Abstract:
Climate variability and change are currently significant global issues. Certainly, understanding
the observed and projected climatic change, can serve as an indispensable tool in devising
effective strategic frameworks to enhancing the socioeconomic welfare of a significant cohort of
agricultural practitioners. The objective of the study was to explore past and projected climate
variability and trend, assessing and quantifying the loss of nitrogen as result of climate change
and its impact on sorghum yield as well as to determine optimum nitrogen fertilizer for sorghum
using CERES-Sorghum model in semi-arid Rift Valley areas of Ethiopia. To achieve this
objective the study mainly focused on the four components; in understand past climate
variability and trends, projected climate change and extremes trends, projected climate change
impact on nitrogen loss and its impact on sorghum yield and nitrogen optimization using
CERES-sorghum under observed climate condition. The primary approach followed was
collecting long term (1981-2021) daily rainfall and air temperature for eleven stations from
EMI. Three and two stations were, respectively, from NRVE and ERVE while six of the stations
were from the CRV. The variability of rainfall and temperature over the past four decades were
assessed using mean, CV, and SAI. Trend analysis was performed following Mann–Kendall test
and Sen’s slope estimator. The start and end of the growing season, length of the growing
period, and dry spells were analyzed for the stations. The second approach was that weather
data for 11 stations were generated using AgMIP-5 technique for RCP 4.5 and 8.5 and for the
period of 2050s and 2080s.MAKESENS was employed for the detection of trend of extreme
indices. Instat v3.37 was used for the analysis of start, end, and length of growth season. The
third approach was to quantify the loss of nitrogen from the sorghum treated with level of
nitrogen with three time of deliver and its impact on sorghum yield and the final approach
nitrogen fertilizer optimization using CERES-sorghum model in observed climate condition for
the sorghum at Melkassa, Mieso and Kobo areas. The months of July, August, and September
were the primary contributors to the overall annual rainfall at all the sites studied. Conversely,
December, January, November, and February exhibited the lowest levels of rainfall across the
locations. In comparison to the longest rainy period, the short rainy period contributed less
rainfall to the annual amount and was also associated with high inter-seasonal variability. The
xix
range of minimum and maximum air temperatures experienced during the short rainy season
varied between 12.24-19.4 oC and 27.7- 36̊ oC, whereas during main rainy season ranged from
11.9 -20.1oC and 24.5-33.4 oC respectively in the studied regions. The trend of rainfall in months
of March and April showed a decline in range of 0.075 -1.78 mmyr-1,0.06-0.97mmyr-1 and 0.11 -
0.84mmyr-1in the CRV, ERVE, and NRVE, respectively. The non-significantly (P ≤0.05)
increasing amounts of rainfall in the months of June in range s of 0.14-1.17mmyr-1and
September month to increase in range of 0.05-0.81mmyr-1. where June as the start and
September as end of the season, respectively, in the studied regions. Rainfall decreases from
0.31–2.76 mmyr-1and increases to a 0.19–5.12 mmyr-1 in the short and main rainy seasons
respectively except decrease in rainfall in the main rainy season in Dhera, Matahara, and Melka
Werer in CRV. The maximum and minimum air temperatures in the month of March to May
show increasing trends, while from June to September there were mixed trends in the studied
sites. The start of the season throughout the main growing period varies between 177 and 196
DOY. Conversely, the end of the season spans from 274 to 285. Similarly, the length of growing
period in the studied regions spans from 78 to 143 days, and the number of rainy days during the
main growing season ranges from 67 to 110 days. The projected annual minimum air
temperatures in CRV, ERVE and NRVE could increase by 1.9 ̊ C (2050s) and 2.6 ̊ C (2080s),
1.8 ̊ C (2050s) and 2.5 ̊ C (2080s) and 1.88 ̊ C (2050s) and 2.69 ̊ C (2080s) respectively under RCP
4.5. However, at the same location, it is projected to increase in both time frames (2050s and
2080s) in all studied sites under RCP 8.5. The annual maximum air temperature, projected
under RCP 4.5 in the CRV, ERV, and NRVE will increase by 1.59 ̊ C (2050s) and
2.18°C(2080s),1.42 ̊ C (2050s) and 2.08 ̊ C(2080s) and 1.46 ̊ C (2050s) and 2.09 ̊ C(2080s)
respectively. However, at same regions, under the RCP 8.5 it rise in both periods (2050s and
2080s). This will be convoy with increase of the hot and cold extremes’ indices in regions. The
change of annual rainfall decrease insignificantly by 0.6-5.5% and 0.32% and increase 0.85–
12.3% and 22.3% in half of the stations located in CRV and ERVE, whereas, in NRVE will
increase 6.1-14.6% under RCP 4.5 in all stations in 2050s.Though the annual rainfall under
RCP 4.5 in 2080s will decline in range of 0.67–10.1%,3.12–4.5% and 0.9-4.6% at CRV, ERVE
and NRVE respectively. In most of the location in CRV and ERVE stations growing season
rainfall decline from 1.45% to 53.8%.and 0.8 to 8.8%. Whereas, in NRVE will increase in 9.2 to
19% under RCP 4.5 in period of 2050. The CERES-Sorghum model coupled in DSSAT -CSM
calibrated using five years (2010–2016) and evaluated with six years (2017–2022) experimental
xx
data of days to anthesis and physiological maturity, grain yield, LAI, and biomass for Melkassa,
Mieso and Kobo. The projected SNR is expected to increase from 1 to 36.7% in the 2050s and 1
to 43.3% in the 2080s under RCP 4.5. Under RCP 8.5, the SNR is expected to increase in range
of 1% to 53.2% in the 2050s and in the 2080 in range of 2.4 to 63.9% . Under RCP4.5, the
projected N2O emission will rise in the range of 0.39% to 13.5% in the 2050s and in 2080s and
decline at Kobo by 2.8% (2050) and 16.2% (2080). Under RCP 8.5, the projected N2O emission
will rise in Melkassa and Mieso but it will decline at Kobo site in the 2050s and 2080s. Under
RCP 8.5 in both time frames, the N-leaching is projected to increase at N application to
sorghum.In general, the lowest SNR, N2O emission and N-leaching in both time frames and
scenarios is projected to be the N fertilizer application rate of 46 N kg ha–1.The projected
decrease in sorghum grain yield is in the range of 6.8 to 11.9% in the 2050s and by 9.45
to17,8% in the 2080s under RCP 4.5. However, under RCP 8.5, projected decrease in sorghum
grain yield is in the range of 7.9 to 17.7% in the 2050s and in the range of 17.3 to 24.3% in the
2080. Therefore, to reduce the risk that may arise because of climate change and its impact on
the environment, sorghum producers should integrate cultivation of the crop with soil moisture
conservation and nutrient and water use efficient genotypesAt the site under study, nitrogen
fertilizer had a significant impact on the mean simulated sorghum grain yield, biomass yield,
harvest index, and NUE of the CERES sorghum model. Consequently, the EONR rates at the
Mieso in ERVE, Kobo in NRVE, and Melkassa in CRV were 29, 34, and 30 N kg N ha–1. These
rates of nitrogen fertilizer the most cost-effective and environmentally optimal recommendations
because of the package availability and the negligible difference between EONR and 46 kg N ha–
1 at three application times: a quarter at planting, half in the mid of the growing season, and a
quarter at the booting stage