Fly ash effect on improving soil properties and rice productivity in Korean paddy soils
Introduction
Rice is the main crop in Korea, where paddy soils are generally characterized by low pH values and low levels of available Si. In the 1990s, average values for pH and available SiO2 were 5.6 and 72 mg kg−1, respectively, which were lower than the optimum ranges of 6.0–6.5 and 130–180 mg kg−1 defined by the Rural Development Administration (RDA, 1999).
The rice plant requires high levels of silica, which increases resistance to pathogens and lodging (Mengel and Kirkby, 1987, Deren et al., 1994) and stimulates the absorption of elements such as N, P, and K (Hu and Wang, 1995). Korea has historically experienced a lack of available Si in paddy soils. Silicate fertilizer in the form of by product slag from iron manufacturing is now supplied at 4-year intervals by the Korean government, which is not adequate. Therefore, an alternative source of cheap Si is currently required.
Fly ash from coal combustion is a glassy material with a very high available Si content (Adriano et al., 1980). In 1997, approximately 3.7 million tons of waste fly ash were produced in Korea, and production could reach 6 million tons by the year 2010 (Cha et al., 1999). Most electrical power stations in Korea import bituminous coal from various areas of world. The addition of alkaline fly ash, which has a pH over 9.0 (Cha et al., 1999), can reduce soil acidity to a level suitable for agriculture (Moliner and Street, 1982) and can increase the availability of Si, Na, K, Ca, Mg, B, S and other trace nutrients (Elseewi et al., 1981, Druzina et al., 1983, Wong and Wong, 1989, Ko, 2000). The commercial use of fly ash as a fertilizer in crop production is uncommon in most countries, because coal ashes may also contain non-essential elements that adversely affect crop, soil and groundwater quality (e.g., As, B, Cd, Se) (Adriano et al., 1978, Adriano et al., 1980, Page et al., 1979). Despite potential negative effects on environmental quality, coal continues to be the prime source of energy in Korea. Hence, the disposal of fly ash is likely to remain a serious issue. The use of fly ash in the manufacturing of cement and concrete is beginning in Korea, but even if this industry becomes prosperous, a large portion of the ash will require other environmentally friendly uses. The present investigation was carried out to determine the effect of fly ash on improving soil properties and rice productivity in Korean paddy soils.
Section snippets
Experimental site and treatment
A fly ash was collected from the thermal power plant located at Hadong, in southern Korea (Table 1). To determine the effect of the application of fly ash on rice, paddy soils were selected in Yehari (35°8′ N and 128°4′ E) which belonged to the Pyeongtaeg series (a somewhat poorly drained silt loam) and Daegok (35°14′ N and 128°12′ E) which belonged to the Nagdong series (a somewhat excessively drained loamy fine sand) in Jinju, Geyongnam, in southern Korea. Experimental plots, 100 m2 (10 m × 10 m)
Soil properties
The amended soils showed only slight increases in pH (<0.5 units) following fly ash application, but the available SiO2 contents also increased significantly. Background available SiO2 levels in Pyeongtage (Sil) and Nagdong (LS) soils were 59 and 37 mg kg−1, respectively (Table 4). The amount of available SiO2 increased to 88, 90 and 109 mg kg−1 in Pyeongtage (SiL) and 81, 93 and 159 mg kg−1 in Nagdong (LS) following the application of 40, 80 and 120 Mg ha−1 fly ash, respectively. These increases were
Yield response and element uptake
Yields of rice in relation to the amount of fly ash applied are shown in Fig. 2. Using a quadratic response model, rice yields were related to fly ash (FA) application rates as
Rice yield in silt loam = 4124 + 33.6 × FA − 0.187 FA2 (model R2 = 0.761∗∗),
Rice yield in loamy fine sand = 5946 + 28.7 × FA − 0.152 FA2 (model R2 = 0.600∗∗),
Acknowledgement
This work was supported by the Brain Korea 21 project in 2002.
References (54)
- et al.
The adsorption of silica on gibbsite and its relevance to the kaolinite surface
J. Colloid Interface. Sci.
(1976) - et al.
Lodging reduces yield of rice by self-shading and reductions in canopy photosynthesis
Field Crops Res.
(1997) - et al.
Germination and seedling growth of vegetable crops in fly ash amended soils
Agr. Ecosyst. Environ.
(1989) - et al.
Growth and elemental composition of corn and bean seedlings as influenced by soil application of coal ash
J. Environ. Qual.
(1978) - et al.
Utilization and disposal of fly ash and other coal residues in terrestrial ecosystem. A review
J. Environ. Qual.
(1980) - et al.
Cadmium availability to sudangrass grown on soils amended with sewage sludge and fly ash
J. Environ. Qual.
(1982) - et al.
Plant uptake and phytotoxicity of boron in Australian fly ashes
Plant soil
(1985) Organic carbon
- Ayers, R.-S., Westcot, D.-W., 1985. Water quality for agriculture. FAO. Irrig. Drain. Paper No....
Nutrient Deficiency and Toxicities in Crop Plants
(1993)