A PROPOSAL TO STUDY DIFFERENT SOIL ORGANIC AND INORGANIC AMENDMENT OPTIONS FOR THE MANAGEMENT OF SALINE/SODIC SOILS AND TEST HIGH VALUE CROP SUITABILITY FOR KALACHA IRRIGATION SCHEME 1 TABLE OF CONTENTS 1.0 INTRODUCTION ............................................................................................................. 3 1.1 GENERAL BACKGROUND ......................................................................................... 3 1.2 STATEMENT OF THE PROBLEM .............................................................................. 4 1.3 JUSTIFICATION OF THE STUDY .............................................................................. 5 FIRST EXPERIMENT ................................................................................................................... 6 Table 1. Experimental layout .......................................................................................................... 7 SECOND EXPERIMENT .............................................................................................................. 7 THIRD EXPERIMENT .................................................................................................................. 8 STATISTICAL ANALYSIS .......................................................................................................... 8 REFERENCES ............................................................................................................................... 9 ANNEX1 BUDGET ABD WORKPLAN……………………………………………………… 10 2 1.0 1.1 INTRODUCTION GENERAL BACKGROUND Sporty agricultural research work in arid and semi-arid has been done, yet this area forms a fifth of the county’s food production zone (Chepchirchir et al 1996). Over reliance on rain-fed agriculture is identified as a contributor to food shortage and insecurity (GoK, 2002). However, a high population growth rate of 2.9% (GoK, 2002) has resulted in increased land pressure that has caused migration of farmers to the Arid and Semi-arid Lands (ASAL). Owing to frequent prolonged droughts, farmers are turning to irrigation as a way of increasing agricultural production in ASALS. . The problems emanate from the change of land use from pastoralism to irrigated farming without adequate capacity to face the challenges of sustainable irrigation development (Muchangi et al., 2005). This has resulted in farming being carried out on this fragile land, with little knowledge or skills on its management. Soils in arid and semiarid regions are characterized by relatively low organic matter (OM) content, high levels of salinity and sodicity, high percentages of expandable clay minerals, and low vegetative cover; all which decrease the stability of the soil structure (Ben-Hur, 2007, Wakindiki et al., 2001). About 40% or about 25 million ha of the land of Kenya is covered by soils that have salinity and/or sodicity problem(s). Of the area under irrigation, more than 50% is undergoing severe land degradation through secondary salinisation and sodification mainly due to improper irrigation and soil fertility management practices (Ngigi, 2002) Many workers (Withers and Vipond, 1974, Mugwanja et al., 1995) stipulate that the success or failure of any irrigated agriculture is determined by the extent to which salt and sodium problems are controlled. Such soils frequently produce serious agricultural and management problems. Not only do they bring the problem of toxicity, but also reduce soil quality, hence soil productivity. Doran et. al., (1999) define soil quality as the capacity of the soil to function in sustaining biological productivity, maintaining environmental quality and promoting plant and animal health. In this context, understanding the effects of salt and sodium concentration on soil quality within the root zone is imperative to ensure sustainable soil quality management under irrigated agriculture (Bernstein and Ogada, 1966). Low irrigation efficiency can create high water table, particularly in restricted drained conditions, thereby causing excessive accumulation of sodium (Bui et al., 1996). In Addition, decline in soil organic matter and nutrient status of these soils requires judicious management strategies for sustained productivity (Mugendi et al., 1999. Success stories on rehabilitation of saline soils for crop production are few and studies show that many irrigation schemes in Taveta area in the coast region have been out of operation since 1996 due to salinity and sodicity problems (Mugwanja, 1995). The management techniques that have been experimented on are leaching, planting methods and use of different crops. Leaching and drainage showed that crop production greatly improved in areas which had otherwise been abandoned due to salinisation and sodification (Muchena, 1985; Mugwanja, 1997).However these management specifications were not being followed due to high costs resulting in further deterioration of soil physical conditions and poor crop yields. This necessitates research to come up with cheaper strategies of management for these soils. Use of gypsum and organic manures were seen to improve sodicity at Bura irrigation scheme; however the results were inconclusive as the appropriate levels of application were not determined (Muchena, 1987). It was therefore concluded that the irrigation scheme partly failed due to deteriorating soil conditions owing to lack of proper soil amendments. These studies therefore indicate that a study of the degree and necessary remedial measures of soil structure deterioration on irrigated saline and sodic soils is required (Wanjogu et al., 2001). Other soil structural characteristics such as water infiltration rate increased with any amendment containing gypsum, Effects of combining gypsum and FYM are expected to give better results and will be tested in this study. 3 This study will therefore have four main strategies in addressing the management of saline and sodic soils in Kalacha irrigation scheme in northern Kenya. These will be 1). Irrigation methods where furrow and drip will be used. Alternate furrow irrigation moves the salt to un-irrigated furrows away from the root zone while drip irrigation will be used to leach the salt below the root zone 2). Plant-based approach using velvet bean (Mucuna pruriens) legume for N-fixation, organic matter increase to improve soil structure and nutrient cycling 3) Fortified compost organic input to improve the soil organic matter content, soil aggregate stability, available water holding capacity and infiltration rate (IR) and 4) Use of gypsum to enhance sodium removal and improve on soil chemical balances. 1.2 STATEMENT OF THE PROBLEM The Kalacha irrigation scheme has seen agricultural production reducing by over 80% between 1984 and 2005 and currently its virtually non existent. This could be attributed to increased salt and sodium concentrations in the soil. Currently, farmers are hesitant to grow crops in the scheme, because they claim that water disappears before reaching the crops. They describe the soils as soapy and smeary when wet, and extremely hard when dry. These soils have poor structure, very high pH, which is too alkaline for crop growth, low organic matter content, high electrical conductivity and high Exchangeable Sodium Percentage (ESP), suggesting extreme saline-sodic conditions. Research results into management of saline soils in Kenya are not documented and yet a study of some of the soils in these areas shows that salinity is a major problem (Mugwanja, 1995, Muchena, 1989). The farmers are aware of soil salinity and its bad effects. The problem is more pronounced in recent years leading to some farmers abandoning farming altogether while others are growing forages under irrigation (Muya et al. 2009). Increased salinization, loss of nutrients through leaching of N and degraded soil structure are serious problems affecting crop productivity at Kalacha irrigation scheme. Consequently, farmers are abandoning crop farming for fodder grass production at the schemes in Marsabit, Kenya. A similar scenario is seen at irrigation projects that had been initially successful and have in many cases declined in productivity and, in some cases, have been abandoned (Muchangi et al., 2005; Ngigi, 2002). Salinity and sodicity are serious problems considering that over 40% of Kenya’s land area is occupied by saline, saline-sodic and sodic soils, covering 2.9, 14.0 and 8.2 million ha respectively. Onion (Allium Cepa) is one of the most potential export crops (Currah and Proctor, 1990; HCDA, 2003) that can be grown under irrigation at the Kalacha irrigation scheme. Bulb onion is considered to be the most important species of the Allium genus and is the third in terms of vegetable production (Brewester, 1994). The production levels in Kenya are low averaging 11 t/ha as compared to Korea whose production is at 46 t/ha. The main cause of decline in agricultural productivity in the scheme was found to be increased salinization, loss of nutrients through leaching of N and degraded soil structure as a result of wrong choice of irrigation methods and practices (Muya et al., 2009). Past studies in the area indicate that the soils are high in sodium and salt concentrations (Muya et al 2009; Ngigi, 2002; Mugwanja et al., 1995; Muchena, 1987). High sodium levels in the soil leads to the collapse of the soil structure and blockage of soil pores. The accumulation of salts in the root zone could be due to poor irrigation water, unsuitable irrigation methods and scheduling that does not take into consideration soil type and infiltration capacity of the soil. This leads to poor soil aeration, poor permeability and water logging thus not allowing leaching of these salts beyond the crop rooting zone. The ultimate result is poor crop growth or complete crop failure (Landon, 1991). There is also an imbalance of cations such as Ca, Mg and K ratios leading to artificial deficiency of these 4 cations. This could partly be attributed to the low water quality that is used for irrigation. Soil analysis shows a high pH and low soil organic matter. It has been observed that farmers in the scheme do not apply any organic fertilizers to the soil and the stover from the crops grown is fed to livestock leaving little chance for organic matter to accumulate in the soil. The soil amendments suggested in this study are aimed at addressing these problems. 1.3 JUSTIFICATION OF THE STUDY Kenya’s onion production has stagnated at about 11t/ha for a long period (FAO, Statistics 2002) while the top producing countries such as South Korea produce up to 46 t/ha. Kenya has potential to produce up to 20 t/ha under irrigation. Production of high value crops such as onion can earn the farmers some income and help alleviate poverty which is one of the Millenium Development Goals (MDG) that the Government of Kenya (GoK) aims to achieve by 2015. This is also in line with the vision 2030 which emphasizes on the need to improve the agricultural sector which is the driving force of the Kenyan economy. Irrigation activities were at their peak in Kalacha in the 1980s before a myriad of problems led to the decline in agricultural production. Onion is important as a cash crop for this scheme as it is less vulnerable to wildlife destruction compared to other crops. It is a potential crop for export (Currah and Proctor, 1990) but little has been done in Kenya to increase its production levels. Currently there is increased demand for onion following increased awareness of its medicinal properties and reduction of imports from Tanzania and Eritrea. There is mounting evidence that all members of the onion family have a positive effect in lowering incidences of heart disease. Trials in the mid-nineties showed a drop in cholesterol levels of a test group when given garlic powder. Nutritionally an average size raw onion contains 1.8g protein, 11.9g carbohydrates, 5g sodium and 38g calcium per 100g. Onions have a long shelf-life and can keep for up to 3 months after harvest when well dried and aerated. They are also of high value, of short duration and with good planning one can have 3 crops per year. Under good management yields of up to 10 tons per acre can be obtained in Kenya. Higher yields of to 23 tons per acre have been reported in Korea (FAO, 2002) and at Ksh 40 per kilogram in Marsabit town can fetch up to Ksh 400,000 per growing period. Onions can be easily transported over large distances with minimum damage making marketing less of a problem in its production. The crop is therefore suitable as a cash crop for areas such as Kalacha that have poor infrastructure and high levels of poverty. Production of this crop is however a challenge under the saline – sodic soils of the area. Under the current production system at the site, farmers have indicated that they are not sure of the crop varieties that are suitable for the area, hence the decline in production. This study will therefore address soil management and suitability of high value crops at the site under the current climatic and appropriate irrigation conditions. There will be three main approaches in addressing the salinity and sodicity of Kalacha irrigation scheme soils: (1) plantbased approach (including legumes for N-fixation, and deep roots to break soil hard pan and grass shallow rooted) to improve soil structure and nutrient cycling, (2) organic inputs and chemical amendments to improve the organic matter content, soil aggregate stability, soil water holding capacity, soil quality and availability of nutrients to the crop (3) monitoring of water use efficiency and leaching for salinity / sodicity management through the use of drip and furrow irrigation. OBJECTIVES OF STUDY The study will have two main objectives: 5 1. To test different soil management options for the improvement of saline-sodic soils. This will include soil amendments especially gypsum, vermicompost, compost manure, fortified farm yard manure and crop based options (barley and mucuna) as green manure 2. To develop the sustainable and economically viable production systems through testing high value crops suitability for Kalacha. Among the crops that are recommended from the study are garlic, chilli, ginger, tumeric and onions that have a good local and national market Among the parameters that will be measured are: 1. To quantify the hydraulic conditions of the soil to provide data for calculating the irrigation water application rate and time setting. 2. Crop yields under the different management options and identifying the best options 3. Evaluating the different for adaptability to the climatic and soil conditions There will be 3 experiments in total. The objective of the first experiment is: To compare the performance of onion under the different soil amendments for the improving saline/sodic soils of Kalacha under two irrigation methods; drip and furrow. FIRST EXPERIMENT The study will investigate the effects of the following factors/ treatments 1. 2 irrigation methods (furrow or drip) 2. Cover crop type – shallow and deep rooted Soil amendment – basically fortified compost (with gypsum, at rates determined in the laboratory). 9 treatment combinations (gypsum fortified compost. Fortified compost at 3 rates and gypsum at 4 rates, giving the following treatment combinations: (1) C0G0 (2) C0G25 (3) C0G50 (4) C10G0 (5) C10G25 (6) C10G50 (7) C15G0 (8) C15G2.5 (9) C15G5 (10) C0G7.5 (11) C10G7.5 (12) C15G7.5); where C and G stand for compost and Gypsum, respectively. The levels of gypsum that will be used in compost fortification will be determined in a laboratory protocol by incubation of soils from the study site. The treatments will be arranged in a split-split plot design. The 2 irrigation methods will be assigned to the main plots. The cover crop types will be assigned to sub-plots while the soil amendments (12 treatment combinations) will be assigned to sub-sub-plots. The sub-sub plots will measure 3m x 3m with 1m between plots. The treatments will be replicated 3 times. Onion will be the test crop and at planting basal phosphorus at a level of 50kg/ha will be applied. Soil moisture monitoring will be carried out in treatments with compost levels at 0, 10 and 15 t/ha while other soil physical and chemical analysis will be carried out in treatments with gypsum levels at 0, 2.5, 5 and 7.5 t/ha, respectively. 6 Table 1. Experimental layout BLOCK 1 BLOCK 2 BLOCK 3 Furrow irrigation 9 1 5 7 3 10 12 4 11 6 2 8 Barley Mucuna 2 10 5 6 3 12 8 9 4 1 7 11 Barley Barley 11 1 2 9 4 12 5 6 3 8 Mucuna 6 8 5 10 7 1 12 2 Barley 2 4 10 9 7 1 3 11 Mucuna Mucuna Drip irrigation 4 7 1 10 9 8 11 6 12 2 5 3 1 4 10 8 3 7 5 11 12 6 2 9 Mucuna 12 2 8 3 9 10 1 5 6 4 7 11 11 3 4 9 Barley 6 5 7 10 8 3 11 2 12 4 9 1 12 5 8 6 Mucuna 11 1 2 5 4 10 3 7 9 8 6 12 Barley 5 11 4 8 1 3 7 12 7 10 2 1 7 4 10 6 5 8 3 9 11 12 One block will measure 77m long by 21m wide. 9 6 2 10 SECOND EXPERIMENT Objective of this experiment is to evaluate the following: The performance of different levels of vermin-compost on the quality and quantity of onion under different levels of salinity. The parameters that will be studies will be: (a) The effects of vermicompost on soil aggregate formation and stabilization. (b) The effects of vermicompost on salinity and sodicity levels. (c) The hydraulic conductivity of the different soils under the different vermicompost levels 7 Four levels of vermicompost will be tested, randomized and replicated 4 times in 4 blocks. Four soil blocks will be used as per the level of salinity and sodicity as determined during the site characterization. Block1 Block2 V1 V3 V3 V2 V2 V4 V1 V4 Block 3 Block 4 V3 V2 V4 V3 V1 V4 V2 V1 THIRD EXPERIMENT The third experiment will be done to determine the most suitable high value crops under the climatic conditions of the area. 5 spices will be tested under the most promising soil amendment practices. The 5 spices will be replicated three times at 4 sites. STATISTICAL ANALYSIS Data will be examined by ANOVA using the general linear model using the Statistical Analysis System (SAS) version 8.1 of the SAS institute Inc. Cary, NC, USA. Separation of means will be subjected to Tukey’s honestly significant difference test (Steel and Torrie, 1960). 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