EFFECTS OF COMPLEMENTARY USE OF RICE HUSK ASH WITH DIFFERENT ORGANIC MANURE SOURCES ON SOIL PHYSICAL PROPERTIES, SOIL ORGANIC CARBON STOCK, GROWTH AND YIELD OF MAIZE (Zea mays)


ABSTRACT
An experiment was conducted to investigate the effect of complementary use of rice husk ash with different organic manure sources on soil physical properties, soil organic carbon stock, growth and yield of maize (Zea mays) at the research and teaching farm of Federal College of Agriculture, Ishiagu, during 2017 cropping season. The experiment involves nine (9) treatments including the control which were as follows: control at 0ton, poultry manure (PD) 10t/ha, swine manure (SW) at 10t/ha, cow dung (CD) at 10t/ha, rice husk dust (RHD) at 10t/ha, poultry dropping+ rice husk ash (PD +RHA) at 5 t/ha +5t/ha each, swine manure + rice husk ash (SM +RHA) at 5t/ha +5t/ha each, cow dung + rice husk ash(CD +RHA) at 5t/ha+5t/ha each, rice husk dust + rice husk ash (RHD+RHA) at 5t/ha+5t/ha each. The treatments were laid in a randomized complete block design (RCBD) and replicated three times. Data on plant height, number of leaves, germination count, stem girth were collected at 2, 4, 6, and 8 weeks after planting (WAP), while the weight of fresh cobs with husk, weight of fresh of cobs without husk, weight of dried cobs, weight of shelled grain were determined after harvest and all the data were analyzed using analysis of variance (ANOVA).  Results showed that poultry dropping when complemented with rice husk ash (PD+RHA) gave the highest significant (p<0.05) increase on the maize growth parameters. It was also obtained that the yield components though not significant (p<0.05) but were increased higher in plots treated with PD+RHA compared to other treated plots and the control. The shelled grain yield ranged from 0.667 to 0.046. The results indicated that the macro-aggregates >2.00 mm were significantly increased higher in the control plots while PD treated plots gave the least value of 2.03 mm. The micro-aggregates <0.25 mm were significantly (p<0.05) improved higher in plots amended with poultry dropping. The soil bulk density was significantly (p<0.05) decreased generally by the application of soil amendments. Soil pH, organic carbon and total nitrogen were significantly improved by soil amendments within the period of study. It was also recorded that the saturated hydraulic conductivity, water retention, water stable aggregate, and mean weight diameter were significantly (p<0.05) improved by the manure application.






CHAPTER ONE
1.0                                       INTRODUCTION
1.1   Background of the Study         
Maize (Zea mays L.) is a tall monoecious annual grass with overlapping sheaths and broad conspicuously distichously blades. The plants have staminate spike-lets in long spike-like racemes that form large spreading terminal panicles (tassels) and pistillate inflorescences in the leaf axils in which the spikelet’s occur in 8 to 16 rows, approximately 30 cm long, on a thickened, almost woody axis (cob).
The whole structure (ear) is enclosed in numerous large foliaceous bracts and a mass of long styles (silks) protrude from the tip as a mass of silky threads (Hitchcock and Chase, 1999). Pollen is produced entirely in the stimulate inflorescence and ear, entirely in the pistillate inflorescence. Maize is wind pollinated and both self and cross pollination is usually possible.
Maize is cultivated worldwide and represents a staple food for a significant proportion of the world's population. No significant native toxins are reported to be associated with the genus Zea (International Food Biotechnology Council, 1990).Maize is a staple food crop only in many parts of the tropics and important food for livestock. The grain is used industrially for starch and oil extraction (Nwite et al., 2011).
Inspite of the contributions of the crop to the country’s economic development, the production is still far below the demand of the growing population. In recognition of the current global food crises, Nigeria currently pursues policy of expanding the land area under cultivation as well as intensifying crop production by continuous cropping system, of which maize is included (Nwite et al, 2012).
 Poor soil fertility and land degradation are major limitations to this policy of increased food production and food security in sub-Saharan Africa, placing many smallholder farmers in a vulnerable position (Okonkwo  et al., 2011). Smallholder farms size in Nigeria are usually cultivated continuously without adequate replenishment of soil nutrients (Mureithi et al., 2004, Okalebo et al., 2006).When a soil is cultivated continuously its productivity gradually decreases due to depletion of organic matter which is believed to be a reservoir of plant nutrients (Eneje and Uzoukwu, 2012; Ebaid and EL-Refael, 2007). Cropping may lead to erosion and leaching of soil nutrients which in turn, adversely affect the physical properties of the soil and are strong limitations to crop production (Igwe et al., 1995).
The above problems have necessitated wide range of technological options for improving soil conservation and land management that are economically viable, ecologically sound, and socially acceptable. These include inorganic fertilizers, crop residue management, green manure, composting, farmyard manure, agro forestry technologies, alley farming, planted fallow, cover crops, and cereal-legumes intercropping or rotation (Buckles et al., 1998).
Over the years, use of chemical (inorganic) fertilizer in crop production has not been sustainable due to its high cost and scarcity, soil acidity, increased soil bulk density, low water infiltration rate and nutrient imbalance (Ojeniyi, 1995; Nottidge et al., 2005). Thus, the needs to investigate alternative sources of nutrients that will be less damaging to the soil environment become imperative. Hence, the recent interest in the use of agricultural wastes (organic manures) by the dominant resource poor farmers (Ayeni et al., 2008, Ayeni and Adetunji 2010). Organic manures such as crop residues and animal excreta are used directly or composted. However due to high quantity needed, adequate quantity of an organic waste may not be obtained, hence the farmers often apply different wastes combined. Since the wastes are of different quantity and nutrient composition, their combined use is expected to have positive cumulative and complementary effects in nutrient supply and improvement of crop yield (Ayeni et al., 2008). Soils in South eastern Nigeria are generally characterized by low pH and exchange capacity, poor buffering capacity and rapid loss of fertility on intensive cultivation (Nwite et al., 2008). Ashes generally have good acid-neutralizing capacity and ability to supply the soil with basic elements (Nwite et al., 2011), hence the reason behind the complementary use of ash material with other organic manure sources. It has been shown that ash could be used to counteract natural and anthropogenic acidification of soil and loss of nutrients (Erriksson, 1998; Serafinelion, 2002).
Maintaining or increasing soil organic matter (SOM) is critical to achieving optimum soil function. In many parts of the world, organic wastes represent an inexpensive and plentiful resource for the treatment of soil quality. However, investigation of the options for the application of organic wastes and their efficacy in improving soil condition are needed to assess their potential to partially or fully replace inorganic fertilizers. Soil organic carbon (SOC) is the most frequently reported soil attribute from long-term agricultural studies and is commonly selected as the key indicator of soil quality and agronomic sustainability because of its impact on other physical, chemical and biological elements of soil quality (Reeves, 1997). Long-term fertility experiments (LTFE) play an important role in understanding the complex interaction involving plants, soils, climate and management practices and are the primary source of information to determine the effects of cropping systems, soil management, fertilizer use, and residue utilization on the quantitative and mechanistic changes on soil quality as well as on SOC pools (Leigh and Johnston, 1994; Rasmussen et al., 1998).
Soil organic carbon (SOC) sequestration contributes to the mitigation of greenhouse gas emissions and to the improvement of soil fertility (Lal R 2004). Net SOC sequestration is the balance of organic carbon inputs into the soil (via crop residues, organic amendments in compost, animal manure, etc.) and organic C decomposition by soil microbes. SOC sequestration efficiency is commonly expressed by the relationship between annual carbon(C) input and SOC accumulation rate, which is an indicator of soil C sequestration ability (McLauchlan 2006). Therefore, information about the carbon sequestration efficiency is useful for seeking high efficiency management strategies of enhancing the SOC stock and soil fertility. Ash application may help in coping with the low nutrient levels in this soil. Witt et al.(2005) showed that nutrient management should be offered great attention in order to obtain appreciable yield.
Rice husk is one of the most widely available agricultural wastes in many rice producing countries around the world. It is of little commercial value and because of its high valuable for its roles in increasing soil fertility and improving soil characteristics by its addition of organic matter to the soil (Njoku et al., 2011). Rice husk removal during rice refining, creates disposal problem due to less commercial interest. Also, handling and transportation of rice husk is problematic due to its low density (Kumar et al., 2012). Much of the husk produced from processing of rice is either burnt or dumped as wastes creating great environmental threat to surrounding area where it is dumped. Therefore, agricultural use of rice husk as organic manure is an alternative solution to disposal problem (Giddel and Jivan, 2007).
Organic wastes are those materials such as agricultural wastes, plant debris, animal dung or their by-products used as soil amendments. These kinds of wastes are becoming increasingly important in addressing soil low fertility due to scarcity and high cost of inorganic fertilizers. The local poor resource farmers had long resorted to use of these materials since they are cheap, easily available and environmental friendly. Besides, organic wastes have physical and chemical properties which facilitate aggregation of mineral particles such as clays which in turn influence soil water regime (Mbagwu, 1990). They are also fundamental source of energy for the soil biota and in that way influence many biologically medicated processes in the soil (Stephenson, 1994).
Furthermore, several studies have been carried out and they indicate positive effect of organic wastes on soil. They contain nutrients needed for crop growth and development. Organic matter from such waste improves soil tilt, increase
1.2     Statement of the Problem
Organic matter depletion in tropical soil has been discovered to be rapid. The constant loss of organic matter in the tropical zone has been attributed to high rainfall, high rate of mineralization (because of high microbial activates bush burning and high carbon losses accompanying tillage operation. The rapid depletion of plant nutrients, low organic matters content and poor physical condition to the soil constitute strong limitations to crop production in the area regarded as major food belt of the eastern region.
However, attempts to restore the lost nutrients with the use of organic fertilizers by rural farmers due the above factors in some soils of the area have led to population and acidification of the soils.
Organic matters have being found to improve the physical prosperities of the soil to maintain better tilt and increase water holding capacity (Ogwuwale et al, 2002). Current the combination of different organic matter constituent has been found to improve the productivity of tropical soil more than ordinary use of farm manure.
Furthermore, several studies have been carried out and they indicate positive effect of organic wastes on soil. They contain nutrients needed for crop growth and development. Organic matter from such waste improves soil tilt, increase.
1.3     Objective of the Study
General Objective
The main objective of the study is to determine the complementary use of rice husk ash with different organic manure sources on soil physical properties, soil organic carbon stock, growth and yield of maize.
Specific objective of the study will includes
v To determine the effect of different manure sources on the physical properties of the soil.
v To evaluate the effects of different organic manure sources on the growth and yield of maize.
v To ascertain the effect of different organic manure sources on the soil organic carbon stock.
1.4     Justification of the Study
Soil carbon level usually increases with organic manure application since organic manure contains not only nutrients that are essential for plant growth but also contain carbon. Improving the soil carbon stock through organic amendment is a good strategy to mitigate climate change as well as giving solution to soil degradation problem by decreasing the carbon concentration in atmosphere. The study aimed at proffering solution to options in mitigating climate change and improvement of degraded soils in south eastern Nigeria through the use of organic amendments particularly organic manure source.





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