated reasons, the outcome of this is rural farmers are taken to increasing use of synthetic
fertilizers to sustain annual rice yield expectations.
Over half of the world’s population relying on rice as their primary source of nutrition and with paddy (flooded
field) rice accounting for 95% of total rice cultivation 3
. Understandably there are numerous agricultural initiatives
and extension programs addressing the issue of paddy rice yields. As with all development programs the theory and
the science is usually the easy part, getting it to work in the real world is often more difficult for even the most self-
evident applications.
Project: “One Ton Per Rai” (OTPR) is an infield experiment being undertaking on a working paddy rice farm in
central Thailand. A number of agricultural extension programs will be evaluated, working in concert and measured
against a known baseline.
Its goal is to demonstrate that rice yields can be increased significantly which will a. in the short term increase the
cash flow of local rural economies and b. in the long term mitigate the impending dilemma of food shortages. In
addition, it will be determined if this can be achieved within an economically and ecologically sustainable system
and also mitigate Greenhouse Gas (GHG) emissions.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page2
2. Program targets:
Thailand’s national paddy rice production rate is currently 3.01 ton/ha (2014) 4
(approximately ½ ton/rai Ɨ.) The
project proposes that using the agricultural extensions programs detailed herein, it is feasible to double rice yield to
6 ton/Ha (approximately 1 ton/Ria Ɨ). The project is a “proof in principle” undertaking, where the best practices for
increasing rice yield will be the primary consideration, with economic viability of the project secondary. This being
said, data gathered on the ‘real world,’ issues such as logistics and input costs can be assessed during the program
and cost benefit analysis will be calculated in a real world model.
Ɨ A Rai is a unit of area measurement used in Thailand and is equivalent to 40,000 m² or 6.25 Rai = 1 Hectare (ha)
It is expected that the project will require five years to achieve its targets
All results and procedures will be published open source
3. Data: Farm statistics:
Rice grown:
Typically the farm grown is Jasmine rice known as Mali rice or known in Thailand as Khao hom mali a variety of
Oriza indica.
The farm usually produces around 5 tons of rice averaging 500 Kg/Rai, in line with the national average.
There is a single rice harvest per season, seeded in July and harvested at the end of November. The seed is sown by
Broadcasting 5
. There is no winter crop.
The farm has been in the family for approximately 40 years and has been a one season crop of rice for every season
and has been consistent in rice production of between 400 Kg and 500 Kg per Rai.
Location:
Working name: Nong’s Farm
Located 10 Km West of Huai Thalaeng, a hamlet half way between Nakhon Ratchasima and Buri Ram in Nakhon
Ratchasima province, central Thailand
GPS: 15°0’31”N 102°33’12E
The farm consists Consist of nine paddies of varying sizes from 857 m² to 2882 m² (see picture 1 & 2) the rice farm
is 10.4 Rai in total (1.66 ha). A contour of 0.005% (1:200) gradient rising from NW to SE
Soil samples have been taken awaiting soils sample data results. Only one sample was taken the assumption being
that the soil is fairly homogenous across the farm.
Cross contamination of experiments is recognized as a potential issue of experimental procedure however, in this
regard we are singularly fortunate that the farm already possess substantial dike structures (bunds) running
throughout the farm. also it is well confined from other neighboring farms either by large bunds, roads or pathways
and hence limiting possible cross contamination.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page3
4. Methodology:
For the OTPR experiment the farm will be split into four sections, one for each for three experiments and a control.
Because of the uneven size of the paddies and various other aspects relating to the land contours etc., the
experimental plan has been laid out thus.
Experimental plot Experiment Size (mean 4133)
A Control 4033 m² 97.5% of mean
B Biochar and NPK 4100 m² 99.2 % of mean
C SRI, Biochar & NPK 3727 m² 90% of mean
D AWD, SRI, Biochar &
NPK
4672 m² 113 % of mean
Scientific and economic validity (what One Ton Rer Rai isn’t):
It is accepted that at the time of program design, it will be difficult to apportion exact scientific validity to the
experiment.
Nong’s farm is a working farm and the resultant crop an integral part of the families income. Their priority, in
conjunction with the project aims, is to produce as much rice as possible. The project will ultimately incur an
additional direct overhead such as logistics, infrastructure improvements and direct increased labor costs.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page4
Our approach can be qualified as being ‘nonscientific’, as it is the nature a working farm that rigorous control over
the many variables is virtually impossible. Therefore the project allows for a pragmatic, results driven approach.
With this in mind, the use relatively large experimental plots (average over 4000 m²), long experimental time
period (five years) it is proposed that the possible extraneous effect of external variables will be been reduced. This
will lend a validity to the results which are more than purely anecdotal.
In addition, the economics of the extensions and the input costs (both capex and opex) can be measured and
evaluated. Also close examination of the physical logistics of the extension methodology can be assessed during the
course of the program, this will highlight the non-technical issues with program.
There are no plans to adopt organic rice growing techniques.
5. Experimental programs
Experiment A: Control:
The control represents the ‘business as usual’ activities of the farm which have been practiced for at least the last
ten seasons and has produced a rice total consistent with the national and local mean.
Seeding methodology will be broadcasting 5
as previous seasons.
NPK (15–15–15) Ɨ will be added at a rate of mixed 25 Kg /rai just before reproductive phase (panicle initiation) 6
approximately 40 days after sowing.
Ɨ NPK = Nitrogen, Phosphorus and Potassium, 15-15-15 expressed as a total percentage of element of the overall
synthetic fertilizer mixture.
Experiment B: Biochar & NPK
Biochar is produced by the conversion of organic matter (usually waste biomass) into charcoal by a process of
pyrolysis (the burning in the matter with restricted oxygen). The resultant granular charcoal is an excellent soil
amendment, possessing a number of properties when prepared and used correctly is conducive to improved soil
conditions and higher crop yields. Although the practice of biochar has been around for millennia, it has only been
in recent decades has its full potential as an integral part of agrarian procedural practices been promoted
principally with the formation of the International Biochar Initiative IBI 7,8
. Commonly described as ‘the oldest new
technology you have never heard of’.
The use of successful use of biochar as a soil amendment requires a minimum of the rudimentary understanding of
soil mechanics, as there are qualifying issues both in the upstream (making effective biochar) and (downstream)
effective use of biochar.
The raw biochar produced from pyrolysis is not in a suitable condition to use immediately, its high adsorption
capacity will mean that it will adsorb all the nutrients within the soil, specifically Nitrogen (N), which will be
diverted away from the plant, this in commonly known as ‘nitrogen shock’8
. To ‘charge’ the biochar it is necessary
to combine the raw char with other ingredients and allowed to ‘charge’ which will present a product in which the
soil nutrients have already been converted into plant available form.
The additions will consist of manure (pig or cow) and local soil and a spray of EM (Effective Microorganisms). For
convenience EM is used instead of IMO (Indigenous Micro Organisms). The mix ratio will be 33-33-33. And will be
‘charged’ for three months prior to application in the field at a rate of 1 kg/ m² which will occur approximately one
month before seeding, dependent on rainfall.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page5
The fertilizer regime will include additional of NPK in this case will be mixed with the biochar mixture at 80:20
charged biochar: NPK (15-15-15), at a rate 25 Kg /rai of NPK
i.e.: total application rate of 125 Kg/rai mixture, this will be added shortly before seeding
A Nitrogen (40-0-0) boost prior to the reproductive phase 6
will be included and again will be mixed In addition an
80:20 charged biochar: N at rate of 25 Kg /rai of N
Experiment C: SRI (System of Rice Intensification) plus Experiment B:
Initially developed in Madagascar in 1980’s 9
and has since developed into a global agricultural extension project
centered from Cornell University college of Agriculture and life sciences 10
.The main premise behind SRI is to
develop agricultural systems which can increase rice yields using existing resources. Although theoretical
application of SRI reduces the methodology to a formulaic approach, in reality it relies heavily on the rice farmer’s
art. Therefore presenting the farmer with a matrix of solutions which can be a pick ‘n mix using; the farmers
experience of local conditions; a better understanding of soil conditions and new introduced planting/seeding
techniques. Chief amongst the new techniques is the use of placing a single seedling at a set distance apart usually
between 20 cm & 30 cm. There are numerous other methodological alterations but the single seed spacing is the
most visual.
Experiment D: Alternate Wet and Dry (AWD) Plus Experiment C:
Alternate Wet and Dry (known as AWD)11
is a paddy rice farming practice whereby the water control in the paddy is
regulated such that the rice plant receives sufficient water for growth rather than being flooded. Maintaining an
aerobic substrate in the paddy will greatly reduce the release of methane (CH4), a potent GHG (Greenhouse gas),
into the atmosphere, therefore AWD is primarily promoted as a GHG mitigation procedure. However, AWD
principles maximizes the efficiency of the farmers’ use of water, thus reducing the crops water requirement.
Current research has also indicated that AWD can increase rice yields as nutrient uptake decreases dramatically
when the flooded paddy is anaerobic. Also, with improved water control and usage it maybe become feasible to
increase, what has traditionally been a single crop per season farm, to two crop per season farm.
AWD does require additional input into the normally open loop growing cycle including the use of pumps
(additional costs and time) and will necessitate the construction of a 10,000 litre reservoir in the Plot D (see
Methodology) which also will decrease the effective growth area by approx. 100 m².
6. Timeline:
It is poposed that the first year trial will be 2017 sowing in late July of that year. The months following the 2016
harvest will be dedicated to field preparation which will require some back hoe work and bund repairs. Aditionally
the biochar needs to be sourced and charged in March 2017. The 2016 rice harvest will be measured and used as a
baseline.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page6
7. Greenhouse gas mitigation:
Although the primary aim of the program is to demonstrate procedures that can significantly increase rice yields, in
a wider context, its environmental impact will be evaluated, therefore it is imperative that the program recognizes
the need for both sustainability and environmental soundness.
Paddy rice production is estimated to account for between 5 - 20% anthropogenic GHG emissions 12,13
. Given this, it
would be positive to demonstrate that the methods we have employed would establish a net GHG reduction. There
is much discussion on the subject of GHG mitigation employing agricultural programs specifically targeting Paddy
rice cultivation. Many are very contentious and scientists and experts in numerous fields are in disagreement over
all of them.14
However, the program as designed has a number of recognized greenhouse gas mitigation mechanisms which
would could be accumulative.
1. Reduction of GHG emissions from switching to pyrolysis of waste biomass from traditional methods of
use/disposal. Its very difficult to place a precise figure on the level of mitigation as this observation would
be dependent a number factors which is completely out of the scope of the program, i.e. what is the
feedstock? What is the pyrolysis methodology? What is the logistical mass flow effect what would normally
be the conversion on of waste biomass? (i.e.: burning or composting etc.). What are the transport logistics?
etc. etc.
2. Carbon sequestration by returning Black Carbon (BC) to the ground sequestering carbon for hundreds
perhaps thousands of years.
3. Reduce the use of synthetic fertilizers and the associated manufacturing train which emits GHG.
4. AWD proposes that the flooded paddy never converts to anaerobic conditions which releases methane into
the atmosphere it is worth noting however that paradoxically the introduction of water into a dry paddy
can increase CO2
Emissions and NOX emissions by a process known as the “Birch effect”15
Ɨ
Ɨ At the time of instigation of the One Ton Per Rai project it is not scheduled for acquisition of data relating to
methane emissions of calculations of net reduction of GHG emissions. In the future however it would be an
excellent opportunity to make side by side comparative measurements. At the current time the global trade in
carbon credits is depressed and no carbon crediting mechanism exist for either part or wholly for the program in
Thailand.
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page7
8. Project participants
Project manager:
Gordon Hirst
Appropriate technology consultant, former environmental program manager Warm Heart foundation
Farm manager:
Jureeporn Kanconchum (Nong)
Fourth generation rice farmer has been cultivating rice on this farm for five seasons
Technical consultants and collaborators:
In addition to the project leads there is a number of academics, researchers and technical advisors who are integral
to the success of the project and agreed to be named collaborators:
Dr. Wolfram Spreer
Lecturer and assistant dean for research and international affairs
Chiang Mai University, Faculty of agriculture Chiang Mai, Thailand
Asst. Prof. Suphatihida Aumtong:
Assistant dean/chairman of soil science program (AWD specialist)
Soil science program, Department of Agriculture, Mae Jo University
Mae Jo, Chiang Mai province, Thailand
Dr. Edward Allen
Consultant soil scientist (specializing in tropical soils)
Vientiane, PDR Laos
Warm Heart Foundation
Dr. Michel Shafer director Warm Heart biochar and environmental program (supplier of biochar to OTPR project)
Echo Asia impact center
Dr. Abram Bicksler: Director
Boomsong Thansirtong: Agriculture program manager (SRI specialists)
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page8
Pictures
Picture 1
Picture 2
One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1
Page9
References
1. https://www.washingtonpost.com/news/wonk/wp/2013/07/01/this-unsettling-chart-shows-were-not-
growing-enough-food-to-feed-the-world/
2. European Journal of Agronomy Volume 36, Issue 1, January 2012, Rice yields and yield gaps in Southeast
Asia: Past trends and future outlook Alice G. Labortea, b, Kees (C.A.J.M.) de Biea, Eric M.A. Smalinga,
Piedad F. Moyab, Anita A. Bolingb, Martin K. Van Ittersumc
(http://www.sciencedirect.com/science/article/pii/S1161030111000979)
3. (http://pdf.usaid.gov/pdf_docs/PNABE720.pdf) Upland rice a global perspective PC Gupta JC O’Toole IRRI
4. CGAIR global rice science partnership (http://ricepedia.org/thailand)
5. https://en.wikipedia.org/wiki/Broadcast_seeding
6. http://ricepedia.org/rice-as-a-plant/growth-phases
7. http://www.biochar-international.org/about
8. Biochar an organic house for microbes: Echo Asia notes (https://c.ymcdn.com/sites/echocommunity.site-
ym.com/resource/collection/F6FFA3BF-02EF-4FE3-B180-F391C063E31A/Biochar-
An_Organic_House_for_Soil_Microbes.pdf)
9. ORIGIN OF THE SYSTEM OF RICE INTENSIFICATION (SRI) (http://sri.ciifad.cornell.edu/aboutsri/origin/)
10. Cornell university college of agriculture and life science SRI international network and resource centre
(http://sri.ciifad.cornell.edu/)
11. New irrigation technique can ease drought effect on rice 06 June 2014 (http://irri.org/news/media-
releases/new-irrigation-technique-can-ease-drought-effect-on-rice)
12. How realistic is the prospect of low-carbon rice production? Lessons from China: Sheng Zhou and Xiangfu
Song
13. Methane Emissions from Rice Cultivation :Flooded Rice Fields (http://www.ipcc-
nggip.iges.or.jp/public/gl/guidelin/ch4ref5.pdf)
14. Sustainable biochar to mitigate global climate change
(https://www.researchgate.net/publication/47545113_Sustainable_biochar_to_mitigate_global_climate_c
hange_Nat_Comm_156)
15. Drying and wetting of Mediterranean soils stimulates decomposition and carbon dioxide emission: the
“Birch effect”

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OTPR Concepte note issue 1

  • 1. CONCEPT NOTE An agricultural extension project attempting to double the rice yield of paddy rice Gordon Hirst September 2016
  • 2. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page1 One ton per rai Concept note Contents: 1. Synopsys 2. Program targets 3. Data: Farm statistics 4. Methodology 5. Experiment programs 6. Timeline 7. Greenhouse gas mitigation 8. Project participants References Pictures 1. Synopsis: According to FAO (Food and Agriculture Organization of United Nations) recent reports, rice demand in Asia is currently outstripping supply and it is forecast for this trend to continue 1,2 . This problem is acerbated by static and even falling productivity of rice per unit area in some parts of South East Asia. This inversion is due to numerous and often interrelated reasons, the outcome of this is rural farmers are taken to increasing use of synthetic fertilizers to sustain annual rice yield expectations. Over half of the world’s population relying on rice as their primary source of nutrition and with paddy (flooded field) rice accounting for 95% of total rice cultivation 3 . Understandably there are numerous agricultural initiatives and extension programs addressing the issue of paddy rice yields. As with all development programs the theory and the science is usually the easy part, getting it to work in the real world is often more difficult for even the most self- evident applications. Project: “One Ton Per Rai” (OTPR) is an infield experiment being undertaking on a working paddy rice farm in central Thailand. A number of agricultural extension programs will be evaluated, working in concert and measured against a known baseline. Its goal is to demonstrate that rice yields can be increased significantly which will a. in the short term increase the cash flow of local rural economies and b. in the long term mitigate the impending dilemma of food shortages. In addition, it will be determined if this can be achieved within an economically and ecologically sustainable system and also mitigate Greenhouse Gas (GHG) emissions.
  • 3. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page2 2. Program targets: Thailand’s national paddy rice production rate is currently 3.01 ton/ha (2014) 4 (approximately ½ ton/rai Ɨ.) The project proposes that using the agricultural extensions programs detailed herein, it is feasible to double rice yield to 6 ton/Ha (approximately 1 ton/Ria Ɨ). The project is a “proof in principle” undertaking, where the best practices for increasing rice yield will be the primary consideration, with economic viability of the project secondary. This being said, data gathered on the ‘real world,’ issues such as logistics and input costs can be assessed during the program and cost benefit analysis will be calculated in a real world model. Ɨ A Rai is a unit of area measurement used in Thailand and is equivalent to 40,000 m² or 6.25 Rai = 1 Hectare (ha) It is expected that the project will require five years to achieve its targets All results and procedures will be published open source 3. Data: Farm statistics: Rice grown: Typically the farm grown is Jasmine rice known as Mali rice or known in Thailand as Khao hom mali a variety of Oriza indica. The farm usually produces around 5 tons of rice averaging 500 Kg/Rai, in line with the national average. There is a single rice harvest per season, seeded in July and harvested at the end of November. The seed is sown by Broadcasting 5 . There is no winter crop. The farm has been in the family for approximately 40 years and has been a one season crop of rice for every season and has been consistent in rice production of between 400 Kg and 500 Kg per Rai. Location: Working name: Nong’s Farm Located 10 Km West of Huai Thalaeng, a hamlet half way between Nakhon Ratchasima and Buri Ram in Nakhon Ratchasima province, central Thailand GPS: 15°0’31”N 102°33’12E The farm consists Consist of nine paddies of varying sizes from 857 m² to 2882 m² (see picture 1 & 2) the rice farm is 10.4 Rai in total (1.66 ha). A contour of 0.005% (1:200) gradient rising from NW to SE Soil samples have been taken awaiting soils sample data results. Only one sample was taken the assumption being that the soil is fairly homogenous across the farm. Cross contamination of experiments is recognized as a potential issue of experimental procedure however, in this regard we are singularly fortunate that the farm already possess substantial dike structures (bunds) running throughout the farm. also it is well confined from other neighboring farms either by large bunds, roads or pathways and hence limiting possible cross contamination.
  • 4. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page3 4. Methodology: For the OTPR experiment the farm will be split into four sections, one for each for three experiments and a control. Because of the uneven size of the paddies and various other aspects relating to the land contours etc., the experimental plan has been laid out thus. Experimental plot Experiment Size (mean 4133) A Control 4033 m² 97.5% of mean B Biochar and NPK 4100 m² 99.2 % of mean C SRI, Biochar & NPK 3727 m² 90% of mean D AWD, SRI, Biochar & NPK 4672 m² 113 % of mean Scientific and economic validity (what One Ton Rer Rai isn’t): It is accepted that at the time of program design, it will be difficult to apportion exact scientific validity to the experiment. Nong’s farm is a working farm and the resultant crop an integral part of the families income. Their priority, in conjunction with the project aims, is to produce as much rice as possible. The project will ultimately incur an additional direct overhead such as logistics, infrastructure improvements and direct increased labor costs.
  • 5. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page4 Our approach can be qualified as being ‘nonscientific’, as it is the nature a working farm that rigorous control over the many variables is virtually impossible. Therefore the project allows for a pragmatic, results driven approach. With this in mind, the use relatively large experimental plots (average over 4000 m²), long experimental time period (five years) it is proposed that the possible extraneous effect of external variables will be been reduced. This will lend a validity to the results which are more than purely anecdotal. In addition, the economics of the extensions and the input costs (both capex and opex) can be measured and evaluated. Also close examination of the physical logistics of the extension methodology can be assessed during the course of the program, this will highlight the non-technical issues with program. There are no plans to adopt organic rice growing techniques. 5. Experimental programs Experiment A: Control: The control represents the ‘business as usual’ activities of the farm which have been practiced for at least the last ten seasons and has produced a rice total consistent with the national and local mean. Seeding methodology will be broadcasting 5 as previous seasons. NPK (15–15–15) Ɨ will be added at a rate of mixed 25 Kg /rai just before reproductive phase (panicle initiation) 6 approximately 40 days after sowing. Ɨ NPK = Nitrogen, Phosphorus and Potassium, 15-15-15 expressed as a total percentage of element of the overall synthetic fertilizer mixture. Experiment B: Biochar & NPK Biochar is produced by the conversion of organic matter (usually waste biomass) into charcoal by a process of pyrolysis (the burning in the matter with restricted oxygen). The resultant granular charcoal is an excellent soil amendment, possessing a number of properties when prepared and used correctly is conducive to improved soil conditions and higher crop yields. Although the practice of biochar has been around for millennia, it has only been in recent decades has its full potential as an integral part of agrarian procedural practices been promoted principally with the formation of the International Biochar Initiative IBI 7,8 . Commonly described as ‘the oldest new technology you have never heard of’. The use of successful use of biochar as a soil amendment requires a minimum of the rudimentary understanding of soil mechanics, as there are qualifying issues both in the upstream (making effective biochar) and (downstream) effective use of biochar. The raw biochar produced from pyrolysis is not in a suitable condition to use immediately, its high adsorption capacity will mean that it will adsorb all the nutrients within the soil, specifically Nitrogen (N), which will be diverted away from the plant, this in commonly known as ‘nitrogen shock’8 . To ‘charge’ the biochar it is necessary to combine the raw char with other ingredients and allowed to ‘charge’ which will present a product in which the soil nutrients have already been converted into plant available form. The additions will consist of manure (pig or cow) and local soil and a spray of EM (Effective Microorganisms). For convenience EM is used instead of IMO (Indigenous Micro Organisms). The mix ratio will be 33-33-33. And will be ‘charged’ for three months prior to application in the field at a rate of 1 kg/ m² which will occur approximately one month before seeding, dependent on rainfall.
  • 6. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page5 The fertilizer regime will include additional of NPK in this case will be mixed with the biochar mixture at 80:20 charged biochar: NPK (15-15-15), at a rate 25 Kg /rai of NPK i.e.: total application rate of 125 Kg/rai mixture, this will be added shortly before seeding A Nitrogen (40-0-0) boost prior to the reproductive phase 6 will be included and again will be mixed In addition an 80:20 charged biochar: N at rate of 25 Kg /rai of N Experiment C: SRI (System of Rice Intensification) plus Experiment B: Initially developed in Madagascar in 1980’s 9 and has since developed into a global agricultural extension project centered from Cornell University college of Agriculture and life sciences 10 .The main premise behind SRI is to develop agricultural systems which can increase rice yields using existing resources. Although theoretical application of SRI reduces the methodology to a formulaic approach, in reality it relies heavily on the rice farmer’s art. Therefore presenting the farmer with a matrix of solutions which can be a pick ‘n mix using; the farmers experience of local conditions; a better understanding of soil conditions and new introduced planting/seeding techniques. Chief amongst the new techniques is the use of placing a single seedling at a set distance apart usually between 20 cm & 30 cm. There are numerous other methodological alterations but the single seed spacing is the most visual. Experiment D: Alternate Wet and Dry (AWD) Plus Experiment C: Alternate Wet and Dry (known as AWD)11 is a paddy rice farming practice whereby the water control in the paddy is regulated such that the rice plant receives sufficient water for growth rather than being flooded. Maintaining an aerobic substrate in the paddy will greatly reduce the release of methane (CH4), a potent GHG (Greenhouse gas), into the atmosphere, therefore AWD is primarily promoted as a GHG mitigation procedure. However, AWD principles maximizes the efficiency of the farmers’ use of water, thus reducing the crops water requirement. Current research has also indicated that AWD can increase rice yields as nutrient uptake decreases dramatically when the flooded paddy is anaerobic. Also, with improved water control and usage it maybe become feasible to increase, what has traditionally been a single crop per season farm, to two crop per season farm. AWD does require additional input into the normally open loop growing cycle including the use of pumps (additional costs and time) and will necessitate the construction of a 10,000 litre reservoir in the Plot D (see Methodology) which also will decrease the effective growth area by approx. 100 m². 6. Timeline: It is poposed that the first year trial will be 2017 sowing in late July of that year. The months following the 2016 harvest will be dedicated to field preparation which will require some back hoe work and bund repairs. Aditionally the biochar needs to be sourced and charged in March 2017. The 2016 rice harvest will be measured and used as a baseline.
  • 7. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page6 7. Greenhouse gas mitigation: Although the primary aim of the program is to demonstrate procedures that can significantly increase rice yields, in a wider context, its environmental impact will be evaluated, therefore it is imperative that the program recognizes the need for both sustainability and environmental soundness. Paddy rice production is estimated to account for between 5 - 20% anthropogenic GHG emissions 12,13 . Given this, it would be positive to demonstrate that the methods we have employed would establish a net GHG reduction. There is much discussion on the subject of GHG mitigation employing agricultural programs specifically targeting Paddy rice cultivation. Many are very contentious and scientists and experts in numerous fields are in disagreement over all of them.14 However, the program as designed has a number of recognized greenhouse gas mitigation mechanisms which would could be accumulative. 1. Reduction of GHG emissions from switching to pyrolysis of waste biomass from traditional methods of use/disposal. Its very difficult to place a precise figure on the level of mitigation as this observation would be dependent a number factors which is completely out of the scope of the program, i.e. what is the feedstock? What is the pyrolysis methodology? What is the logistical mass flow effect what would normally be the conversion on of waste biomass? (i.e.: burning or composting etc.). What are the transport logistics? etc. etc. 2. Carbon sequestration by returning Black Carbon (BC) to the ground sequestering carbon for hundreds perhaps thousands of years. 3. Reduce the use of synthetic fertilizers and the associated manufacturing train which emits GHG. 4. AWD proposes that the flooded paddy never converts to anaerobic conditions which releases methane into the atmosphere it is worth noting however that paradoxically the introduction of water into a dry paddy can increase CO2 Emissions and NOX emissions by a process known as the “Birch effect”15 Ɨ Ɨ At the time of instigation of the One Ton Per Rai project it is not scheduled for acquisition of data relating to methane emissions of calculations of net reduction of GHG emissions. In the future however it would be an excellent opportunity to make side by side comparative measurements. At the current time the global trade in carbon credits is depressed and no carbon crediting mechanism exist for either part or wholly for the program in Thailand.
  • 8. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page7 8. Project participants Project manager: Gordon Hirst Appropriate technology consultant, former environmental program manager Warm Heart foundation Farm manager: Jureeporn Kanconchum (Nong) Fourth generation rice farmer has been cultivating rice on this farm for five seasons Technical consultants and collaborators: In addition to the project leads there is a number of academics, researchers and technical advisors who are integral to the success of the project and agreed to be named collaborators: Dr. Wolfram Spreer Lecturer and assistant dean for research and international affairs Chiang Mai University, Faculty of agriculture Chiang Mai, Thailand Asst. Prof. Suphatihida Aumtong: Assistant dean/chairman of soil science program (AWD specialist) Soil science program, Department of Agriculture, Mae Jo University Mae Jo, Chiang Mai province, Thailand Dr. Edward Allen Consultant soil scientist (specializing in tropical soils) Vientiane, PDR Laos Warm Heart Foundation Dr. Michel Shafer director Warm Heart biochar and environmental program (supplier of biochar to OTPR project) Echo Asia impact center Dr. Abram Bicksler: Director Boomsong Thansirtong: Agriculture program manager (SRI specialists)
  • 9. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page8 Pictures Picture 1 Picture 2
  • 10. One Ton Per Rai Author: Gordon Hirst September 2016: Issue 1 Page9 References 1. https://www.washingtonpost.com/news/wonk/wp/2013/07/01/this-unsettling-chart-shows-were-not- growing-enough-food-to-feed-the-world/ 2. European Journal of Agronomy Volume 36, Issue 1, January 2012, Rice yields and yield gaps in Southeast Asia: Past trends and future outlook Alice G. Labortea, b, Kees (C.A.J.M.) de Biea, Eric M.A. Smalinga, Piedad F. Moyab, Anita A. Bolingb, Martin K. Van Ittersumc (http://www.sciencedirect.com/science/article/pii/S1161030111000979) 3. (http://pdf.usaid.gov/pdf_docs/PNABE720.pdf) Upland rice a global perspective PC Gupta JC O’Toole IRRI 4. CGAIR global rice science partnership (http://ricepedia.org/thailand) 5. https://en.wikipedia.org/wiki/Broadcast_seeding 6. http://ricepedia.org/rice-as-a-plant/growth-phases 7. http://www.biochar-international.org/about 8. Biochar an organic house for microbes: Echo Asia notes (https://c.ymcdn.com/sites/echocommunity.site- ym.com/resource/collection/F6FFA3BF-02EF-4FE3-B180-F391C063E31A/Biochar- An_Organic_House_for_Soil_Microbes.pdf) 9. ORIGIN OF THE SYSTEM OF RICE INTENSIFICATION (SRI) (http://sri.ciifad.cornell.edu/aboutsri/origin/) 10. Cornell university college of agriculture and life science SRI international network and resource centre (http://sri.ciifad.cornell.edu/) 11. New irrigation technique can ease drought effect on rice 06 June 2014 (http://irri.org/news/media- releases/new-irrigation-technique-can-ease-drought-effect-on-rice) 12. How realistic is the prospect of low-carbon rice production? Lessons from China: Sheng Zhou and Xiangfu Song 13. Methane Emissions from Rice Cultivation :Flooded Rice Fields (http://www.ipcc- nggip.iges.or.jp/public/gl/guidelin/ch4ref5.pdf) 14. Sustainable biochar to mitigate global climate change (https://www.researchgate.net/publication/47545113_Sustainable_biochar_to_mitigate_global_climate_c hange_Nat_Comm_156) 15. Drying and wetting of Mediterranean soils stimulates decomposition and carbon dioxide emission: the “Birch effect”