1. Introduction
Rice is a staple food for over half the world’s population and rice consumption is increasing with population growth [
1]. Approximately, 75% of the world’s rice production is derived from irrigated lowland fields, which receive some 34–43% of the total world’s irrigation water [
2]. However, water resources for the agricultural sector have been decreasing along with a rapid increase in non-agricultural demands for water and global climate change [
3]. Therefore, a key strategy for sustainable rice production would be developing water-saving rice cultivation systems.
Alternate wetting and drying (AWD) is an irrigation practice that can reduce water consumption in rice fields without sacrificing yield. Its use has been proposed and tested in many regions [
4,
5,
6,
7,
8,
9]; however, the effect of AWD on rice yield has produced inconsistent results. For instance, some studies on rice reported higher grain yields under AWD than under continuously flooded conditions [
10,
11,
12,
13], while others reported AWD to decrease grain yields [
14,
15,
16]. The conflicting results of these reports suggest that yield responses under AWD may depend on the cultivation environment and rice variety. Consequently, for successful local implementations of AWD, reliable validation and adaptation trials are needed.
In Kenya, the demand for rice is increasing due to changes in eating habits and increasing urban population [
17]. In 2017, Kenya imported 634,852 t of rice, costing the country 264 million USD [
18]. Thus, boosting rice production is an urgent issue for food security in the country. In Kenya, approximately 80% of rice is produced in irrigated lowland fields [
19,
20]. The Mwea Irrigation Scheme, which is located 100 km northeast of Nairobi at the southern foot of Mt. Kenya, is the largest rice-growing irrigation scheme in Kenya, covering 9000 ha and accounting for 78% of the irrigated paddy fields [
20]. Hence, Mwea would be one of the most important areas for increasing rice production in Kenya.
The location of Mwea (near the equator, at approximately 1200 m above sea level) ensures high levels of radiation—typical for tropical regions—and large day–night temperature differences that are typical for highlands. The main rice variety grown in Mwea is Basmati 370, a lowland variety favored by consumers, especially in the urban areas, for its aroma and high cooking quality [
21]. Most farmers in Mwea grow rice once a year, sowing between July and August and harvesting between December and January [
21,
22,
23]. However, as shortage of irrigation water is often a problem in Mwea, some farmers may start sowing around September-November, depending on the availability of irrigation water [
21]. Due to the high-altitude location of Mwea, the air temperature can sometimes drop below 18 °C during the growing periods, which can reduce filled-grain ratio in Basmati 370 [
24,
25]. In order to improve the rice productivity, this problem needs to be addressed.
Under such cultivation environment, AWD has been introduced as a part of the technology packages for rice cultivation, such as System of Rice Intensification (SRI) and Water Saving Rice Culture (WSRC) [
17,
26]. These technology packages improved rice grain yield compared to conventional continuous flooding (CF) cultivation [
17,
27]. However, the factors responsible for the yield improvement have not been clarified. Moreover, SRI and WSRC are technology packages that combine AWD and other cultivation technologies, so it cannot be said that AWD itself was evaluated.
Clarifying whether the yield response under AWD depends on the cultivation environment and rice variety will provide useful information for developing a water management strategy based on the actual condition. In this study, we investigated the effects of AWD on rice growth and yield over four cropping seasons under the unique cultivation environment in the tropical highlands and analyzed the reasons behind the differential effects of AWD on rice yields across these cropping seasons.
2. Materials and Methods
The study was conducted at the experimental field of the Kenya Agricultural and Livestock Research Organization (KALRO), Mwea Centre, Kerugoya County, Kenya (0°39′ S, 37°22′ E), at an elevation of 1162 m above sea level, during the rice growing season, from 2014 to 2017. The soil of the experimental field was Nitisol. At the start of the experiment, it contained 3.3% total C, 0.25% total N (C/N coda), 753 mg kg−1 available phosphorous pentoxide (Bray II), 0.35 cmol (+) kg−1 exchangeable K, determined after extraction with 1 M ammonium acetate (pH 7.0), 0.52 mg kg−1 Cu, 188 mg kg−1 Fe, 0.19 mg kg−1 Zn, and 43 mg kg−1 Mn. Cu, Fe, Zn, and Mn were extracted by 0.1 N HCl and determined by inductively coupled plasma-atomic emission spectroscopy (ICPE-9000; Shimadzu Co. Ltd., Kyoto, Japan). Soil pH (H2O) was 5.24. Temperature, rainfall, and solar radiation were recorded by a weather station (Weather Bucket; Agriweather Inc., Sapporo, Japan) located at the research farm.
The experiments comprised two water management regimes: CF and AWD. The two treatments were laid out in randomized block designs—the size of each plot was 4 m × 7 m in all years—in three replications. To prevent the movement of water from CF to AWD, the plots were separated by bands (approx. 1 m width) and enclosed by buried PVC sheets (Aze sheet; Iwatani Corporation, Osaka, Japan, 0.5 mm thick, and 45 cm high). In the AWD plots, soil was maintained with shallow water depth, and irrigation was stopped after the first application of chemical fertilizer, at 7−10 days after transplanting (DAT). In the AWD plots, irrigation water was applied approximately 5 cm above the soil surface when the perched water table reached −20 cm. This cycle was repeated until the late-ripening stage. In the CF plots, water depth was maintained at approximately 5 cm above the soil surface until the late-ripening stage. Approximately 10 d before harvesting, irrigation water was drained in both water treatments. The depth of the perched water tables was measured using a plastic pipe (diameter 20 cm) with numerous small holes inserted in the soil. Soil water potential at 20 cm of soil depth was also measured using a tensiometer (pF meter DIK8333; Daiki Rika Kogyo Co. Ltd., Saitama, Japan). Soil electrical conductivity (EC) and temperature were measured weekly (at an approximately 5 cm soil depth) from transplanting to heading time, using an EC meter (FieldScout Direct Soil EC Meter 2265FSTP; Spectrum Technologies, Inc., Aurora, IL, USA). Soil pH and oxidation-reduction potential (ORP) were also measured weekly (at the same soil depth) using a pH meter (FieldScout SoilStik pH Meter 2105; Spectrum Technologies, Inc.), and an ORP meter (ORP Meter 2010; Spectrum Technologies, Inc.), respectively.
The rice variety used in the study was Basmati 370, which is widely grown in the Mwea region in Kenya. In Mwea, farmers usually start sowing in July according to the allocation of irrigation water [
22,
23]. The peak season of sowing is from July to August. However, depending on the availability of irrigation water, the sowing time is often delayed by 1–2 months [
21]. Therefore, the trials were conducted with early sowing in 2015 and 2017 and late sowing in 2014 and 2016 to replicate the actual sowing practices of farmers. Seeds of Basmati 370 were soaked in water for two days and sowed in a seedbed. Sowing was conducted on 25 September, 26 August, 17 September, and 9 July in 2014, 2015, 2016, and 2017, respectively. In all plots, 15 t ha
−1 of manure, made from cow dung, was applied in the soil before transplanting. The grain yields of this rice variety sown between July and February were reported to be comparable in the Mwea region [
23]. Seedlings were manually transplanted, with one seedling per hill, approximately 14 days after sowing. The transplanting density was 30 cm between rows and 30 cm between plants in a row. Seven DAT, 25 kg ha
−1 of N, P, and K was applied in the form of NPK (17:17:17), with an additional 25 kg ha
−1 of N fertilizer applied 21 and 54 DAT in the form of ammonium sulfate.
Plant growth measurements were performed on five randomly selected plants from each plot. Number of tillers and plant length were regularly measured from tillering to heading stage. The Soil Plant Analysis Development (SPAD) values for leaf chlorophyll content were regularly measured with a SPAD meter (SPAD-502 plus; Konica Minolta Inc., Tokyo, Japan). Heading date was defined as the point, where more than half of panicles had emerged from the plants’ sheath. Plants were then harvested approximately 40 days after heading. In 2014, we selected three portions of 1.44 m2 from each plot and the above-ground part was harvested manually. In 2015, 2016, and 2017, 1 m2 of the above-ground part was harvested from each plot. After measuring the number of panicles, grains were manually removed from the panicle and dried in the open air. The harvested grains were placed in fresh water; subsequently, the grains that floated were defined as unfilled grains (immature grains + sterile grains), whereas those that sank grains were defined as filled grains. Both filled and unfilled grains were dried in the air and counted. Filled grain ratio was calculated as follows: filled grains (sunken grains)/total grains × 100. The weight of 1000-grain was measured for filled grains, and grain moisture content of the grains was measured by a grain moisture tester (Riceter f512; KETT Electric Laboratory, Tokyo, Japan). Rice straws were dried in an oven at 80 °C for more than three days, and their dry matter weights were determined. Harvest index (HI) was calculated by dividing the grain weight by the total above-ground biomass.
Analysis of variance (ANOVA) was performed using Statistical Analysis System (version 9.0) (SAS Institute Inc., Cary, NC, USA) to assess the main effects of cultivation year, water treatment, and their interactions. Means of growth and yield parameters were separated using the least significant difference test at p < 0.05 in Statistical Analysis System (version 9.0) (SAS Institute Inc., Cary, NC, USA).
4. Discussion
The results of our trials revealed that AWD had negative effects on the above-ground biomass (
Table 4). In terms of vegetative growth, Basmati 370—being a lowland variety—is considered to have been adapted to CF rather than AWD conditions. However, the grain yield responses to the water management varied depending on the year of cultivation (
Table 4). Grain yield was affected by water management in all years, but the direction of the AWD-induced effect was completely different depending on the year. In 2015, AWD had a negative effect on grain yield, whereas it had a positive effect in 2016. In 2014 and 2017, AWD did not change grain yield. Thus, even though AWD tended to reduce dry matter production of this lowland rice variety in the Mwea region, the effect of AWD on grain yield was not consistent.
We have discussed the causes for the differential effect of AWD on grain yield. In general, under non-stressed conditions, grain yield of rice is mainly determined by above-ground biomass as source size, and number of grains per square meter as sink size [
28,
29]. In our study, the grain yield was determined by the source and sink size only in 2015 and 2017 (
Table 5). The main determinant of grain yield in 2014 and 2016 was filled grain ratio, which was affected by the cultivation environment rather than the source and sink size.
Under unfavorable weather conditions, such as low temperature, the HI, which is a measure of the distribution efficiency of photosynthetic assimilates to grains, is strongly and positively correlated with grain yield [
30]. The results of this experiment suggested that low temperature during the panicle initiation stage and ripening stage in 2014 and 2016 inhibited translocation and resulted in a lower filled grain ratio (
Table 4,
Table 5 and
Table 6).
Njinju et al. [
24] reported a reduction in the filled grain ratio of Basmati 370 due to inhibition of translocation under low temperature conditions in Mwea. In our trial, the decrease in filled grain ratio was not attributed to the average of mean temperatures between 14 days before heading and heading, but to the average of minimum temperatures recorded during the same period. Farrell et al. [
31] reported that sharp drops in the nighttime temperatures can cause sterility, and even if the mean temperatures stay high, the effects of extremely low minimum temperatures will be irreversible. In 2014 and 2016, night temperatures were very low (14.2–15.2 °C), and the differences between the maximum and the minimum temperature during the period from 14 days before heading to heading were large (12.2–15.1 °C) (
Table 6). Thus, the decrease in filled grain ratio may be due to the occurrence of sterility caused by the very low minimum temperature (
Figure 3). However, the ripening process may also have been affected, because there was a positive and significant correlation between filled grain ratio and average minimum temperature for the period from heading to 14 days after heading under CF. These results suggested that the inhibition of translocation under CF in 2014 and 2016 was due to sterility at both flowering and ripening stages after heading.
In 2014 and 2016, the effect of low temperature on grain filling was more severe under CF than under AWD (
Table 4). This demonstrates the mitigation effect of AWD on the decline in filled grain ratio when rice is exposed to low temperature during the reproductive and ripening stages. Under CF, the ORP decreased, as the paddy soil was under reduced condition (
Table 1). Zhang et al. [
32] reported that decreased root activity caused by reduced soil promotes cold-induced damage in rice. Under AWD conditions, rice can maintain high root activity [
13,
33]. Therefore, it was suggested that the mitigation effect of AWD on the decline in grain filling was related to the maintenance of higher root activity under aerobic conditions. In 2015 and 2017, rice was not exposed to low temperature during reproductive and ripening stages (
Table 6). Hence, filled grain ratio did not decrease even under CF (
Table 4). Accordingly, there was no mitigation effect of AWD on the decline in grain filling in 2015 and 2017. In the present study, Basmati 370, which is susceptible to cold stress [
25], was studied for four years. However, large differences in various varieties have been observed in previous cold tolerance evaluations conducted in Mwea [
25]. Therefore, further studies are needed to evaluate and validate the effect of AWD in tropical highlands using varieties with different cold tolerance abilities.
Generally, soil water potential in AWD should be kept higher than −30 kPa to avoid reduction of grain yield caused by water stress [
34]. In our trial, soil water potential for the AWD plots did not drop below −10 kPa all year (
Figure 2). Thus, it can be said that there was no severe water stress caused by the AWD. Total rainfall during the 2015 growth period was higher than 2014, 2016, and 2017, however, this difference in the annual precipitation rate should not have affected rice growth and yield, as the trials were conducted under irrigated paddy fields. Since variations in the solar radiation were relatively constant, this factor is unlikely to have accounted for the observed differences in yields under CF and AWD (
Table 1). Similarly, differences in soil temperature, EC, and pH, between CF and AWD were equally minor, and therefore their influence on the yield responses can be considered negligible.