1. Introduction
Rice (
Oryza sativa L.), widely farmed all around the world, is an important cereal crop for the majority of the human population worldwide, as a staple food [
1,
2,
3,
4]. Previous studies showed that rice provides 23 to 50% of total calories for almost half of the global population [
5,
6]. Hence paddy cultivation is crucial in the fight against food insecurity and farmer poverty and a downward trend in rice-growing productivity would undermine global food security [
7,
8]. According to Saha
, et al. [
9], rice is called “Global Grain” due to its importance as a staple food for over half of the world's population. In the same way, in the face of rising population growth, climate change, changing food habits and various conflicts, rice yields need to be improved to meet future food demand [
4]. Unfortunately, the increase in yields has not been significant enough to meet the ever-increasing global demand for rice, due to a number of constraints [
7]. Notably, declining and stagnating yields are the main threats to rice cultivation [
3,
10]. Labor shortages, water scarcity, higher rice production cost and resource degradation, including multiple nutrient deficiencies, soil salinity and groundwater depletion are constraints to sustainable rice production [
9,
10,
11]. In the same way, climate change, abiotic stresses, water crisis, energy crisis, low nitrogen use efficiency, increasing micronutrient deficiencies, increasing labor costs, decreasing labor availability, low soil fertility, less efficient management of crops, soil and water and increasing methane emissions are further threats to rice farming [
3,
8,
12].
Rice cultivation, the most water consumer crop, is highly sensitive to water stress due to its high water requirements [
2,
3,
13]. According to Nawaz,
et al. [
3], flood-grown rice accounted for over 75% of worldwide production.. Besides, Fu
, et al. [
14] added paddy production required not only high water usage, but also much fertilizer. Consequently, irrational water and fertilizer applications are sources of environmental problems. Paddy farmers think that more nitrogen fertilizer improves yields [
15]. However, Fu,
et al. [
14] argued that rice production contributes to the pollution of surface and groundwater through the leaching and runoff of nitrogen and phosphorus. Previous studies found that frequent irrigation and excessive fertilization in rice cultivation caused losses of nitrogen and phosphorus [
16,
17]. In China, annual runoff losses of nitrogen and phosphorus from rice fields were estimated at 272.6 ± 101.2 Gg/yr
-1 and 17.0 ± 6.4 Gg/yr
-1 respectively. In the same way, Ibrahim,
et al. [
12] revealed over the span of thirty years (1990–2020), that the gap between potential yields and paddy yields obtained by rice producers remains high due to poor water and fertilizer management. Alam,
et al. [
15] explained that nitrogen use efficiency (NUE) in rice cultivation is 20-40%, with a large unused portion ranging from 60-80% contributing to the degradation of soil, water and air quality.
To reduce the problems, several alternative solutions were proposed for sustainable rice farming. According to Shekhawat,
et al. [
8], the paddy production constraints led to a paradigm shift in the agronomic management of rice-growing practices. The application of shallow-wet irrigation and innovative irrigation technologies would contribute to mitigate the fertilizer losses and hence reduce pollution in rice-growing areas [
18]. A number of water management strategies at different scales are proposed and implemented [
16]. Previous studies showed that compared to continuously flooded irrigation, water saving-irrigation practices such as alternate wetting and drying can reduce irrigation water and fertilizer losses through runoff and leaching [
19,
20]. Liu,
et al. [
16] demonstrated that efficient irrigation water management combined with good agricultural practices such as optimizing fertilization increased water use efficiency and reduced diffuse nitrogen and phosphorus pollution. Optimum water management at field level is the most effective method of reducing nitrogen and phosphorus losses, compared with efficient fertilization management [
18]. An integrated soil, crop and fertilizer management strategy would be an effective approach to improving nitrogen use efficiency and, consequently, significantly reducing nitrogen losses by 2030 and minimize adverse environmental issues [
15]. Ladha,
et al. [
7] argued that management practices combined with regular improved cultivar replacement enabled annual production to be maintained at a sustainable level. According to Jin,
et al. [
13], water-saving practices compared to continuously flooded practice, can increase denitrification loss. In addition, conservation rice growing, including soil and water conservation technologies, such as transplanting, zero tillage and efficient application of water, use of organic and inorganic fertilizers and chemicals, would be a key asset for sustainable rice production [
11,
15,
21].
Similarly, good farming practices as incorporation of rice straw residues reduce nitrogen leaching losses through microbial nitrogen immobilization, due to the high C/N ratio [
17,
22]. In the same way, the creation of new rice varieties that are less water-demanding, short-cycle and stress-tolerant offers an alternative for optimal water management [
11]. In the Sahel, the decision-support tools are used for agronomic management (nutrient, weed and integrated rice crop management practices) and water management practices (salinity-control technologies, water-saving technologies) [
12]. Unfortunately, even though farmers have some knowledge about applying fertilizer and fertilizer rates, land preparation, using improved varieties, pests and diseases management, market information, and storage and processing food, most rice farmers lack knowledge of irrigation water management [
23].
In addition, Ibrahim,
et al. [
12] showed that previous research has focused little on plot-level practices and the sustainability of rice-growing systems. For this reason, Ijachi,
et al. [
5] recommended training of farmers on soil and water management and climate friendly practices that mitigate climate variability in rice production. Ismael
, et al. [
24] also, suggested small-holder farmers need more assistance and technical support to identify and adopt more productive and less costly Rice Farming Systems. For sustainable rice production, we need to identify specific critical points in agronomic and water management in irrigation schemes, by assessing rice growers' perception, for future research.
3. Results
3.1. Respondents' Socio-Economic Characteristics
The socio-economic characteristics of rice farmers are shown in
Table 1. The results showed that female rice growers accounted for half of all rice growers. The average age of rice farmers was 44.5 years, with 7% under 27 and 13% over 58. Approximately, less than 6% of rice farmers were single, compared with over 85% married. More than two-thirds of the rice growers surveyed had a primary or secondary education (Primary & JHS) with rates of illiterates and university graduates of 19% and 4% respectively. Average experience in irrigated rice farming is 9 years, with around 40% of farmers having less than 5 years' experience and 20% having more than 15 years. Many rice growers, i.e. 65%, used rented plots, compared with 21% who had their own or family land. Over 80% of rice growers were members of agricultural cooperatives, while 62% were producers whose only income was from farming. Trade, handicrafts and livestock farming were the main sources of income, in ascending order, in addition to rice production. Agricultural credit was accessed to over 64% of rice growers. The proportion of farmers using sharecroppers was 86%, while 14% used family labor. The majority of rice growers (80.9%) had a single plot on the irrigated fields, versus 19.1% who had more than two plots (
Figure 3).
Fewer growers (27%) stocked up on rice for the lean season than those who sold immediately at harvest (62%). Rice growers representing 40% sold their paddy at harvest for cash needs (10.8%), repayment of agricultural credit (27.3%) or to honor market contracts (1.8%) (
Figure 4). Over half of producers (53%) sold their harvest in the form of white rice, as opposed to 47% who sold paddy immediately. For 63% of producers and 37% of rice growers, the market was available, and for those who responded (54%), it was mainly Aggregators (32.7%), traders (18%) and households (3.2%) before production.
3.2. Agronomic Practices in Irrigation Schemes
3.2.1. Training Attended in Rice Production
Survey results showed that 61% of rice growers had received training in rice production, whereas 39% had not (
Figure 5). The training sessions included composting, mineral fertilization, economic profitability and rice seed production. The rate of female and male rice farmers trained was 53% and 65% respectively. Nevertheless, the Pearson test showed that the number of women trained was significantly higher than the number of men, at the 5% level (p-value = 0.01138).
3.2.3. Soil Preparation
To clear the plots, almost all (96%) of the growers applied chemical products, half of whom, in addition to herbicides, combined mechanical methods to keep the plots perfectly cleared brush (
Figure 6). The choice of clearing method was influenced by a number of socio-economic characteristics. Access to agricultural credit significantly affected the clearing method at the 5% level (p-value = 0.033447). Indeed, 52% of non-credited farmers opted for chemical clearing only, compared with 36% of credited farmers, while 60% of credited rice farmers opted for combined mechanical and chemical clearing, vs. 43% of non-credited farmers. This means that rice growers with financial resources requested mechanical land clearing following the chemical herbicides treatment. The farmer's experience in irrigated rice growing also had an impact on the clearing method at the 5% significance level (p-value = 0.002475). Approximately, more than 52% of farmers with 11 - 15 years’ experience chose chemical land clearing only, while 53% of farmers with above 15 years’ experience and 52% of farmers with Below 5 years’ experience adopted combined chemical and mechanical land clearing. The level of education also affected the adoption of a particular type of land clearing (p-value = 0.017302). More than half of JHS (51.8%) and SHS (50.1%) farmers preferred combined mechanical and chemical land clearing, while 60% of university rice growers opted for chemical land clearing only. However, no preference was shown by illiterate and primary-level farmers.
Around 55% of rice growers aged between 38-47 years and 48 - 57 years used chemical clearing only, while 53% of growers aged 18 - 27 years, 63% of growers aged 58 - 67 years and 38-63% of growers aged above 68 years used chemical clearing combined with mechanical clearing. On the other hand, 71.3% of growers aged 28 - 37 years used chemical clearing combined with burning. The Pearson test reveals that the age of rice growers (p-value = 0.047531) at the 5% significance level. It should also be added that available manpower affects the choice of clearing type at the 5% threshold (p-value = 0.013249), as does the rice farmer's source of income (p-value = 8.6244e-12). Farmers who have another source of income in addition to agriculture (handicrafts, trade and livestock) prefer chemical clearing only (89%), whereas rice farmers who practice only agriculture opt for chemical and mechanized clearing (40%), in order to have a cleanly cleared plot.
Zero ploughing accounted for 47.5% of farmers versus 46.0% for tiller ploughing (
Figure 7). The Pearson test revealed that grower experience significantly influencing the choice of ploughing method with a p-value = 1.2901e-05. Growers with less than 10 years' experience were more inclined to use tiller and tractor ploughing, while growers with more than 11 years' experience favoured zero tillage and manual ploughing. Also, membership of a rice-growers' cooperative was found to influence the choice of ploughing type at the 5% significance level (p-value = 1.4452e-8). Indeed, growers who were members of a cooperative practiced more motorized plowing. The producer's source of income also affected the choice of ploughing method for p-value = 8.6244e-12.
As with ploughing, 47.1% of rice farmers opted for no muddling and 37.4% for tiller muddling (
Figure 8). Statistical analysis showed that several socio-economic factors had an impact on rice farmers' choice of mudding method at the 5% significance level. Access to agricultural credit influenced the choice of mudding method with a p-value = 2.2504e-10. The percentage of farmers without access to agricultural credit who adopted no muddling was 75%, while the percentage of farmers with access to agricultural credit who adopted tiller muddling was 88.5%. Rice growers with access to agricultural credit prefer tiller muddling.
The choice of tiller mudding method was influenced by the farmer's rice-growing experience (p-value = 0.012339). The tendency to use tiller mudding decreased with experience, i.e. those with less experience adopted more tiller mudding (55% for farmers with below 5 years’ experience, 20% for farmers with 6 - 10 years’ experience, 13% for farmers with 11 - 15 years’ experience and 11% for farmers with Above 15 years’ experience). Membership of a rice cooperative was a factor in the choice of mudding method, at p-value = 5.1297e-10, because around 75% of rice growers who were not members of an agricultural cooperative adopted zero and manual mudding, whereas 41% of growers who were members of a rice cooperative practiced tiller mudding. Adoption of the type of mudding also depended on the level of education of the rice farmer, with a p-value = 0.0038393. Preference for tiller mudding decreases with increasing level of education (45.5% for uneducated, 44.0% for primary, 30.5% for JHS and 19.2% for SHS). Plot ownership and mudding method were also related, with p-value = 0.00. Approximately, 88.8% of producers using public plots practiced mudding with tiller, whereas 87.5% of rice growers using family lands and 71.5% using rented plots adopted zero mudding, due to the availability of agricultural machinery on public irrigated schemes.
3.2.4. Setting Up the Growing Operation
Three cultivars, including IR 841 (83%), Chapeau vert (14.4%), GR34 (1.1%) and Nerica (0.4%), with seed purchased from agricultural extension service (43.1%) and agricultural input shop (29.8%), were planted on irrigated fields (
Figure 9). Rice transplanting was widely practiced (83%), compared with 17% of farmers who opted for direct seeding. Pearson's statistical test showed that the choice of sowing method is linked to gender at the 5% significance level (P-value of 0.010401). In comparison, women adopting transplanting were less numerous than men at the 5% significance level according to the Pearson test (p-value = 0.005). Access to agricultural credit and sowing method are linked at the 5% significance level with a p-value = 0.00, as 98.9% of rice farmers who obtained agricultural credit practiced transplanting, compared with 55% of rice farmers who have not had access to agricultural credit. Training also influences the adoption of the sowing method with a p-value = 1.4609e-06. Only 8.3% of trained farmers use direct seeding, compared with 30.3% of untrained farmers. Farmer experience has a significant influence on the choice of sowing type at the 5% significance level (p-value = 5.8013e-06). The rate of transplanting decreases as rice-growing experience increases, in the order of 84.7% for below 5 years’ growers, 81.3% for 6 - 10 years’ growers and 61.70% for 11 - 15 years’ growers. Nevertheless, 100% of growers above 15 years opted for transplanting.
Cultivation patterns varied on irrigated fields, with 25 cm x 25 cm and 15 cm x 15 cm being the most popular (
Figure 10). Statistical analysis shows that the choice of cropping pattern is affected at the 5% significance level by access to credit (p-value = 0.00). For example, over 93% of rice growers who adopted the 25 cm x 25 cm cropping pattern, essentially by transplanting, had access to credit, whereas around 94% of growers who adopted the 20 cm x 20 cm cropping pattern by direct sowing did not obtain agricultural credit.
Grower experience influenced the choice of cropping pattern at the 5% threshold (p-value = 2.3895e-08). Experienced growers with more than 15 years' experience preferred the 15 cm x 15 cm cultivation pattern, while the order of adoption of the 25 cm x 25 cm cultivation pattern decreased from growers with less than 5 years' experience (47%), growers with 6 - 10 years' experience (33%), growers with 11 - 15 years' experience (26%) and growers with 15 years' experience (4%). Gender and choice of cropping pattern were also linked for p-value = 0.0035642, because men preferred the 25 cm x 25 cm and 15 cm x 15 cm cropping patterns compared with women, whereas women adopted the 15 cm x 20 cm cropping pattern. Nursery time before transplanting was above 12 days for 71% of respondents and 8 - 12 days for only 9% of growers, with 20% of growers having no idea about nursery time. The farmers who opted for continuous monocropping of rice (58%) and rotation crops were okra (10.1%) and vegetable coret (1.8%). Training influenced the choice of cropping pattern at the 5% threshold (p-value = 4.1254e-10) because the majority of trained rice growers adopted a 25 cm x 25 cm cropping pattern.
3.2.5. Fertilization and Weed Control
Almost all respondents (99.3%) did not apply compost as basal fertilizer. On the other hand, 98.9% of rice growers applied mineral fertilizer in the form of N15P15K15 or urea 46%. A large number of rice growers (96.4%) did not apply N15P15K15 as a basal fertilizer (
Table 2). Nevertheless, two weeks after transplanting, over 40% of growers applied N15P15K15 fertilizer at doses ranging from 50 to 600 kg/ha, with a peak of 200 kg/ha (24%). At seven weeks after transplanting, 96.8% of growers had not applied any dose of N15P15K15 fertilizer, although small numbers of growers had applied doses ranging from 50 to 200 kg/ha. One week after transplanting, 30% of those responding had applied various doses of urea fertilizer (46% ranging from 50 to 400 kg/ha), while 70% of rice growers reported applying no fertilizer at all (
Table 3).
Nevertheless, by the seventh week after transplanting, 73% of growers had applied urea in doses ranging from 25 to 500 kg/ha, with a peak of 200 kg/ha (40%), as recommended by the agricultural extension services. At week ten, 80% of rice growers had not applied any urea fertilizer at all (46%). At the same time, 20% had applied doses of 46% urea ranging from 25 to 500 kg/ha, with a peak of 50 kg/ha (15%).
Table 4.
Amount & timing of urea application.
Table 4.
Amount & timing of urea application.
Application period of Urea fertilizer |
Amount applied (kg/ha) |
Percentage of farmers (%) |
One week after planting |
0 |
69,4 |
50 |
14,0 |
100 |
14,7 |
200 |
1,4 |
400 |
0,4 |
Seven weeks after planting |
0 |
27,0 |
25 |
0,4 |
50 |
1,8 |
100 |
16,5 |
150 |
11,5 |
200 |
39,6 |
300 |
1,4 |
400 |
1,1 |
500 |
0,7 |
Ten weeks after planting |
0 |
71,9 |
25 |
0,7 |
50 |
15,5 |
100 |
6,1 |
150 |
1,4 |
200 |
0,7 |
300 |
0,4 |
500 |
1,8 |
Fertilizer doses applied under rice were based on different sources, mainly routine practices (94.2%) and own knowledge (4.3%) (
Figure 11). The recommendations of agricultural extension services had a considerable impact on the choice of fertilizer doses. Herbicides were used by 98.6% of rice growers to control weeds (
Figure 12). Nonetheless, some combined this chemical method with manual or mechanical methods. These chemical herbicides were purchased from local markets (53.2%), generally unauthorized products, and from agricultural input stores (43.2%) (
Figure 13).
3.3. Irrigation Practices
Only 6.1% of rice growers have received training in rice irrigation, 64.7% of whom have received training in irrigation and drainage techniques, and 35.3% of whom have received training in water management. According to the respondents, water is distributed on irrigated fields in three ways: on-demand distribution (51.4%), continuous distribution (30.2%) and rotational distribution (13.3%) (
Figure 14). In any event, 100% of rice growers were unaware of the amount of irrigation water used for each application.
The water level above ground after irrigation varies from 0 to 15 cm, with over 57.5% opting for a water level between 5 and 15 cm (
Figure 15) and 80.2% of rice growers irrigated when water depth was below the soil surface (
Figure 16). Farmer training affected the choice of water level above ground after irrigation at the 5% threshold. Overall, 62% of trained rice growers adopted a water level between 5 and 15 cm, compared with less than 31% of untrained growers. However, around 54% of untrained rice growers versus 34% of trained growers preferred a blade of 0 cm above ground after irrigation. With regard to the dependence of grower experience on the water level above ground after irrigation, over 60% of growers with below 5 years of experience adopted between 5 -15 cm, while the oldest were in the order of 40%. Irrigation frequency on irrigated perimeters was ignored by 46.0% of farmers, and for 46.8% of respondents, irrigation frequency was below 10 days (
Figure 17). Over 30.6% of respondents were unaware of the water-saving technology used, with 33.8% adopting continuous flood irrigation and 23.0% practicing AWD (
Figure 18).
Regarding water distribution at plot level, 52.2% believed that water distribution was fair, versus 40% who didn't, and 8% who didn't know whether water was available for everyone. Moreover, 60.8% of growers acknowledged that the irrigation schedule was regularly respected, as opposed to 39.2% who didn't think so. According to 58% of growers, there were conflicts over irrigation water on irrigated perimeters, compared with 42% of rice growers. Access to the irrigation extension was available to only 5.4% of growers, compared with 94.6% who had no such access.
3.4. Famers’ Perception on Water and Agronomic Management
Almost all (98.2% vs. 1.8%) of the rice farmers surveyed had no knowledge of water productivity, and only fewer than 1.1% vs. 98.9% felt that water productivity could be improved through timely water delivery. Over 63.3% had no knowledge of water-use-efficiency and around 36.7% thought that water delivery as required improved water-use efficiency. Farmers' perception of water-saving methods for rice irrigation was variable (
Figure 19). An estimated 29% had no knowledge of irrigation water-saving methods. According to some, irrigation water saving methods were layout of rice-growing basins (36%), maintenance of tertiary canals (12%), being present in the field during water deliveries (7%), dam bulding (4%). Nevertheless, few growers thought that the methods for saving irrigation water were water delivery as required (5%) and good production scheduling (1%). Statistical analysis revealed that, at the 5% confidence level, training had improved farmers' knowledge of irrigation water saving. For example, of untrained farmers, 42% had no knowledge of water saving in irrigated rice production, compared with 28% of trained farmers. In addition, the grower's experience helped improve his knowledge of water-saving strategies in irrigated rice production to the 5% level. However, after more than 15 years' experience, 65% of growers were no longer applying water-saving methods.
Close to 28% of rice farmers did not know how to determine the irrigation period, while 49% thought they irrigated when the soil was dry (
Figure 20). Others irrigated by intuition (10%) or in relation to the transplanting period (6%) and the yellowing of the rice crop. To determine the amount of water to irrigate, over 32% of rice growers had no knowledge at all, and around 35% relied on rice height and leaves color, followed by 22% on intuition (
Figure 21). Meanwhile, less than 3% of rice growers used dikes to keep water from overflowing into basins. The factors for wasting irrigation water cited by growers were multiple, and the most recurrent included channel poor condition (32.6%) and poor irrigation practices (28.3%) respectively (
Figure 22). In the same way, factors such as illegal plots increasing around the irrigation scheme (12.4%), Non-respect of irrigation scheduling (11.5%) and Lack of billing by quantity of water used (6.6%) result in high overall water losses.
Over 97% versus 3% of growers agreed that the shortage of irrigation water was affecting paddy rice yields. To reduce the water deficit in rice irrigation, 34% of rice growers proposed using drain water, 28% suggested repairing the canal and 7% timely water demand (
Figure 23). As well, other growers thought that reducing water wastage (5%), respecting the irrigation schedule (3%) and having a janitor (1%) could reduce the irrigation water deficit on the irrigated perimeter. To make up for this deficit, 28% of rice growers used drainage water. With regard to the potential risks associated with the use of drainage water, 73% of rice growers were unaware and 25% felt that the use of drainage water presented no risk.
Like irrigation water deficit, some 77.3% of growers versus 22.7% and 80.2% versus 19.8% respectively acknowledge that excess irrigation water has a negative effect on paddy rice yields and fertilizer use efficiency. Thus, to reduce excess irrigation water, 27% of growers did not know how to proceed, 69% suggested improving drainage and only 4% recommended avoiding over-irrigation.
Rice growers (95.7%) had no knowledge of soil salinity and 96% were unaware of its causes (
Figure 25). However, 4.3% thought that the causes of salinity could be chemical inputs (1.8%), water logging (0.4%) and little amount of water (0.4%). As for the causes of salinity, 96% of rice growers were unaware of the consequences of salinity on rice production (
Figure 26). Nevertheless, 4% of growers thought that soil salinity was the cause of plant diseases, poor flowering, plant wilting and crop yellowing.
When asked how to improve irrigation water management, growers suggested Water-saving training (28.1%), Water-saving awareness (26.1%), Willingness to adopt water-saving method (22.5%), Water-saving practices monitoring (17.7%) and Irrigation canal repair (5.5%) (
Figure 27). Rice producers expressed different views on the disadvantages of inappropriate pesticide use (
Figure 28). The main consequences highlighted were soil and water pollution (34.5%), Yield loss (28.6%) and Soil salinity (23.0%). In the same way, rice growers considered that inappropriate use of fertilizers caused yield loss (33.9%), Fertilizer loss (30.4%) and oil and water pollution (24.2%) (
Figure 29). However, they recognized the positive effects of mulches and compost use on soil fertility improvement (28.9%), yield increase (24.9%), fertilizer use increase (24.5%) and saving-water (21.7%) (
Figure 30).
3.5. Impact of Socio-Economic Characteristics, Farming Practices and Irrigation Water Management on Paddy Rice Yields
Rice growers producing twice a year were estimated at 65.5%, compared with 34.2% of growers producing only once a year. However, 0.4% of rice growers produce three times a year. The Reasons due to one production cycle a year were diverse (
Figure 31). In ascending order, respondents ranked water shortage, tiller shortage and flooding as the most important reasons. Paddy yields were low, ranging from 0.4 to 4.2 t/h, with an average yield of 1.5 t/ha (
Figure 32). Fewer than 7.6% (21/278) achieved above-average paddy yields. The values showed that 62% of rice growers were below average, and over 88% of growers did not achieve a yield exceeding 2 t/ha, despite the 6 - 8 t/ha potential of the cultivar (IR841) mostly planted.
Pearson's statistical tests showed that some socio-demographic characteristics had an effect on paddy yield. The impact of farmers' age on paddy yields was not significant. Nonetheless, no farmer aged 18-27 or over 68 obtained a yield higher than the overall average (1.5 t/ha). In addition, growers obtaining yields in excess of 1.5 t/ha were limited to a maximum of two plots. Producer income sources also had a significant impact on paddy rice yields at the 5% confidence level (p-value = 0.00), because among producers who obtained more than 1.5 t/ha, the majority were rice growers who only practiced agriculture. Statistical analysis also showed that labor sources affected yields at the 5% significance level (p-value = 6.7845e-06). Sharecroppers accounted for 95% of farmers who achieved yields of over 1.5 t/ha. Access to credit and paddy yield were significantly linked (p-value = 0.00). Among producers who obtained more than 1.5 t/ha, access to agricultural credit was only 23.8% versus 76.2%. Grower experience influenced yield at the 5% significance level (p-value = 8.3061e-06), as among those with above-average yields, growers with 6-11 years' experience accounted for 57%, following producers with less than 5 years' experience (24%). Rice growers with more than 15 years' experience were less represented (19%).
Several farming practices affected paddy yield substantially. Clearing method was shown to have a significant effect on yield at the 5% confidence level, with a p-value of 0.00. Farmers using combined chemical and mechanical land clearing accounted for 52.3% of those who obtained more than 1.5t/ha, compared with 38% of those using chemical land clearing alone. The statistical test showed that the ploughing type affected yields at the 5% threshold (p-value = 1.3323e-15), because, among growers who obtained 1.5 t/ha, 57% opted for tiller ploughing and 38% for no ploughing. The type of muddling had a significant incidence on yields at the 5% level. Among rice growers who obtained more than 1.5 t/ha, manual muddling, no muddling and tiller muddling accounted for 57%, 33% and 10% respectively. The sowing method strongly contributed to paddy yield, and among farmers who obtained more than 1.5 t/ha, direct seeding accounted for 43% and transplanting for 57%. In the same way, the cropping pattern showed a significant effect on paddy yields at the 5% confidence level. Rice growers opting for the 15 cm x 20 cm and 20 cm x 20 cm cropping patterns accounted for 55.5% and 27.8% respectively of those achieving over 1.5 t/ha.
The Pearson test revealed a dependency between different fertilizer doses, fertilizer types and rice yield at the 5% confidence level. Applying N15P15K15 as a basal fertilizer affected yield for p-value = 0.000000. Over 95% of farmers who obtained 1.5t/ha did not apply any N15P15K15 as basal fertilizer. Meanwhile, applying N15P15K15 one week after sowing produced no effect on yield at the 5% confidence level (p-value = 0.40630). Of the farmers who obtained 1.5 t/ha, 67% applied zero amount of N15P15K15 and 19% applied 50kg/ha of N15P15K15 after one week of sowing. Fertilizing with N15P15K15 at seven and ten weeks after sowing yielded a significant effect for p-value = 0.024235 and p-value of 0.033371 respectively. Seven and ten weeks after sowing, farmers who applied zero N15P15K15 accounted respectively for 67% and 95% of farmers with above-average yields. The application of urea as a fertilizer had no effect on paddy rice yield at the 5% confidence level (p-value = 0.57826). Among rice growers who obtained more than 1.5 t/ha, 100% applied zero amount of urea as background fertilizer, 90.5% applied zero amount of urea one week after sowing and 100% applied zero amount of urea two weeks after sowing. Furthermore, the application of urea seven weeks after sowing had a significant effect on paddy yield at the 5% threshold (p-value 0.0042413). In fact, 90.5% of growers with yields of over 1.5 t/ha applied zero urea seven weeks after sowing. Among the best rice growers, 57%, 19% and 19% applied 100 kg/ha of urea, 50 kg/ha of urea and 150 kg/ha of urea respectively ten weeks after sowing.
Training in irrigation or water management had an effect on paddy rice yield at the 5% threshold (p-value = 8.9308e-08). Farmers who had been trained in irrigation represented 57.1% of farmers who obtained more than 1.5 t/ha, compared with 42.9% of those who had no training. Water delivery method affected rice yields significantly at the 5% confidence level (p-value = 0.00000). Among those with more than 1.5 t/ha, the number of farmers using the "distribution by demand" water delivery method was higher (67%), while the number of farmers using the "continuous distribution" method was lower (5%). Like water delivery method on irrigation scheme, water level above soil has a significant effected on yield at the 5% confidence level (p-Value of 0.00). Farmers with a water level above soil of between 0 and 5 cm accounted for around 81% of those producing more than 1.5 t/ha, while 19% were farmers with no water and producing under rainfed conditions. The water-saving technology adopted significantly affected yield with a p-value of 0.00000. Indeed, growers who opted for AWD represented more than 76.2% of rice growers who obtained more than the overall average yield (1.5 t/ha). Among those who obtained 1.5 t/ha, 86% felt that water saving could be implemented through the realization of rice paddocks. Among growers who obtained 1.5 t/ha, those who felt that excess irrigation water reduced the efficiency of fertilizer use accounted for over 76%. In addition, 33% and 38% respectively felt that fertilizer use efficiency could be improved by applying the recommended doses and appropriate practices.
5. Conclusions
In this research paper, the perceptions of rice growers in irrigated fields regarding agronomic practices and irrigation water management were assessed. Farmers' perceptions express their choices in terms of agronomic and irrigation practices. The socio-economic characteristics of growers influencing these choices were also studied. In the same way, the effect of respondents' socio-demographic profiles and agricultural and irrigation practices on paddy rice yields was also evaluated. The results revealed that farmer training in irrigated rice production and non-household farm labor use were positive for good farming and irrigation practices adoption, and hence high yields. In contrast, rice grower's experience, off-farm activities and access to agricultural credit negatively affected yields. Chemical combined mechanical clearing, tiller ploughing, transplanting, high plant densities and required doses of fertilizer applying at the convenient times were some of the farming practices that helped improve yields. On the contrary, tiller mudding was counter-productive. Furthermore, on-demand water distribution, above-soil water depth, water-saving strategies and knowledge of efficient water and fertilizer management methods were also irrigation practices that boosted yields. In view of these results, the study suggested that research should focus on training strategies covering as many producers as possible. In the same way, the real causes of the under-performance of agricultural credit and tiller mudding must be analyzed with a view to sustainable rice production, as agriculture modernization cannot be effective without farm machinery and access to agricultural credit.
Figure 2.
A conceptual framework.
Figure 2.
A conceptual framework.
Figure 3.
Number of plots used.
Figure 3.
Number of plots used.
Figure 4.
Reasons for choosing the harvest sales period.
Figure 4.
Reasons for choosing the harvest sales period.
Figure 5.
Training attended in rice production.
Figure 5.
Training attended in rice production.
Figure 6.
Plot clearing practices.
Figure 6.
Plot clearing practices.
Figure 7.
Plot plough practices.
Figure 7.
Plot plough practices.
Figure 8.
Plot muddling practices.
Figure 8.
Plot muddling practices.
Figure 9.
Seed purchase place.
Figure 9.
Seed purchase place.
Figure 10.
Crop spacing adopted.
Figure 10.
Crop spacing adopted.
Figure 11.
Basis for the quantity of fertilizer applied to the rice.
Figure 11.
Basis for the quantity of fertilizer applied to the rice.
Figure 13.
Herbicide purchase place.
Figure 13.
Herbicide purchase place.
Figure 14.
Water supply mode.
Figure 14.
Water supply mode.
Figure 15.
Water level above the soil after irrigation.
Figure 15.
Water level above the soil after irrigation.
Figure 16.
Water level above the soil surface before the next irrigation.
Figure 16.
Water level above the soil surface before the next irrigation.
Figure 17.
Irrigation frequency.
Figure 17.
Irrigation frequency.
Figure 18.
Water-saving technologies.
Figure 18.
Water-saving technologies.
Figure 19.
Knowledge on water-saving methods.
Figure 19.
Knowledge on water-saving methods.
Figure 20.
Determining the irrigation period.
Figure 20.
Determining the irrigation period.
Figure 21.
Determine the water amount to apply.
Figure 21.
Determine the water amount to apply.
Figure 22.
Water wastage factorsTo improve the fertilizer-use efficiency, more than half the growers (51.8%) recommended fertilizing without water, 3.2% thought application rates recommended for fertilizers and 2.9% suggested increasing the fertilizer rate (Figure 24). On the other hand, over 39% of rice growers did not know how to improve fertilizer-use efficiency. The Pearson statistic showed that training improved farmers' knowledge of fertilizer-use efficiency at the 5% level. In fact, 65% of untrained growers did not know how to improve fertilizer-use efficiency, whereas 71% of trained farmers felt that to increase fertilizer-use efficiency, it was necessary to drain the water before fertilizing and to respect the recommended amount. However, the growers' experience had no impact on the strategy for improving fertilizer-use efficiency to the 5% level. Furthermore, over 94.6% had no access to irrigation advisory service for improving water management, which would justify the poor performance of irrigated fields.
Figure 22.
Water wastage factorsTo improve the fertilizer-use efficiency, more than half the growers (51.8%) recommended fertilizing without water, 3.2% thought application rates recommended for fertilizers and 2.9% suggested increasing the fertilizer rate (Figure 24). On the other hand, over 39% of rice growers did not know how to improve fertilizer-use efficiency. The Pearson statistic showed that training improved farmers' knowledge of fertilizer-use efficiency at the 5% level. In fact, 65% of untrained growers did not know how to improve fertilizer-use efficiency, whereas 71% of trained farmers felt that to increase fertilizer-use efficiency, it was necessary to drain the water before fertilizing and to respect the recommended amount. However, the growers' experience had no impact on the strategy for improving fertilizer-use efficiency to the 5% level. Furthermore, over 94.6% had no access to irrigation advisory service for improving water management, which would justify the poor performance of irrigated fields.
Figure 23.
Water deficit reducing strategies.
Figure 23.
Water deficit reducing strategies.
Figure 24.
Fertilizer use-efficiency improvement.
Figure 24.
Fertilizer use-efficiency improvement.
Figure 25.
Salinity causes.
Figure 25.
Salinity causes.
Figure 26.
Salinity consequences.
Figure 26.
Salinity consequences.
Figure 27.
Water management improvement.
Figure 27.
Water management improvement.
Figure 28.
Inappropriate pesticides use.
Figure 28.
Inappropriate pesticides use.
Figure 29.
Inappropriate fertilizers use.
Figure 29.
Inappropriate fertilizers use.
Figure 30.
Mulches and compost use.
Figure 30.
Mulches and compost use.
Figure 31.
Reasons due to one production cycle/year.
Figure 31.
Reasons due to one production cycle/year.
Figure 32.
Yield from last production cycle.
Figure 32.
Yield from last production cycle.
Table 1.
Study samples.
Region |
Rice irrigation schemes |
Sample of rice farmers |
Coastal region |
Kovie |
76 |
Agome- Glouzou |
92 |
Forest region |
Kpele Beme |
44 |
Kpele Tutu |
36 |
Savannah region |
Koumbeloti |
30 |
Total |
|
278 |
Table 2.
Farmers' socio-demographic characteristics.
Table 2.
Farmers' socio-demographic characteristics.
Profile of producers |
Women |
Men |
Total |
Gender |
|
90 |
188 |
278 |
Age |
No knowledge |
0 |
4 |
4 |
18 – 27 years |
4 |
15 |
19 |
28 – 37 years |
11 |
46 |
57 |
38-47 years |
33 |
55 |
88 |
48 – 57 years |
27 |
47 |
74 |
58 – 67 years |
14 |
20 |
34 |
above 68 years |
1 |
2 |
3 |
Marital status |
No answer |
0 |
1 |
1 |
Divorced |
1 |
0 |
1 |
Married |
70 |
169 |
239 |
Single |
4 |
12 |
16 |
Widower/widow |
15 |
6 |
21 |
Educations background |
None |
32 |
22 |
54 |
Primary |
39 |
65 |
104 |
JHS |
14 |
70 |
84 |
SHS |
3 |
23 |
26 |
University |
2 |
8 |
10 |
Experience |
Below 5 years |
35 |
76 |
111 |
6 – 10 years |
16 |
48 |
64 |
11 – 15 years |
21 |
27 |
48 |
above 15 years |
18 |
37 |
56 |
Type of tenancy |
No answer |
0 |
1 |
1 |
Clan-based |
12 |
20 |
32 |
Own |
5 |
22 |
27 |
Public |
25 |
64 |
89 |
Rented |
48 |
81 |
129 |
Member’s of farmers cooperative |
No answer |
0 |
6 |
6 |
No member |
10 |
33 |
43 |
Member |
80 |
149 |
229 |
Source income |
Agriculture |
56 |
116 |
172 |
Agriculture & Trade |
25 |
15 |
40 |
Agriculture & Handicrafts |
3 |
33 |
35 |
Agriculture & Livestock |
6 |
24 |
30 |
Agricultural credit access |
Agricultural credit access |
40 |
60 |
100 |
No Agricultural credit access |
50 |
128 |
178 |
Table 3.
Amount & timing of N15P15K15 application.
Table 3.
Amount & timing of N15P15K15 application.
Application period of N15P15K15 fertilizer |
Amount applied (kg/ha) |
Percentage of farmers (%) |
Basal |
0 |
96,4 |
150 |
1,8 |
200 |
1,1 |
250 |
0,4 |
Two weeks after planting |
0 |
38,8 |
50 |
1,4 |
100 |
6,5 |
150 |
11,2 |
200 |
24,1 |
250 |
0,4 |
300 |
10,1 |
400 |
6,1 |
500 |
1,1 |
600 |
0,4 |
Seven weeks after planting |
0 |
96,8 |
25 |
0,4 |
50 |
1,1 |
100 |
1,1 |
200 |
0,7 |