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Multispectral Images Tetracam Agriculture Digital to Estimate Nitrogen and Grain Yield of Rice at Different Growth Stages

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Several methods are available to monitor the nitrogen content of rice during its various growth stages. However, monitoring still requires a quick, simple, accurate and inexpensive technique that needs to be developed. In this study, Tetracam Agriculture Digital Camera was used to acquire high spatial and temporal resolution images to determine the status of N and predict the grain yield of rice (Oryza sativa L.). Twelve pots of rice were subjected to four different N treatments (0, 125, 175 and 250 kg ha-1). Three replicates were arranged in a randomized complete block design to determine the status of N and predict rice yield. The images were captured at different growth stages (i.e., tillering, panicle initiation, booting and heading stage) of rice in each pot. N and grain yield were significantly correlated with NDVI (R2 = 0.78) and GNDVI (R2 = 0.88), especially at the panicle initiation and booting stages, respectively. The study demonstrated the suitability of using the Tetracam images as a sensor for estimating chlorophyll content and N. Moreover, the findings showed that the images revealed their potential use in forecasting grain yield at different growth stages of rice. Key Words: grain yield, nitrogen, rice, Tetracam agriculture digital camera, vegetation indices
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116
INTRODUCTION
Nitrogen (N) is one of the most critical nutrients for crop
production in the world. It is also the nutrient element
applied in the largest quantity for most annual crops
(Huber and Thompson 2007). Fageria et al. (2008)
reported that N was responsible for 85% of the variation
in rice grain yield in Brazilian Inceptisol. In the
developing countries, intensive agricultural production
systems have increased the use of N fertilizer in an effort
to produce and sustain high crop yield, although only 20–
35% of N fertilizer is recovered by the crop because of
losses in several ways (Ponnamperuma and Deturck
1993). It means that N represents the largest part in
fertilizer variable input costs especially in paddy fields
with a double cropping system. On the other hand, lack
of the appropriate amount of N can cause either N stress
or N loss on the crop or environmental pollution, which
is of great concern to the public. Thus, appropriate N
management can help to improve overall rice production
to meet address the need for food security as well as
prevent environmental pollution.
Several different methods are available for assessing
the N status of the crop. One of these methods is tissue
analysis, an example of which is determining the
Kjeldahl N. It is a direct and accurate way of detecting
the N status of a crop, but it is time-consuming and
operators are required. Another technique is use of the
Soil Plant Analysis Development (SPAD) meter to
estimate N status from the measurement of leaf
transmittance in two wavebands centred at 650 nm and
940 nm (e.g., Gholizadeh et al. 2009). Although this
estimation method can be faster and cheaper than
analysis conducted in the laboratory, it still requires field
references, which are derived from laborious procedures
of leaf measurement in the field (Confalonieri et al.
2006).
Multi-Spectral Images Tetracam Agriculture Digital Camera to
Estimate Nitrogen and Grain Yield of Rice at Different Growth Stages
M. M. Saberioon
*, 1
, M. S. M. Amin
1
, W. Aimrun
2
, A. R. Anuar
3
and A. Gholizadeh
1
1
Centre of Precision Farming Technology, Faculty of Engineering, Universiti Putra Malaysia, Serdang, 43400
Selangor, Malaysia
2
Department of Biological and Agricultural Engineering, Faculty of Engineering, Universiti Putra Malaysia
3
Department of Land Management, Faculty of Agriculture, Universiti Putra Malaysia
*
Author for correspondence; e-mail: saberioon@gmail.com; Tel.: + 60 17 6161071; Fax: +60 38 6566061
Several methods are available to monitor the nitrogen content of rice during its various growth stages.
However, monitoring still requires a quick, simple, accurate and inexpensive technique that needs to be
developed. In this study, Tetracam Agriculture Digital Camera was used to acquire high spatial and
temporal resolution images to determine the status of N and predict the grain yield of rice (Oryza sativa
L.). Twelve pots of rice were subjected to four different N treatments (0, 125, 175 and 250 kg ha-1). Three
replicates were arranged in a randomized complete block design to determine the status of N and
predict rice yield. The images were captured at different growth stages (i.e., tillering, panicle initiation,
booting and heading stage) of rice in each pot. N and grain yield were significantly correlated with NDVI
(R2 = 0.78) and GNDVI (R2 = 0.88), especially at the panicle initiation and booting stages, respectively.
The study demonstrated the suitability of using the Tetracam images as a sensor for estimating
chlorophyll content and N. Moreover, the findings showed that the images revealed their potential use
in forecasting grain yield at different growth stages of rice.
Key Words: grain yield, nitrogen, rice, Tetracam agriculture digital camera, vegetation indices
Abbreviations: ADC – agriculture digital camera, DAP – days after planting, GNDVI – Green-Normalized Difference
Vegetation Index, L – Optimal for Adjusting Soil Optical Properties, LNC – leaf nitrogen concentration, NDVI –
Normalized Difference Vegetation Index, NIR near infrared, RCBD – randomized complete block design, RS
remote sensing, SAVI – Soil-Adjusted Vegetation Index
ISSN 0031-7454 PHILIPP AGRIC SCIENTIST
Vol. 96 No. 1, 116–121
March 2013
The Philippine Agricultural Scientist Vol. 96 No. 1 (March 2013)
117
Researchers also estimate N status remotely. Remote
Sensing (RS) with aerial images is used to assess N over
the entire fields. Shou et al. (2007) used the high
resolution satellite to evaluate the N status of winter
wheat, which proved that near infrared (NIR) reflectance
has good correlation with sap N concentration, but low
correlation with shoot total N concentration and shoot
biomass. Limitations of these platforms for commercial
use on individual fields are the high cost of images, the
low temporal resolution of satellite images and the short
availability of usable data from satellite images because
of clouds and shadows of clouds. Moreover, the accuracy
of such a technique appears to be easily affected by low
resolution and obvious soil background noises (Broge
and Leblanc 2001). Airborne sensors offer much greater
flexibility than satellite platforms by being able to
operate under clouds and by having a much finer spatial
resolution (Lamb and Brown 2001). However, this type
of imagery is still costly when dedicated ‘mobilization’
of the aircraft is required, especially for remote locations
and repeated data acquisition needs. Therefore, a rapid,
accurate, simple and inexpensive method to monitor a
crop’s N status in the field with high temporal resolution
would be helpful to make rice production more
environmentally and economically sound.
Studies of RS applications in agriculture have used
Vegetation Indices (VIs) to evaluate crop condition. VIs
are easily used and would be an accurate and simple
method in digital image analysis for determining N status
in crops (Hansen and Schjoerring 2003). These indices
are used to enhance the vegetation features and also
reduce the influence of exogenous factors (Daughtry et
al. 2000; Xue et al. 2004).
Tetracam Agriculture Digital Camera (ADC)
(Tetracam, Inc., Chatsworth, Cal.) is one of the ground
platform remote sensors which has been re-engineered
recently to be the simplest and most flexible visible and
near infrared (NIR) camera. It can capture images in
visible light wavelengths longer than 520 nm and near-
infrared wavelengths up to 920 nm. Recently, Swain et
al. (2010) used the Tetracam ADC in paddy fields to
determine the total biomass and to predict the yield as a
function of nutrient status.
Leaf N concentration (LNC) can be determined by
using spectraradiometry from compiled bands of 620 and
760 or 400,620 and 880 nm (Shibayam and Akiyama
1989). Tetracam, which has the potential for determining
the amount of N in crops, covers these wavelengths.
Furthermore, this lightweight camera can be used under
cloudy conditions to monitor the status of N after
planting or during growing stages, with high spatial and
temporal resolution.
This study evaluated the capability of Tetracam ADC
in monitoring N status and estimating yield in paddy
fields on a canopy scale as a fast, inexpensive and simple
technique by using different VIs during the different
growth stages of a crop. Knowledge of N status before
applying fertilizer will enable farmers to practice
precision farming in rice cultivation.
MATERIALS AND METHODS
Theoretical Calculation
In this study, the three most common vegetation indices
were used, namely, Normalized Difference Vegetation
Index (NDVI), Green-Normalized Difference Vegetation
Index (GNDVI) and Soil Adjusted Vegetation Index
(SAVI). NDVI is expressed as follows:
(1)
where NIR is near infrared and R is red.
GNDVI is more highly correlated with final grain
yield in corn (Shanahan et al. 2001). It can be a
promising index for determining the status of N uptake in
wheat during its growth stages (Moges et al. 2005).
GNDVI can be calculated based on the equation
GNDVI (2)
where NIR is near infrared and G is green.
Another index, SAVI, has been developed to
minimize the background influences since NDVI is
affected by soil brightness. SAVI is formulated using the
equation (3)
where NIR is near infrared, R is red and L is the function
of vegetation density.
The value of L is critical in minimizing the influence
of backgrounds in vegetation reflectance. Based on a
suggestion by Huete (1988), L with the value of 0.5 is
optimal for adjusting soil-optical properties.
Field Preparation
The field experiment was conducted at Field No. 2 of the
Universiti Putra Malaysia. The soil in the pots was
obtained from the Tanjung Karang area within Block C
from a major soil series, namely, Telok series (Typic
Sulfaquept). The experiment comprised 12 pots
measuring 3 × 3 m. Rice (Oryza sativa L.) cv. MR-219
was sown in a completely randomized block designed
with three replicates and grown under flooded conditions.
In addition, four different levels of N fertilization were
applied to the rice cultivar, namely, a control with no
fertilizer (N0), and three additional N levels [N1: 22.1,
31.45, 22.95 and 8.5 kg ha
-1
; N2: 44.2, 62.9, 45.9 and 17
Tetracam for Estimation of Nitrogen and Grain Yield M. M. Saberioon et al.
The Philippine Agricultural Scientist Vol. 96 No. 1 (March 2013)
118
kg ha
-1
; and N3: 65, 92.5, 67.5 and 25 kg ha
-1
, which
were applied at the three leaf-stage (15–20 d after
planting, DAP), tillering (35–40 DAP), panicle formation
(55–60 DAP) and grain formation stages (65–70 DAP),
respectively].
Data Acquisition
Vertical images from the central zone of the pots during
tillering, panicle initiation, booting and heading stages
were obtained with a Tetracam ADC (Tetracam Inc.,
Chatsworth, CA, USA). All images were taken between
12:00 and 13:00 on clear days for comparable solar angle
and light intensity, and stored as Raw-8bit image (RAW)
format. The camera had been calibrated by capturing the
images from the Teflon calibration tag under the same
lighting conditions as the images under study.
For a comparison of image acquisition, a SPAD-502
chlorophyll meter (Minolta, Osaka, Japan) was used to
measure the chlorophyll concentration of rice at the
center of the youngest fully developed leaves. Ten
measurements of leaves from each pot were taken and an
average SPAD value for each pot was calculated at each
sampling time as the final value of this rice sample and as
the reference concentration of its N status. Grain yield
data were collected after 110 d. The yield samples were
air-dried and threshed for grains with hull, and the
weights were expressed on the basis of 14% moisture
content.
Image Processing
Images captured by the Tetracam ADC camera were
uploaded to the PixelWrench2 software (Tetracam, Inc,
Chatsworth, Cal.) for deriving the vegetation indices
(VIs). Furthermore, NDVI, Green-NDVI and SAVI were
produced for each image, from which the averages VIs
were estimated.
RESULTS AND DISCUSSION
Estimation of N and Chlorophyll Content Using
Vegetation Indices
Pearson’s correlation between the indexed and SPAD
readings (Table 1) shows that the indices had no
significant correlation with SPAD at the tillering stage,
but all of them showed a significant positive correlation
with the SPAD readings (P = 0.01) at the panicle
initiation and booting stages. Moreover, Table 1 shows
the positive correlation of SPAD readings with only the
NDVI and SAVI at the heading stage. The highest
correlation could be seen between the vegetation indices
and the SPAD readings at panicle initiation. Moreover,
among the indices, SAVI had the highest correlation with
the SPAD readings during the same growth stage (r =
0.896). All three indices generally showed a downward
trend in the correlation with the SPAD readings. In other
words, the correlation between SPAD and NDVI,
GNDVI and SAVI decreased with the growth stage.
The regression model was developed for SPAD with
NDVI, GNDVI and SAVI values in SPSS (IBM
®
SPSS
®
software). The results indicated a good fit (R
2
= 0.78,
RMSE = 2.59) for NDVI at panicle initiation (Table 2).
In general, the indices had the highest correlation with
SPAD during the panicle initiation and booting stages.
Estimation of Grain Yield Using Vegetation Indices
Pearson’s correlation between grain yield and indices
(Table 3) shows a highly significant positive correlation
between indices and grain yield at both panicle initiation
and booting stages (P = 0.01). The highest correlation
could be seen between GNDVI and grain yield at the
booting stage. There was an upward trend in the
correlation between the grain yield and vegetation indices
from panicle initiation to the booting stage. This increase
suggests that the booting stage could be the most
appropriate time to forecast the grain yield by using VIs.
Furthermore, a regression model was developed for both
grain yield and VIs. The results (Table 4) showed a good
regression between GNDVI and grain yield at booting
(R
2
= 0.88, RMSE = 2.33). The estimation models were
developed for this study by using the SPSS in order to
gain good fit models for N estimation. The fit estimation
regression model between SPAD and VIs can be found in
Table 5. Also, the fit estimation regression model
between VIs and grain yield is shown in Table 6.
CONCLUSION
Tetracam ADC was used for capturing multi-spectral
images over rice canopy to estimate the chlorophyll
content, N and grain yield. We found that Tetracam ADC
may be a promising sensor for capturing images to
determine N status and predict yield in rice. The relation
between VIs and SPAD readings also showed the
applicability of the Tetracam ADC images for
determining the status of N in rice. The linear regression
model demonstrated a good fit (R
2
= 0.78) for estimating
N in rice using Tetracam ADC based on NDVI and
GNDVI. The linear model (R
2
= 0.88) suggested that rice
Table 1. Correlation between vegetation index (VI) and
soil plant analysis development (SPAD) reading at
various growth stages of rice.
Growth Stage Days After
Planting NDVI GNDVI SAVI
Tillering 51 0.572
n.s.
0.567
n.s.
0.571
n.s.
Panicle initiation 60 0.887
**
0.886
**
0.896
**
Booting 79 0.785
**
0.783
**
0.749
**
Heading 93 0.789
**
−0.356
n.s.
0.654
**
**
Significant at 0.01.
n.s.
No significant correlation
NDVI normalized difference vegetation index, GNDVI – green-
normalized difference vegetation index, SAVI – soil adjusted vegetation
index
The Philippine Agricultural Scientist Vol. 96 No. 1 (March 2013)
Tetracam for Estimation of Nitrogen and Grain Yield M. M. Saberioon et al.
119
yield could be predicted by using GNDVI derived from
images obtained by the Tetracam ADC. Our study also
confirmed that the best growth stages for measuring the
status of N in rice would be the panicle initiation and
booting stages. Further study is recommended to evaluate
the capability of other nutrients, which have important
roles during the different growth stages of rice in paddy
fields.
REFERENCES CITED
BROGE NH, LEBLANC E. 2001. Comparing prediction power
and stability of broadband and hyperspectral vegetation
indices for estimation of green leaf area index and canopy
chlorophyll density. Remote Sens Environ 76:156–172.
CONFALONIERI R, STROPPIANA D, BOSCHETTI M,
GUSBERTI D, BOCCHI S, ACUTIS M. 2006. Analysis of
rice sample size variability due to development stage,
nitrogen fertilization, sowing technique and variety using
the visual jackknife. Field Crop Res 97:135–141.
DAUGHTRY CST, WAITHALL CL, KIM MS, DE
COLSTOUN EB, McMURTREY III JE. 2000. Estimating
corn leaf chlorophyll concentration from leaf and canopy
reflectance. Remote Sens Environ 74: 229–239.
FAGERIA NK, BALIGAR VC, LI YC. 2008 the role of
nutrient efficient plants in improving crop yields in the
twenty first century. J Plant Nutr 31(6):1121–1157.
GHOLIZADEH A, AMIN MSM, ANUAR AR, AIMRUN W.
2009. Evaluation of leaf total nitrogen content for nitrogen
management in a Malaysian paddy field by using soil plant
analysis development chlorophyll meter. Am J Agric Biol
Sci 4 (4): 278–282.
HANSEN PM, SCHJOERRING JK. 2003. Reflectance
measurement of canopy biomass and nitrogen status in
wheat crops using normalized difference vegetation indices
and partial least squares regression. Remote Sens Environ
86:542–553.
Table 2. Regression between vegetation index (VI) and
soil plant analysis development (SPAD) reading at
different growth stages of rice.
Growth
Stage
NDVI GNDVI SAVI
R2
Root
Mean
Square
Error
R2
Root
Mean
Square
Error
R2
Root
Mean
Square
Error
Panicle
initiation 0.78 2.59 0.78 2.60 0.70 3.04
Booting 0.71 2.18 0.75 2.05 0.77 1.94
Heading 0.62 2.03 - - 0.42 2.50
NDVI normalized difference vegetation index, GNDVI green-
normalized difference vegetation index, SAVI – soil adjusted vegetation
index, R
2
– regression
Table 3. Correlation between vegetation index (VI) and
grain yield at different growth stages of rice.
Growth
Stage
Days
After
Planting NDVI GNDVI SAVI
Tillering 51 0.581
*
0.577
*
0.580
*
Panicle
initiation 60 0.859
**
0.857
**
0.803
**
Booting 79 0.915
**
0.940
**
0.939
**
Heading 93 0.642
*
−0.485
n.s.
0.778
**
**
Significant at 0.01.
*
Significant at 0.05.
n.s.
No significant correlation
NDVI – normalized difference vegetation index, GNDVI –
green-normalized difference vegetation index, SAVI – soil
adjusted vegetation index
Table 4. Regression between vegetation index (VI) and
grain yield at various growth stages of rice.
Growth
Stage
NDVI GNDVI SAVI
R
2
Root
Mean
Square
Error
R
2
Root
Mean
Square
Error
R
2
Root
Mean
Square
Error
Panicle
initiation 0.73 3.50 0.73 3.52 0.64 4.07
Booting 0.83 2.76 0.88 2.33 0.88 2.39
Heading 0.41 5.2
NDVI – normalized difference vegetation index, GNDVI – green-
normalized difference vegetation index, SAVI – soil adjusted vegetation
index, R
2
– regression
Table 5. The curve fit estimation regression model between soil plant analysis development (SPAD) reading and
vegetation indices.
Growth
Stage NDVI GNDVI SAVI
Panicle initiation SPAD= 87.36*NDVI-30.19 SPAD= 88.595*GNDVI-30.828 SPAD= 84.615*SAVI-28.20
Booting SPAD= 40.412*NDVI+29.76 SPAD= 46.323*GNDVI+29.33 SPAD= 41.956*SAVI+29.40
Heading SPAD = 52.07*NDVI+26.75 SPAD= 30.918*SAVI+31.03
SPAD – Soil Plant Analysis Development, NDVI – Normalized difference vegetation index, GNDVI – Green normalized difference vegetation index, SAVI –
Soil adjusted vegetation index
Table 6. The curve fit estimation regression model between grain yield and vegetation indices
Growth
Stage NDVI GNDVI SAVI
Panicle initiation Yield= 103.093*NDVI-63.013 Yield= 104.447*GNDVI-63.691 Yield= 98.58*SAVI-59.706
Booting Yield= 72.258*NDVI+4.171 Yield= 83.23*GNDVI+3.360 Yield= 74.086*SAVI+3.692
Heading Yield= 62.694*SAVI+0.213
SPAD – Soil Plant Analysis Development, NDVI – Normalized difference vegetation index, GNDVI – Green normalized difference vegetation index, SAVI –
Soil adjusted vegetation index
The Philippine Agricultural Scientist Vol. 96 No. 1 (March 2013)
Tetracam for Estimation of Nitrogen and Grain Yield M. M. Saberioon et al.
120
HUBER DM, THOMPSON IA. 2007. Nitrogen and plant
disease. In: Datnoff LE, Elmer WH, Huber DM, editors.
Mineral Nutrient and Plant Disease. St. Paul, MN, USA:
The American Phytopathological Society. p. 31–44.
HUETE AR. 1988. A soil vegetation adjusted index (SAVI).
Remote Sens Environ 25 (1988): 295–309.
LAMB DW, BROWN RB. 2001. Remote sensing and mapping
of weeds in crops. J Agric Eng Res 78(2): 117–125.
MOGES SM, RAUN WR, MULLEN RW, FREEMAN KW,
JOHNSON GV, SOLIE JB. 2005. Evaluation of green, red,
and near infrared bands for predicting winter wheat
biomass, nitrogen uptake, and final grain yield. J Plant
Nutr 27(8): 1431–1441.
PONNAMPERUMA FN, DETURCK P. 1993. A review of
fertilization in rice production. Int Rice Comm Newslett
42:1–12.
SHANAHAN JF, SCHEPERS JS, FRANCIS DD, VARVEL
GE, WILHELM WW, TRINGE JS, SCHLEMMER MR,
MAJOR DJ. 2001. Use of remote sensing imagery to
estimate corn grain yield. Agron J 93: 583–589.
SHIBAYAM M, AKIYAMA T. 1989. Estimating grassland
phytomass production with near-infrared and mid-infrared
spectral variables. Remote Sens Environ 30(3): 257–261.
SHOU L, JIA L, CUI Z, CHEN X, ZHANG F. 2007. Using
high-resolution satellite imaging to evaluate nitrogen status
of winter wheat. J Plant Nutr 30(10): 1669–1680.
SWAIN KC, THOMSON HP, JAYASURIYA HPW. 2010.
Adoption of an unmanned helicopter for low altitude
remote sensing to estimate yield and total biomass.
ASABE J 53(1): 21–27.
XUE L, CAO W, LUO W, DAI T, ZHU Y. 2004. Monitoring
leaf nitrogen status in rice with canopy spectral reflectance.
Agron J 96: 135–142.
The Philippine Agricultural Scientist Vol. 96 No. 1 (March 2013)
Tetracam for Estimation of Nitrogen and Grain Yield M. M. Saberioon et al.
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The climate is changing constantly, and this change is affecting millions of people to encounter extreme challenges to health, migration, water security, livelihood security, cultural identity, food security, and many other related risks. Climate change is deeply entangled with global patterns of inequality affecting beyond 375 million people every year with an escalation of 50% as compared to the previous decade. This increase is giving rise to social issues such as poverty, unemployment, unequal opportunities, racism, and malnutrition, which are affecting many people. The investigation and analysis of social issues is an important research theme as it is significant to make people think of ways and approaches for problem solving through critical thinking and mitigation approaches. One of the major effects of climate change is that our social harmony is disturbed, and it is giving space to hostility and suspicion. It has caused large-scale social dissatisfaction and created suffering and misery. In this chapter, we summarized the trepidations of climate change and social concerns that are penetrating in developing countries. The study calls attention to the inevitability to develop and spread evidence-based interventions to combat the risk in the wake of climate change. There is a dire need to promote social cohesion and community resilience to mitigate the possibility of social conflict in changing climate.KeywordsClimate changeSocial impactSocial indicatorsFood securityLivelihood securityMitigationSustainability
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Effective water use depends on judicious application of irrigation at the right amount at the right time and with the right methods. Irrigation scheduling deliberates when to apply, how much to apply, and where to apply in the crop field. Especially, irrigation scheduling is the decision of when and how much water should be applied in field crops. Inefficient water use in poor nations resulted in water losses up to 25%. Inadequate levelled crops and unscheduled irrigation without taking into account the management allowable deficit (MAD) and potential soil moisture deficit (PSMD), and without soil and meteorological requirements, could not provide the exact information of agricultural irrigation necessities. The calculation of crop water requirements and significantly improved water use efficiency may decrease the environmental consequences of watering and increase the resilience of agricultural production by conservative water use applications with proper measuring of soil moisture levels. In this chapter, the concepts of field capacity, management allowable deficit, potential soil moisture deficit, and permanent wilting point are expanded with descriptions. Under water-limiting circumstances, simulation modelling from decision support system for agrotechnology transfer (DSSAT) played a significant role in irrigation scheduling with estimation of possible evaporation. DSSAT determines daily crop water requirements (ETc) and irrigation scheduling based on read-in values with automatic applications based on soil water depletion. Conclusion of study strongly intervened modelling and measuring soil moisture with vital utility in irrigated agriculture and must be used in order to maximize the advantages of a limited irrigation distribution. Several strategies for better water management practices under current climate change scenarios provides irrigation opportunities to meet the water demands for all users in developing countries.KeywordsWater managementIrrigation schedulingSoil moistureManagement allowed deficit (MAD)Field capacityPSMDPermanent wilting pointDSSAT
Thesis
Dans ce travail de thèse, il a constaté que l’étude des technologies numériques dans l’agriculture est récente dans le domaine de l’économie et par un scoping review, il a été identifié certains gaps dont le manque des études empiriques. Ainsi, quatre technologies ont été étudiées : connexion internet, robot de traite, outils d’aide à la décision (OAD) et outils de surveillances électroniques. Dans le secteur du lait, elles augmentent la production mais les effets sont plus importants pour les petites et moyennes exploitations. Plus important encore, les technologies connexion internet et OAD sont bénéfiques à tous les agriculteurs, utilisateurs ou non, puisque grâce à la proximité physique, ils arrivent à capter les effets d’agglomération techniques.Aussi, il a été trouvé qu’il existe un certain effet de rebond dans l’impact des technologies sur la production d’effluent. La contribution de la thèse est tout d’abord,nous avions été le premier, à notre connaissance, à avoir pu estimer ces effets à l’échelle nationale, effectivement les données étant encore très récentes l’appariement de plusieurs sources a été notre premier défi. Ensuite, nous avions appliqué deux nouvelles approches pour estimer les effets d’une utilisation de technologie, le Two-Stage least square (Geraci et al., 2014) et le Coarsening Exact Matching (Iacus et al, 2008) qui promettent des résultats plus pertinents pour notre contexte de donnée en coupe transversale et présentant une endogénéité. Enfin, la dernière contribution de la thèse est d’apporter des recommandations afin de permettre aux politiques publiques de comprendre les effets des nouvelles technologies et promouvoir les meilleures d'entre elles.
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Early information on rice crop yields is essential for production estimation to formulate strategies on food security and rice grain exports in a country. This research aimed to develop a machine learning approach for rice yield forecasting using multi-temporal Moderate Resolution Imaging Spectroradiometer (MODIS) data in Taiwan. We processed the data following three main steps. Firstly, data pre-processing was carried out to reconstruct the smooth time-series Normalized Difference Vegetation Index (NDVI) data for 2000 to 2018, using the empirical mode decomposition (EMD). Secondly, we established rice crop yield models using the random forest algorithm. Then, the datasets from 2000 to 2017 were used for formulating predictive models to forecast rice crop yields in 2018. Thirdly, the robust performance of yield models was evaluated by comparing the predicted results with the official yield statistics. The results showed that the root mean square percentage error (RMSPE), mean absolute percentage error (MAPE), and Willmott’s index of agreement (d) values, achieved for the first crop, were 11.8%, 9.3%, and 0.81, while those for the second crop were 11.2%, 9.1%, and 0.91, respectively. In both cases, these findings were also reaffirmed by a close relationship between these two datasets, with the correlation coefficient (r) values greater than 0.85. The approach followed in the study can be followed elsewhere for rice yield forecasting to address food security concerns.KeywordsMODISNDVIRiceYieldRandom forest algorithm
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Soil-available nutrients (SANs)are essential for crop growth and yield formation. Appropriate variable rate fertilization (VRF) can control SAN at a normal level to avoid unnecessary damage to sustainable production capacity. The precondition of optimizing the application of VRF is obtaining the real-time status of SAN. A new method for SAN estimation has been proposed by integrating modified World Food Studies (WOFOST) and time-series satellite remote sensing (RS) data. This method can provide field scale SAN estimations with high accuracy. However, the estimation accuracy at a subfield scale was low for VRF application because of the poor spatial resolution of common satellite imagery. In this letter, the subfield SAN estimations were optimized to ensure the VRF value. Time-series multispectral images acquired by an unmanned aerial vehicle (UAV) were used to replace common satellite data, and the SAN values for haplic phaeozem in selected spring maize plot in Hongxing Farm (48°09ʹ N, 127°03ʹ E) were estimated. Based on the field SAN data, the estimation accuracies using satellite data and UAV data were analyzed. The results show that the UAV data improved SAN estimations at the subfield scale).
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Presently normalized difference vegetative indexes (NDVI) based on red (RNDVI) or green (GNDVI) reflectance are commonly used to evaluate plant health, biomass, and nutrient content. This study was conducted to determine which of these two indexes is more correlated with biomass, forage nitrogen (N) uptake, and final grain yield of winter wheat. Three experimental sites were established in Oklahoma in the fall of 2001 at Stillwater. Spectral reflectance measurements were taken at Feekes growth stage 4, 6, and 10.5 followed by winter wheat forage harvest. When evaluated at specific stages of growth, RNDVI was consistently more highly correlated with biomass than GNDVI. Green NDVI and RNDVI were more highly correlated with forage N uptake than with dry biomass at each stage of growth, but neither index appeared to have a comparative advantage over the other. Both indexes were highly correlated with final grain yield and grain N uptake across all locations. Neither index appeared to have a sizeable advantage over the other, suggesting that either will perform equally well when predicting forage N uptake, grain yield, and grain N uptake in winter wheat. Red NDVI does appear to be a better predictor of forage biomass, specifically at earlier stages of growth. Contribution of Okla. Agric. Exp. Stn.
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Nitrogen (N) applications often increase crop yields significantly, but N needs vary spatially across fields and landscapes. The color of the wheat plant is sensitive to N status and may provide a means to accurately predict N fertilizer rates matching spatial variability. Previous researches have reported that remote sensing may contribute to N management decisions by collecting spatially dense information. The objective of this study was to determine the feasibility of using high-resolution satellite imaging for evaluating N status of winter wheat in the North China Plain. High-resolution images from a QuickBird satellite were taken on April 1, 2002 at booting stage of wheat with multi-spectral wavelengths (blue, green, red, and near-infrared). Correlation analyses indicated that all the broadband indices derived from the satellite images correlated well with sap nitrate concentration, SPAD readings, total N concentration, and aboveground biomass. The individual band reflectance values R, G, B correlated well with sap nitrate concentration, SPAD readings, total N concentration, and aboveground biomass. These results demonstrated the potential of using new generation high-resolution satellite imaging for large area wheat N status diagnosis.
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Farmers must balance the competing goals of supplying adequate N for their crops while minimizing N losses to the environment. To characterize the spatial variability of N over large fields, traditional methods (soil testing, plant tissue analysis, and chlorophyll meters) require many point samples. Because of the close link between leaf chlorophyll and leaf N concentration, remote sensing techniques have the potential to evaluate the N variability over large fields quickly. Our objectives were to (1) select wavelengths sensitive to leaf chlorophyll concentration, (2) simulate canopy reflectance using a radiative transfer model, and (3) propose a strategy for detecting leaf chlorophyll status of plants using remotely sensed data. A wide range of leaf chlorophyll levels was established in field-grown corn (Zea mays L.) with the application of 8 N levels: 0%, 12.5%, 25%, 50%, 75%, 100%, 125%, and 150% of the recommended rate. Reflectance and transmittance spectra of fully expanded upper leaves were acquired over the 400-nm to 1,000-nm wavelength range shortly after anthesis with a spectroradiometer and integrating sphere. Broad-band differences in leaf spectra were observed near 550 nm, 715 nm, and >750 nm. Crop canopy reflectance was simulated using the SAIL (Scattering by Arbitrarily Inclined Leaves) canopy reflectance model for a wide range of background reflectances, leaf area indices (LAI), and leaf chlorophyll concentrations. Variations in background reflectance and LAI confounded the detection of the relatively subtle differences in canopy reflectance due to changes in leaf chlorophyll concentration. Spectral vegetation indices that combined near-infrared reflectance and red reflectance (e.g., OSAVI and NIR/Red) minimized contributions of background reflectance, while spectral vegetation indices that combined reflectances of near-infrared and other visible bands (MCARI and NIR/Green) were responsive to both leaf chlorophyll concentrations and background reflectance. Pairs of these spectral vegetation indices plotted together produced isolines of leaf chlorophyll concentrations. The slopes of these isolines were linearly related to leaf chlorophyll concentration. A limited test with measured canopy reflectance and leaf chlorophyll data confirmed these results. The characterization of leaf chlorophyll concentrations at the field scale without the confounding problem of background reflectance and LAI variability holds promise as a valuable aid for decision making in managing N applications.
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Airborne remote-sensing has been identified worldwide as a promising technique for identifying and mapping weeds in crops, and potentially offers a solution to the current logjam in precision weed management: namely, the ability to generate timely and accurate weed maps. One of the main advantages of remote-sensing is that synoptic weed data can be acquired virtually instantaneously (within the field of view of the sensor), and a weed map generated within hours of data acquisition. However, because little information is available concerning the scale at which weeds should be managed within fields, the sensing and mapping technology has tended to dictate the resolution at which weeds must be mapped. This paper summarizes the work completed to date to investigate the use of airborne remote-sensing for weed mapping in crops, and discusses application of the technology in precision weed management practices.
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Airborne remote-sensing has been identified worldwide as a promising technique for identifying and mapping weeds in crops, and potentially offers a solution to the current logjam in precision weed management: namely, the ability to generate timely and accurate weed maps. One of the main advantages of remote-sensing is that synoptic weed data can be acquired virtually instantaneously (within the field of view of the sensor), and a weed map generated within hours of data acquisition. However, because little information is available concerning the scale at which weeds should be managed within fields, the sensing and mapping technology has tended to dictate the resolution at which weeds must be mapped. This paper summarizes the work completed to date to investigate the use of airborne remote-sensing for weed mapping in crops, and discusses application of the technology in precision weed management practices.
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The determination of sample size before collecting experimental data is fundamental to obtain reliable estimates of variables describing agroecosystem development. In order to analyze the influence of experimental factors (artificially-induced variability) on rice sample size, an experiment was carried out in 2004 in northern Italy. In particular, different sample size determinations were carried out for different fertilization levels, varieties (Indica and Japonica type), development stages, sowing techniques and typologies of the sampling unit. The obtained sample sizes were compared to investigate the influence of each factor, keeping the others constant (for example, we have compared the sample sizes computed for different fertilization levels within the same variety, the same phenological stage and the same sampling unit). Since original data were often not normally distributed and the variances of the original samples were not homogeneous, a new approach for sample size determination based on a visual evolution of the jackknife was preferred to classical techniques.Results (expressed as number of plants) showed that (i) sample sizes computed in an early phenological stage (between 21 and 27) are higher than those calculated for later stages (15–21); (ii) fertilization hides soil N content variability with the consequence that larger sample sizes are required for unfertilized plots (21–27) compared to fertilized plots (15–27) and (iii) for the early sampling, the Indica type variety required larger sample size (always 27) with respect to the Japonica type variety (21–24). For row-seeded rice, the number of plants instead of linear centimeters as the sampling unit led to lower sample sizes (18–27 versus 30–33). These results highlight the influence of experimental factors and development stage on within-plot variability, and therefore the importance of preliminary samplings for sample size determination.
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Near-infrared and mid-infrared spectroradiometric reflectance variables were studied for estimating grass phytomass production within grass plots fertilized with five rates of nitrogen. Nine difference vegetation indices, five single wavelengths, and one waveband were correlated with phytomass. Among the 15 variables studied, TM5 (1550–1750 nm), reflectance at the 1100 nm (R1100), 1650 nm (R1650), and 2200 nm (R2200) wavelengths, and five indices [R1100–R1200, R1100–R1650, (R1100–R1300)-TM5, R1100–R2200, and R1200–R1650] had significant coefficients of determination (r2) ranging from 0.83 to 0.92. The spectral variables involving the mid-infrared wavelengths generally yielded the highest r2 coefficients. These results suggest the potential for estimating grass phytomass production over large and inaccesible rangeland areas using Thematic Mapper (TM5 and TM7) satellite data.