Using small-scale on-farm weather monitoring equipment as a tool for understanding farmer rationales and risk management in response to climatic risk. Kaori Sasaki”, John S. Caldwell*, Abou Berthé+, Mamadou Doumbia+, Hiromitsu Kanno”, Kiyoshi Ozawa*, Abdouramane Yorote+, Takeshi Sakurai* ”National Agricultural Research Center for the Tohoku Region, Morioka, Iwate, Japan *Japan International Research Center for Agricultural Sciences (JIRCAS), Tsukuba, Ibaragi, Japan +Institut d’Economie Rurale (IER), Sotuba, Bamako, Mali ABSTRACT Farmer decision making and management are highly influenced by climate, especially uncertain rainfall, in rainfed agriculture in areas such as Mali, West Africa. We have used small-scale, automated weather monitoring equipment on-farm as a tool for understanding farmer rationales in response to climatic risk. Precipitation and air and soil temperature recording stations equipped with a data logger (Onset, HOBO) that can record over a long time period without maintenance were placed on 15 collaborating farmers’ fields in each of two villages chosen in a reconnaissance. Using farmer-defined land units (terroirs), farmers indicated areas on maps with early rainfall, and this empirical knowledge was supported by the distribution of early rainfall measured by the stations. We will show the equipment and results of analysis of temporal and spatial rainfall variability compared with farmer management monitored weekly, particularly dry seeding. INTRODUCTION The climate of Mali, West Africa, is not uniform, but varies depending primarily on latitude. In the north is the Sahara desert, while the south is a transition region from the Sahel to the tropical rain forest. Even in the south, the total amount of rainfall varies from 200 mm at the limit the arid zone, through 500-900 mm annual rainfall in the semi-arid zone, and 900-1100 mm in sub-humid zone, reaching up to 1400 mm at the southernmost limit. Overall, West Africa is extremely vulnerable to changes in water availability, as precipitation shows high interannual, seasonal and spatial variability. As a result, farm management and decision making are greatly influenced by climate. The risk of uncertain rainfall has increased since the 1980s. Precipitation isohyets have moved southward by 0.5-1.0° latitude, or approximately 100-200 km (Ministère IHE, 1990). Locations that formerly had 1000 mm and fell in the sub-humid zone (900-1100 mm annual rainfall, Berthé et al., 1991) now have 800 mm of rainfall and fall into the semi-arid zone (500-900 mm annual rainfall). In the February 2001 reconnaissance of nine villages, farmers were highly aware of spatial variability. Farmers had indicators which they found empirically useful to anticipate the coming rainy season, while they also made use of meteorological forecasts over the radio. However, current meteorological forecasts are made at the regional level, which can span a range of 700 mm to 1200 mm annual rainfall. Farmers said that they could not use radio forecasts for their specific conditions, and they needed fine-tuned forecasting at the district or sub-district level. On the other hand, meteorological observatories are limited in number and location. Previous studies of rainfall variability in West Africa have used rainfall data from the regional level of about 100 km2, which includes a large amount spatial variability. Mechanisms of local rainfall variability have not been identified completely. In addition, the degree of spatial variability occurring at the field revel is not known. To address these issues, we have undertaken assessment of interannual, seasonal and spatial variability at the farmer’s level. This will be also useful for downscaling of strategic rainfall prediction. In recent years, meteorological observation technology has developed considerably. New, inexpensive weather monitoring equipment now makes it possible to obtain field-level weather data to compare with farmer practices. Our ultimate goal is the development of a decision aid system, based on analysis of risks associated with climatic variability in alternative farmer production choices. In this paper, we report on: The on-farm weather monitoring equipment used Results of analysis of weather data from these stations, especially temporal and spatial variability of precipitation, and comparisons with empirical knowledge of farmers. Some results of comparisons of farmer behavior with rainfall events. We will show these results in several examples that are derived from collaboration between farmers and researchers. MATERIALS AND METHODS A reconnaissance survey of nine villages was conducted in February 2001. In the southeastern area of Mali, preliminary selection of villages was done using topography and the location of larger lowlands that are called bas-fonds. After surveying nine villages retained, we chose two villages as research sites based on team ranking of 10 criteria (Caldwell et al., 2002a, 2002b). One is Niessoumana (10 x 14 km area) located at the frontier of the semi-arid zone with 800 mm of average annual rainfall, and other is Diou (23 x 19 km) located in sub-humid area with 1200 mm average annual rainfall (Fig. 1). The topography is essentially flat in Niessoumana (although microvariation in topography was documented in our research), and more undulating in Diou. Fig. 1 Location of the two research sites Annual rainfall is averaged from 1969 to 1992. Semi-arid Village Niessoumana (mm) Semi-humid Village Diou One larger main meteorological observation station was placed in the center of each village. These stations record precipitation, air temperature, relative humidity, wind speed, wind direction, solar radiation and air pressure. In addition, 15 farmer collaborators were selected based on risk robustness and land use criteria (terroirs, as defined by farmers using a farmer-drawn land use map in May 2001) for the weather monitoring equipment, which we call ‘HOBO station’ (Fig. 2). These measure precipitation, air and soil temperature. Each HOBO station is equipped with a compact, inexpensive and high performance data logger (Onset, HOBO). It is thus able to record over a long time period without maintenance. A total of 29 HOBO stations were set, 14 in Niessoumana and 15 in Diou, respectively. The locations of the HOBO stations in Niessoumana are indicated in Figure 3. All of the HOBO station equipment was set on a wooden stand. Installation conditions are shown in Figure 2. HOBO stations were set in the different types of crop fields, including cotton, rice, millet, maize, and groundnut, of farmer collaborators. The collaborators were chosen based on farmer-defined risk indicators and land use through a participatory process (Caldwell et al., 2002b). Meteorological observation began in late May 2001 and is still continuing. We report here on the results of the 2001 rainy season 2001 from 26 May to 19 September in the semi-arid village, Niessoumana, in this paper. In each village, we presented our activities and results, providing feedback back to farmers and checking with their perceptions and knowledge through farmer’s meetings. On the fourth visit in July 2002, we showed a rainfall map based on HOBO observations and compared it with farmer’s understanding and recognition of rainfall variability. We also conducted transect surveys with farmers, recording local topographical variability as well as microchanges in flora and the location of plants that served as indicators of the rainy season. In addition, we obtained aerial photograph images of the topography and compared these with transect and field observations of topography. Air temp. and Rain gauge Logger(HOBO) in a Shelter Logger Soil temp. (HOBO) Fig. 2 HOBO station for recording precipitation and temperature (installed May 2001) RESULTS AND DISCUSSION Performance of weather monitoring equipment Routine maintenance and data collection from HOBO stations is conveniently done using a notebook personal computer through the serial port. Functioning of the data logger is easily checked based on a flashing light. Detailed precipitation data were collected by the HOBO for each event with high resolution. Air and soil temperature data were collected every an hour. A HOBO is able to store 8000 data, which is sufficient to record an entire rainy season. However, during the year, many kinds of unexpected problems occurred. Some of the soil temperature cables were eaten by cattle, and wooden stands were attacked by termites during the dry season. At certain times, the HOBO logger stopped unexpectedly. We attributed the cause to conveyed lightning. All of the problems were resolved, and from these experiences, field assistants (one per village) learned what to check for to assure functioning of the equipment. These problems caused us to understand the difficulty of obtaining a complete set meteorological observations, and what is needed to assure this. It is very important to consider the environment in which stations are placed in advance and establish a program for frequent maintenance. Spatial variability of rainfall: focus on the onset of rainy season The onset of the rainy season is critical for crop seeding and germination. Weekly precipitation in the first month of the rainy season was mapped from HOBO station data in the semi-arid village, Niessoumana, and is shown in Figure 3. The northeast, east and southeast extremes had highest rainfall, more than 100 mm in this period. Rainfall then decreased gradually as one moved westward. However, there were no observation sites at the far western part of the village, and this trend could not be confirmed all the way to the western limit of the village... The maximum spatial difference is about 30 mm in this village, within an area of 10 x 14 km. This value indicates that during the first stage of the rainy season, rainfall varied by 30% between fields only few km away from each other. At the end of rainy season, the total rainfall of Niessoumana averaged about 1000 mm, a value 100 mm greater than average rainfall at the N’Tarla agronomic research station which is close to Niessoumana. The spatial variability of total rainfall had same trend as shown in Figure 3 for the first month of the rainy season. This leads us to conclude that rainfall spatial variability is a characteristic of the rainy season as a whole. We are currently assessing topographical variation revealed from the transect survey and aerial photograph imagery as a factor affecting spatial variability. Comparison between rainfall map generated from HOBO observations and farmer understanding of rainfall variability We held a meeting with farmers in Niessoumana in July 2002 to compare farmer knowledge and the results of HOBO station observations. We printed key maps and graphs and shared these as graphical results with the farmers. At first, however, in the meeting we did not show these, but instead asked the farmers in which areas they observed rainfall to start and in which areas rainfall was highest. Farmers answered that rainfall starts from the east side, followed by the northeast and southeast areas, and that these areas also have highest rainfall, based on their observations. Then we showed our rainfall map, and the farmers agreed that it matched their observations. This shows that farmer empirical knowledge of rainfall is quite accurate. If this can be confirmed in other villages in the future, then farmer knowledge may be used to help assess and improve agronomic practices on a spatial basis. Fig. 3 Spatial Variability of rainfall, June 22-28 in semi-arid village, Niessoumana. ■ : main meteorological station, ● : HOBO station. Isohyets show total rainfall during June 22-28, 2001. Hatching indicates areas with greater than 100mm rainfall. Farmer behavior at the onset of rainfall Farmers often divided plantings of the same crop between two fields. One field was seeded earlier, prior to the first rains, and the other after the first rains. This is a farmer strategy for reducing risk. Early seeding is called semis-á-sec, or “dry seeding”. If it succeeds, the crop is in the field for a longer period of time and can benefit from all the rainfall of that year. However, considerable variability was seen in the success of semis-á-sec, depending on the number of days prior to the first rain. When semis-á-sec failed, due to late rains or poor distribution of rainfall in the young seedling stage, farmers must reseed. Reseeding increases seed and labor requirements and may result in lower yield if maturity comes after rains end. There was high variability in seeding dates for each crop. For some crops, the standard deviation in initial seeding was greater 10 days. The pattern of seeding matched the pattern of rainfall spatial variability (Fig. 3). This again validates the value of farmer knowledge. 35 P recipitation Tem perature 30 20-Sep 13-Sep 6-Sep 30-Aug 23-Aug 0 16-Aug 0 9-Aug 5 2-Aug 20 26-Jul 10 19-Jul 40 12-Jul 15 5-Jul 60 28-Jun 20 21-Jun 80 14-Jun 25 7-Jun 100 o 120 Mean temperature(C) N iessoum ana 31-May Weekly total precipitation (mm) 140 D ate Fig. 4 Weekly rainfall and temperature, May-September, 2001, in semi-arid village, Niessoumana. Weekly precipitation and temperature are calculated from main station data. The dashed line shows the division of the rainy season into early and middle stages apparent in rainfall event frequencies. On June 22-28, data was lost with rain gauge trouble, and interpolated the average of nearest 3 HOBO stations. 100 N iessoum ana Precipitation (mm) 90 80 70 60 50 40 30 20 10 0 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Localtim e Fig. 5 Hourly total rainfall averaged over the period May 26-Sept. 19 in Niessoumana. Values are averages of 13 HOBO stations. Intraseasonal temporal variability of rainfall At the beginning of rainy season, rainfall events are not constant, and the amount of rainfall per week is unstable (Fig. 4). There were breaks in rainy season, with no rainfall recorded. The earlier breaks increase the risk of seedling failure. Conversely, one rainfall event exceeded 100 mm in one night (July 5). As the rainy season progresses, air temperature slowly decreases. After the middle of July, rainfall events happen more frequently and amount of rainfall of each event is less more constant while temperature decrease stops and temperature stays at 26oC. Figure 5 shows hourly rainfall variability in Niessoumana. We can see a clear diurnal variation, in which the maximum rainfall is observed late in the night and / or early in the morning, while on the other hand, minimum rainfall tends to appear in midday. Also, daytime spatial variability is higher (data not shown). These characteristics of diurnal variation are in good agreement with the nature of convective activity over the land, caused by the movement of the Inter Tropical Convergence Zone (ITCZ). CONCLUSIONS AND FUTURE DIRECTIONS The extent of local spatial Fig.6 variability of rainfall was determined from on-farm meteorological observations. Hour Also, farmer behavior, particularly for seeding, corresponded with rainfall events ly and indicated a strategy of risk dispersion. Similar analysis of the spatial variability of rainfall and seeding dates is being undertaken now total for the semi-humid village. rainf The mechanisms of spatial and all temporal rainfall variability have not been established, but observation of localizedavera topography through transect surveys with farmers, together with aerial photographs, gedin comparison with rainfall observation conducted in this study, may provide a keyforto understanding this variability. We plan to assess topographical relationships among May the sample fields, to determine if topographical location is related to the spatial 26-se variability in arrival of the first rains. The key question for monitoring is to determine how rainfall variability interacts with p. 19 farmer choices of planting dates, in varieties, and weeding practices. We are gradually developing an understanding ofNiess farmer responses and their decision making process in response to climatic variability.ouma In the semi-arid village, the 2001 season represented a wet year, and indicated farmer responses to wetter-than-normal conditions. Conversely, na. the semi-humid village had drier-than-normal conditions in 2001. As we observe farmer choices and rationales under different sets of rainfall conditions over the four The years anticipated in this research, we hope to be able to provide in a future report a values complete picture of farmer strategies in response to micro-level rainfall spatial and are temporal variation. averag e of 13 HOBO stations . REFERENCES Berthe A.L., Blockland A., Boure S., Diallo B., Diallo M.M., Geerling C., Mariko F., N’Djim H and Sanogo B. (1991) Profil d’environnement Mali-Sud. Institut d’Economie Rurale, Bamako, Mali, and Institut Royal des Tropiques, Amsterdam. Caldwell, J.S., H. Kanno, A. Berthe, A. Yorote, K. Sasaki, M. Doumbia, K. Ozawa, T. Sakurai (2002a) Climatic Variability in Cereal based Cropping Systems in Mali, West Africa. Farming Japan 36-4, 35-41 Caldwell, J.S, A. Berthé, M. Doumbia, H, Kanno, K. Ozawa, A. Yorote, K.Sasaki, T. Sakurai (2002b). Incorporation of Farmer-Based Climate and Risk Indicators into Research Design and Farmer Typologies in Southern Mali. Journal for Farming Systems Research-Extension 17th International Symposium issue (in press). Ministere de l’Industrie, de l’Hydraulique et de l’Energie et Programme des Nations Unies pour le Devloppement (1990) Synthese hydrogeologique du Mali. Departement de la Cooperation Technique pour le Developpement (DCTD), Bamako, Mali. Corresponding author information: Kaori SASAKI National Agricultural Research Center for Tohoku Region 4, Akahira, Simokuriyagawa Morioka, Iwate, 020-0198, Japan Tel. 81-19-643-3461 Fax. 81-19-643-3573 E-mail kaoris@affrc.go.jp Tool Bazaar