Fly Ash Use in Agriculture A Perspective

INTRODUCTION Fly ash has a potential in agriculture and related applications. Physically Fly Ash occurs as very fine particles, having an average diameter of

INTRODUCTION Fly ash has a potential in agriculture and related applications. Physically Fly Ash occurs as very fine particles, having an average diameter of 25>

It was generally observed that both sandy and clayey soils tend to become loamy in texture (Capp 1978) in the U.S. the average silt content in fly ash is about 63.2% (Sharma et. al. 1989) but in India this content ranges from about 16% (IIT, Kharagpur) to 45% (UAS, Raichur).

Modification of bulk density The grain size distribution especially the silt size range of fly ash affects the bulk density of soil. Chang et. al. (1977) observed that among five soil types Reyes silty clay showed increase in bulk density from 0.89 to 1.01 when the corresponding rates of Fly Ash amendment increased from 0 to 100%. But soils with bulk densities varying between 1.25 and 1.60, a marked decrease in bulk density was observed by the addition of Fly Ash. Page et. al (1979, 1980) reported that Fly Ash amendment to a variety of agricultural soils tend to decrease the bulk density. Optimum bulk density in turn improves the soil porosity, the workability of the soil, the root penetration and the moisture retention capacity of the soil.

Water holding capacity of soil The application of Fly Ash has been found to increase the available water content of loamy sand soil by 120% and of a sandy soil by 67% (PAU, Ludhiana). RRL Bhopal reported that application of Fly Ash increase the porosity of Black Cotton Soil and decreases the porosity of sandy soils and thereby saves irrigation water around by 26% and 30% respectively. Chang et. al. (1977) reported that at an addition of 8% by weight Fly Ash, increased the water holding capacity of soil. They also reported that soil hydraulic conductivity improved at lower rates of Fly Ash application but deteriorated when the rate of Fly Ash amendment exceeded 20% in calcareous soils and 10% in acidic soils. This improvement in water holding capacity is beneficial to the plants especially under rainfed agriculture.

Soil pH In India most of the Fly Ash produced is alkaline in nature. Hence an application of these to agricultural soil increases the soil pH. This property of fly ash can be exploited to neutralize acidic soils (Elseewi et. al. 1978; Phung et. al. 1978). Jastrow et. al. (1979) reported that while addition of fly ash improves soil pH on one hand, it simultaneously adds essential plant nutrients to the soil on the other hand. Page et. al. (1979) observed that experiments with calcareous and acidic soils revealed that fly ash addition increased the pH of the former from 8.0 to 10.8 and that of the latter from 5.4 to 9.9. It has also been reported that the use of excessive quantities of fly ash to alter pH can cause increase in soil salinity especially with unweathered Fly Ash (Sharma et. al. 1989).

Some fly ashes are acidic which may be used for reclamation of alkaline soils. In one of the project sites of FAM at Phulpur, IFFCO has done some work on the reclamation of alkaline soils and observed that the pH of these soils could be brought to near neutral status using these acidic fly ashes.

Effect on soil crust

Fly ash application helps in reducing surface encrustation, which is a problem in red soils (CAS, Raichur). This effect in turn can enhance soil aeration and help in improvement of germination of plants grown on it.

Effect on growth and yield of crops

The positive impact of Fly Ash application on growth & yield of crops has been reported by various agencies. Some of which are given below: Regional Research Laboratory (RRL) Bhopal reported that on an average in comparison to control around 50-60% more yield of Brinjal, around 45% more yield of potato & pea, around 40% more yield of tomato and around 29% more yield of cabbage were recorded in Fly Ash treated plot when Fly Ash was applied @25% of soil. Punjab Agriculture University (PAU) observed that application of Fly Ash @10t/ha increased the yield of wheat from 21.5 q/ha to 24.1 q/ha and that of cotton from 1245 kg/ha to 1443 kg/ha. They have also been found that Fly Ash application @10% by weight increased the dry matter yield of moong from 3.80 gm to 7.36 gm and Fly ash addition from 0 to 80 t/ha increased the yield of paddy from 61.82 q/ha to 63.58 q/ha. College of Agriculture, Raichur observed that the yield of groundnut was increased from 24.1 q/ha to 31.9 q/ha with the application of fly ash @20 t/ha.

View of Groundnut Crop grown on fly ash treated soil at IIT-Kharagpur Forestry and Floriculture species on an Ash Pond (By TERI at BTPS Badarpur) Promising indications were obtained from the preliminary research findings (highlights of which have been given above). A need was felt for collection of a set of empirical data through scientifically designed trials using standard procedures and protocols in a coordinated manner at the national level on the benefits and possible adverse effect of fly ash application in agricultural fields. Fly Ash Mission (FAM) along with its associate agencies has taken up a large number of demonstrative trials (more than 50) at various sites at dispersed locations across the country under varied agro-climatic conditions on a spread of crops, forestry & horticulture species. These trials are being done with varied dose ranges based on the results of the part research experiences of respective centers at their sites. Even upto 100% ash bodies have been used to obtain the extreme effects. The tables 2 & 3, would provide a picture of the locations, plant types and soil types and fly ash dose ranges which have been covered under Fly Ash Mission projects.

Table 2: Field crops & vegetables projects undertaken by FAM S. No.SoilFly ash doses rangeCrops & No. of SitesLocationExecuted by 1Alluvial Soil0-200 t/haRice, wheat (2)Farakka CFRI, Dhanbad 2Alluvial Soil0-100 t/haMustard, jute (1)Farakka CFRI, Dhanbad 3Laterite Soil0-200 t/haRice (5), wheat (4)Bakreshwar CFRI, Dhanbad 4Laterite Soil0-100 t/haMustard, Potato, Lentil (1)Bakreshwar CFRI, Dhanbad 5Black Soil0-50 t/haSugarcaneChidambaramAnnamalai University 6Laterite Soil0-150 t/haGroundnutNeyveliAnnamalai University 7Laterite Soil0-100 t/haSugarcaneNeyveliAnnamalai University 8Black Soil0-150 t/haRice-Green Gram (1)SathamangalamAnnamalai University 9Black Soil0-120 t/haCotton-Rice (1)VellampudugaiAnnamalai University 10Lateritic Soil0-10 t/haRice-Groundnut (3)Kharagpur IIT-Kharagpur 11Lateritic Soil0-20 t/haRice, Groundnut-Mustard (1)KharagpurIIT-Kharagpur 12Lateritic Soil0-30 t/haMustard-Rice (1)KharagpurIIT-Kharagpur 13Lateritic Soil0-10 t/haRice (2)-Mustard, Groundnut, Potato (1)Balarampur, Gholghoria, BurariIIT-Kharagpur 14Lateritic Soil (Red)0-80 t/haSunflower-Groundnut (2)Raichur CAS, Raichur 15Black Soil0-80 t/haSunflower-Maize (2)Raichur CAS, Raichur 16Alluvial Soil0-650 t/haTomato (1), Cabbage (1), Potato (1), wheat (2), Pea (1)- Maize(6), Wheat-Maize (2)Dhodhar, Nilgiri, Rihand NagarRRL, Bhopal 17Alluvial Soil0-650 t/haSunflower (1), tomato (1), Potato (1), Wheat (1), Berseem (1), Red Gram (1), Maize (4), Rice (1)Nilgiri, Rihand NagarRRL, Bhopal 18Alluvial Soil0-40/0-80 t/haRice-Wheat (1), Cotton-Wheat (1), Sunflower-Maize (1), Wheat-Rice (1)Ropar, BhatindaPAU Ludhaina 19Alluvial Soil0-12 t/haWheatRopar (Astalpur)PAU Ludhaina 20Alluvial Soil100% ash body with 7.5 cm soil coverArhar-Wheat (1)BhatindaPAU Ludhaina 21Black Soil0-640 t/ha (Residual Effect)Wheat-Maize, Soyabean-Maize, Lemon Grass (1)SarniRRL, Bhopal 22Alluvial Soil0-640 t/haMaize-Onion, Rice-Sunflower (1)AngulRRL, Bhopal Table 3: Forestry, Land Reclamation projects undertaken by FAM S. No.Soil/Land TypeFly ash doses rangeTree Species & No. of Sites LocationExecuted by 1Laterite Soil0-240 t/haEucalyptus (1)Chaudwar, CuttakTCRDC, Patiala 2Laterite Soil0-24% of pit volume Eucalyptus, Acacia auriculiformis, Casurina equisetifolia, Acacia mangium (1)Durga Prasad, CuttackTCRDC, Patiala 3Alkali-Saline Eroded land ( in Arid Zone)0-20% v/wEucalyptus, Zizyphus, Jojoba (1)JaipurTERI, New Delhi 4Ash Pond-Melia azadirach, Delbergia Sisso, Eucalyptus sp., Populus deltoides(1)BadarpurTERI, New Delhi 5Low Fertile Soil1/3 Pit volumeCeiba pentandra, Melia azadirach, Cassia siamea, Erythrina indica, Cassia glauca, Bauhinia purpurea, Putranjiva ,Pongamia glabra ,Thevetia elifera (1)New Delhi TERI, New Delhi 6Usar 0-5%Rice, Wheat (1)DailapurIFFCO, Phulpur 7Usar 0-5%Rice ,mustard (1)TardihIFFCO, Phulpur 8Usar 0-5%Rice, Wheat (1)YakubpurIFFCO, Phulpur 9Usar 0-6%Rice, Wheat (1)PurisudiIFFCO, Phulpur 10Usar 0-6%Rice, Wheat (1)ParasinpurIFFCO, Phulpur 11Usar 0-6%Rice, Wheat (1)MobarukpurIFFCO, Phulpur 12Ash Pond-Rajnigandha ,Tagetus, Carnation, Palmarosa, Sunflower (1)Badarpur, New DelhiTERI, New Delhi Flyash for reclaiming saline alkaline soil – Rice Crop at IFFCI, Phulpur Flower at Ash Pond (by TERI at Badarpur) These trials have been scientifically designed to collect empirical data on effect of fly ash application on soil, plant and natural ground water near the application site. Indicative monitoring is being done of the soil, plant produce, macro & micro nutrient status including the trace & heavy metal status and also the changes in the natural radioactivity level (if any as a result of application of fly ash) on soil, plant and natural ground water near the trial site. The aspect of the nutritional quality of produce grown in fly ash treated soils if also being addressed in a special project by the National Institute of Nutrition. Institute of Physics, Bhubaneswar is testing the samples of all FAM project sites for some heavy metals and radionucleide levels. More than 1000 samples have been tested so far. At most places the levels appear to be in the normal range. Highlights of the some the important findings from these trials are as follows: Effect on crop growth and yield:

In rice-groundnut cropping system, application of Fly ash @ 10 t/ha to both the crops increased grain yield of rice on an average by 14% and pod yield of groundnut by 26% over control (IIT-Kharagpur)

Application of Fly Ash @ 10 t/ha in combination with organic and inorganic sources either in one or both the seasons in rice-groundnut cropping system increased grain yield or rice and pod yield of groundnut significantly over application of only chemical fertilizer to both the crops (IIT-Kharagpur)

The treatment combination fly ash @ 10 t/ha alongwith Paper Factory Sludge (@ 15 t/ha) & chemical fertilizer (CF) applied to rice and only CF to potato increased grain yield of Rice and tuber yield of Potato significantly over CF applied to both crops in Rice-Potato cropping system. (IIT-Kharagpur)

In Rice – Mustard cropping system, application of Pond ash @ 10 t/ha in combination with organic and inorganic sources to rice and subsequent mustard with CF alone increased yield of rice by 13-15 % and seed yield by 15-18% as compared to the treatment of similar combination but without Pond Ash.(IIT-Kharagpur)

Use of Pond ash/Fly ash either in splits or as one time application along with organic and inorganic sources were equally effective in increasing grain yield of rice and seed yield of mustard, as compared to the treatment without Pond ash / Fly ash. (IIT-Kharagpur)

At College Of Agriculture -Raichur yield of Sunflower was increased by about 25% in red soil under rained as well as irrigated conditions when fly ash was applied @ 60T/ha along with 20t/ha FYM.

More than 70% increase in yield of groundnut was observed when fly ash was applied @ 30 t/ha along with FYM @ 20 t/ha at CAS Raichur.

The yield of maize also increased by about 35% of present when Fly Ash was applied @ 30 t/ha along with FYM @ 20 t/ha (CAS Raichur).

The performance efficiency of both dry fly ash and pond ash in respect of crop growth parameters (yield & improvement in physical and chemical properties of soil was found to be similar by CFRI, Dhanbad in their studies at Farakka & Bakeraswar). Best grain & straw yield of both paddy and wheat crops were observed 200 t/ha pond ash dose (20-40% increases were observed).

Paddy & Wheat crops grown with Fly Ash showed early maturing tendencies at Farakka

Annamalai University, in their trials found that the application of 100 t/ha of Lignite Fly Ash (LFA) did not adversely affect the germination of seeds of Rice, Green-gram, Groundnut, Sugarcane or Cotton. Satisfactory levels of germination were observed and these were found to be at par with those in control plots (where no Fly Ash/ Pond Ash was applied).

Annamalai University also reported yield increases due to LFA application in eight out of twelve of the field trials (with LFA application between 4-120 t/ha) showing a range of 8% to 36% increase in yield of produce (over control).

Significant yields increases were seen in 2nd and 3rd crop of Groundnut at 10t/ha LFA. Increasing the dose of LFA to 100 t/ha significantly increased pod yield in the first crop itself. (Annamalai University).

Effect on soil health:

In rice based cropping system, application of Fly ash/ Pond Ash @ 10 t/ha alongwith organic and inorganic sources wither in one season or in consecutive seasons improved physical properties of soil through decreasing its bulk density and increasing its water holding capacity and porosity (IIT-Kharagpur)

Being alkaline in nature, application of Fly ash/ Pond Ash @ 10 t/ha in combination with organic and inorganic sources increased pH of acid-latertic soil to a considerable extent (IIT-Kharagpur)

In rice based cropping system, repeat application of Fly Ash/ Pond Ash @ 10 t/ha in combination with organic and inorganic sources raised the fertility status of soil, as compared to the treatment of similar combination but without Fly ash/ Pond ash (IIT-Kharagpur)

In general, the available heavy metal status of soil decreased under Fly ash/ Pond Ash based treatments (IIT-Kharagpur)

Application of Fly ash/ Pond Ash increased soil dehydrogease activity, which was more discernible in aerobic condition than flooded/reduced soil condition (IIT-Kharagpur)

RRL, Bhopal (in the project site Dhodhar, Rihand Nagar) found that the nutrient availability was enhanced in soil where 25% coal ash was applied at one time and in those plots wherein addition to the 25% ash was made initially and 5% addition was made every year.

At CAS, Raichur pH & Electrical Conductivity of soil did not differ significantly due to application of different fly ash levels.

CAS, Raichur also found that the combined application of Fly Ash & FYM had a beneficial effect on the fertility status of soil the content of total lead, arsenic and selenium did not change significantly due to application of recommended dose(upto 60 t/ha) of Fly Ash. However, at higher rate of applications the contents of these toxic elements increased marginally.

CAS, Raichur found that the content of toxic elements was lesser in red soils as compared to black soils.

RRL, Bhopal in its trials at Nilgiri, Rihand Nagar (Land- fill site) found that the primary & secondary nutrients were increased in ash filled plots. The heavy metals like Co, Ni, Cr, Pb, Cd where found to be below detectable limits.

CFRI, Dhanbad found that the application of alkaline Fly Ash (pH 8.3) helped in neutralizing the acidic red soil (pH 5.01) making it more productive and suitable for cultivation. It also helped in improving the utilisation efficiency of NPK fertilizer.

Annamalai University found hat application of Lignite Fly Ash in various soil types showed the following types of soil modifications: Neutralising soil pH Increasing EC Increasing available levels of potassium, sulphur and boron.

Effect on quality of yield and uptake of nutrients and toxic elements:

In rice based cropping system, application of Fly Ash/ Pond Ash @ 10 t/ha in combination with organic and inorganic sources increased the concentration of macronutrients (N, P, CA and Mg) in rice grain and edible part of the subsequent crops (groundnut, potato and mustard) as compared to the treatment of similar combination, but without Fly Ash/ Pond Ash (IIT-Kharagpur)

Decrease in heavy metal concentration in grain or edible part of the different crops under Fly Ash/ Pond Ash based treatment is due to dilution effect of these elements through increased grain/edible yield (IIT-Kharagpur)

Radionucleide levels in grain/edible part of rice, groundnut, potato and mustard varied under Fly Ash/ Pond Ash based treatments as compared to the treatments without it and indicated no adverse effect of Fly ash/ Pond Ash (IIT-Kharagpur).

The nutritional value of agricultural produce grown on ash-filled land-fill sites in terms of protein & carbohydrates were found to be comparable with the National Institute of Nutrition-Standards (RRL, Bhopal- trials at Nilgiri, Rihand Nagar)

Effect on ground water:

Application of Fly Ash/ Pond Ash in combination with organic and inorganic sources released lower quantity of Fe and Mn to ground water as compared to the treatment without Fly Ash/ Pond Ash (IIT-Kharagpur).

In ground water samples the level of 286Ra was decreased, 228Ac remained unchanged under Fly Ash/ Pond Ash based treatment as compared to the treatments without it, indicating poor leaching of radionucleide to ground water. Thereby the ground water quality due to application of Fly Ash/ Pond Ash remained unaffected with respect to radionucleide contamination (IIT-Kharagpur).

Other effects:

The crops grown under Fly Ash/ Pond Ash based treatment were observed to be resistant to disease, insect, and pest infestation as compared to the crops grown without Fly Ash/ Pond Ash (IIT-Kharagpur).

At Bakreshwar, in farmers’ field trials the farmers have observed that the crops grown in Fly Ash treated plots were relatively more resistant to pest attack in compared to those in control plots.

Farmers were enthused to take `groundnut’ crop in rabi using Fly Ash as compared to the traditional `boro rice’ crop at Kharagpur for a better `cost-benefit ratio’. Use of Fly Ash as a Mine Soil Amendment The physical effects of fly ash additions on soils were discussed earlier, but relatively high loading rates (> 100 tons per acre) are generally required to significantly influence soil physical properties such as water holding capacity and aggregation. In most instances, fly ash is added to soils primarily to affect chemical properties such as pH and fertility, and loading rates are limited by chemical effects in the treated soils. Plant growth on fly ash-amended soils is most often limited by nutrient deficiencies, excess soluble salts and phytotoxic B levels (Page et al., 1979; Adriano et al., 1980). Fly ash usually contains virtually no N and has little plant-available P. However, newer power plants may be adding ammonia as a flue gas conditioner to limit NOX emissions which may lead to some plant-available N. Application of fly ash to soil may cause P deficiency, even when the ash contains adequate amounts of P, because soil P forms insoluble complexes with the Fe and Al in more acidic ashes (Adriano et al., 1980) and similarly insoluble Ca-P complexes with Class C ashes. Amendment of K-deficient soil with fly ash increases plant K uptake, but the K in fly ash is apparently not as available as fertilizer K, possibly because the Ca and Mg in the fly ash inhibit K absorption by plants (Martens et al., 1970). In some cases, soils have been amended with fly ash in order to correct micronutrient deficiencies. Acidic-to-neutral fly ash has been found to correct soil Zn deficiencies, although alkaline fly ash amendment can induce Zn deficiency because Zn becomes less available with increasing pH (Schnappinger et al., 1975). Fly ash application has also been shown to correct B deficiencies in alfalfa (Plank and Martens, 1974). In some cases, plant yields after fly ash application have been reduced because of B toxicity (Martens et al., 1970; Adriano et al., 1978). Soil amendment with fly ash to alleviate B deficiencies should be carefully monitored in order to avoid B toxicity. Fly ash often contains high concentrations of potentially toxic trace elements. Plants growing on soils amended with fly ash have been shown to be enriched in elements such as As, Ba, B, Mo, Se, Sr, and V (Furr et al., 1977; Adriano et al., 1980). Although trace amounts of some of these elements are required for plant and animal nutrition, higher levels can be toxic. Highly phytotoxic elements often kill plants before the plants are able to accumulate large quantities of the element; which limits their transfer to grazing animals. Elements such as Se and Mo, however, are not particularly toxic to plants and may be concentrated in plant tissue at levels that cause toxicities in grazing animals. Soils amended with high rates of fly ash may accumulate enough Mo to potentially cause molybdenosis in cattle (Doran and Martens, 1972; Elseewi and Page, 1984). Finally, amendment of soil with fresh fly ash may increase soil salinity (reported as soluble salts or electrical conductance-EC) and associated levels of soluble Ca, Mg, Na, and B. Incorporation of 80 T/A unweathered fly ash from a Nevada power plant increased soil salinity 500 to 600% and also caused a significant increase in soluble B, Ca, and Mg (Page et al., 1979). Fly ash that has been allowed to weather and be leached by rainfall for several years generally has much lower soluble salt and soluble B concentrations and is more suitable for use as a soil amendment (Adriano et al., 1982). In general, ashes which have been wet-handled in the plant and stored in ponds will be much lower in soluble salts and B than dry-collected ashes. Use of Fly Ash in Acidic Spoil and Coal Refuse Revegetation Alkaline fly ash can aid in the reclamation of acidic spoils and refuse piles, although one-time ash applications do not appear to be effective in maintaining increased pH if pyrite oxidation is not completely stopped and neutralized. The pH of an extremely acidic surface mine soil and a coal refuse bank in West Virginia was initially raised to near neutral by application of high rates of alkaline (pH 11.9) fly ash. Soil pH dropped 1 to 2 units over the next two growing seasons, however, presumably because of continued pyrite oxidation in the spoils and leaching of Ca and Mg oxides from the fly ash (Adams et al., 1972). Jastrow et al. (1981) used fly ash as an alternative to lime in a greenhouse experiment involving acidic coal refuse. The initial pH of the refuse was 3.5. Amendment with fly ash raised the pH to 4.8, but it dropped to 4.2 by the end of one growing season. In another greenhouse experiment, the application of fly ash to extremely acidic coal refuse resulted in a higher pH and significantly increased barley yields (Taylor and Schumann, 1988). Boron toxicity has been observed in plants grown on fly ash-amended mine spoils, although in some cases toxicity symptoms were apparent but yields were not reduced (Adams et al., 1972; Keefer et al., 1979; Taylor and Schumann, 1988). Jastrow et al. (1981) implicated Mn, Zn, and V toxicity as possible factors in reduction of tall fescue yields on fly ash-amended coal refuse. Coal refuse often contains high levels of trace elements and fly ash application can raise the concentrations of these elements to toxic levels, especially if pH is not controlled. Return to Table of Contents Studies on possible negative effects of Fly Ash application Ground Water

Fly Ashes contain a small amount of trace and heavy metals which may percolate down and pollute ground water. The solubility of these elements is

At Central Fuel Research Institute (CFRI), Dhanbad it was observed that the quality of ground water did not change with the application of flyash and all the parameters including the trace and toxic metal contents were within the permissible limits. Some other research organisations also observed that Fly Ash has no significant polluting effect on ground water.

Uptake of heavy metals and toxic elements by plants

Fly Ash has ppm level concentration of heavy metals, when applied to soil these elements may get absorbed by plants grown on it which may ultimately enter into food chain. However, the absolute quantities of these elements in flyashes are low which may not result into negative effect. The data on trace element uptake and accumulation by plant are limiting. Despite fairly intensive research over the last 25 years, the data on trace element accumulation are rather sketchy and inconsistent. Boron in FLy Ash is readily available to plants and investigators consider B to be limiting factor in unweathered Fly Ash utilisation (Townsend and Gillham (1975); Elseewi et.al. 1978; Ciravolo and Adriano, 1979). RRL, Bhopal conducted a study regarding the uptake of heavy and trace metals by some vegetable crops and it was observed that the uptake is quite low and remains within the normal range.

Central Fuel Research Institute, Dhanbad observed that there is no significant differences in uptake of trace & heavy metal between control and Fly Ash treated plots. Although Fly Ash contain a moderate amount of trace and heavy metals, the uptake and accumulation of these by plants in very negligible.

Radionuclides

There have been several reports in the literature on the presence of radionuclides in Fly Ash but studies on their impact have been few (Coles et.al. 1978; Gowiak and Pacynas, 1980). The radiochemical pollution of Uranium and Thorium series is always present in Fly Ash (Eisenbud and Petrow 1964). The concentration of natural Uranium varies from 14 to 100 ppm although in exceptional cases it may be as high as 1500 ppm whereas that of Thorium is less than 10 ppm. The Fly Ash concentrates besides other gaseous and trace metal oxides, several radioactive contaminants like 222Ru & 220Ru (Sharma et.al. 1989). Bhaba Atomic Research Centre, Bombay is of the opinion that most of the Indian coals has very low levels of radioactivity which is well below the hazardous limit. Hence radioactivity of Fly Ash may not be a limiting factor for its application for agriculture purposes. Central Fuel Research Institute, Dhanbad observed that there is no significant uptake of radioactive elements by plants and also that there was negligible cumulative build up of these contaminants in soil when Fly Ash applied for agriculture purposes.

Conclusions: The potential of fly ash as a resource material in agriculture and related areas is now a well-established fact and more and more researchers and `users’ are getting convinced with its utility potential in this field. The major attribute, which makes Fly ash suitable for agriculture, is its texture and the fact that it contains almost all the essential plant nutrients except organic carbon and nitrogen. Although fly ash cannot substitute the need of chemical fertilizers or organic manure it can be used in combination with these (or in some cases may part substitute their requirement) to the to get additional benefits in terms of improvement in soil physical characteristics, increased yields etc. As in the case with fertilizers and any other agriculture input , the amount and method of fly ash application would vary with the type of soil, the crop to the grown, the prevailing agroclimatic condition and also the type of fly ash available. Although, fly ash has many benefits as an input material for agriculture applications, in view of the fear in the minds of many (regarding the levels of natural radioactivity in Fly Ash and/ the characteristic presence of some amounts of heavy and toxic elements in it) there may be some cautions which have to be taken for the time being while using Fly Ash in agriculture. From the information available till now, there appears to be not much ground for concern on these accounts (heavy metals, radioactivity etc) however further confirmatory studies at the ICAR centers would be helpful in bringing out recommendations in this field. Meanwhile there appears to be sufficient ground now for the cautious and judicious use of this useful material, which is otherwise being wasted/ underutilized. References: Arthur, M.F., Zwick, T.C., Tolle, D.A., and Van Varis, P. (1984) Effects of flyash on microbial Co2 evolution from our agricultural soil. Water Air Soil Pollut., 22, 209. 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Elseewi, A.A., Binghman, F.T. and Page, A.L.(1978) Growth and mineral composition of lettuce and swiss chard grown on flyash amended soils, in Environmental Chemistry and Cycling processes, Conf. 760429, Adriano, D.C. and Brisbin, I.L.,Eds., U.S. Department of Commerce, Springfield, VA, 568. Faculty of Agriculture, Annamalai University (1999). Interim Report of Fly Ash Mission sponsored project “Selected Technology Project for Fly Ash Disposal and Utilization in Agriculture” (10-03). Fail, J.L. amd Wochok, Z.S. (1977) Soyabean growth on flyash amended strip mine soils. Palnt Soil, 48, 473. Gowiak, B.J. and Pacyna, J.M. (1980) Radiation dose due to atmospheric releases from coal-fired power stations. Int.J. Environ. Stud. 16,23. Gralloway, J.N., Likens, G.E. and Edgeston, E.S.(1976) Acid rain precipitation in the north eastern United States; pH and acidity, Science 194, 722, IIT Kharagpur (1999) Draft report Of Fly Ash Mission sponsored project ” Utilisation Of Fly Ash And Organic Wastes In Restoration Of Crop Land Ecosystem ” submitted to Fly Ash Mission Jastrow, J.D., Zimmerman, C.A., Dvorak, A.J. and Hinchman, R.R.(1979) Comparison of Lime and Flyash as Amendments to Acidic Coal Mine Refuse: Growth Responses and Trace Element Uptake of Two Grasses. Argonne National Laboratory, Argonne, IL, 43. Kumar, V. (1996) Fly Ash Utilisation: A Mission Mode Approach in Ash Ponds and Ash disposal Systems. Raju, V.S., Dutta, M., Seshadri, V., Agarwal, V.K. & Kumar, V., Eds. Narosa Publishing House, New Delhi, 365. Kumar V, Goswami G and Zacharia K A (1999). Fly Ash: Its Influence on Soil Properties. Indian Society Soil Sciences Workshop, 18-21st October 1999, Calcutta Kumar V, Goswami G and Zacharia K A (1998). Fly Ash Use in Agriculture: Issues & Concern. International Conference on Fly Ash Disposal & Utilisation, 20-22nd January, New Delhi. Natusch, D.F.S. (1975) Characteristics of pollutants from coal combustion and conversion process, in Toxic Effects on the Aquatic Biota from Coal and Oil Shale Development, Quarterly Progress Rep. Oct.- Dec., Natural Resources Ecology Laboratory, Colorado State University, Fort Collins, 73, 1975. Padmakaran, P. et.al.(1994) Fly ash and its utilisation in industry and agricultural land development. Research & Industry, 40, 244-250. Page, A.L., Elseewi, A.A. and Straughan, I.R. (1979) Physical and Chemical Properties of flyash from coal-fired plants with reference to environmental impacts. Residue Rev., 7, 83. Page, A.L., Elseewi, A.A., Lund, L.J., Bradford, G.R., Mattigod, S., Chang, A.C. and Bingham, F.T. (1980) Consequences of Trace Element Enrichment of Soils and Vegetation from the Combustion of Fuels Used in Power Generation. University of Claifornia, Riverside, 158. Phung, H.T., Lund, I.J. and Page, A.L. (1978) Potential use of flyash as a liming material in Environmental Chemistry and Cycling Processes, Conf. 760429, Adriano, D.C. and Brisbin, I.L., Eds. U.S. Department of Energy, 504. Punjab Agriculture University (1993) Utilisation of flyash in agriculture and revegetation of dumping sites. Annual progress report. Rohriman, F.A.(1971) Analysing the effect of flyash on water pollution. Power, 115, 76. RRL Bhopal (1999) Interim report Of Fly Ash Mission sponsored project “Long Term Effect Of Fly Ash On Soil Fertility And Crop Yield” submitted to Fly Ash Mission Sharma, S. et.al. (1989) Flyash dynamics in soil-water systems. Critical Reviews in Environmental Control 19(3), 251-275. Townsend, W.N. and Gillham, E.W.F. (1975) Pulverised fuel ash as a medium for plant growth, in The Ecology and Resource Degradation and Renewal, Chadwick, M.L. and Goodman, G.T., Eds., Blackwell Scientific, Oxford, 287. Vijayan, V. & Ramamurthy, V.S. (1995) Measurement of indoor radon levels in Bhubaneshwar. Bulletin of Radiation Protection, vol (18) No. 1 & 2. Zacharia, K.A.; Kumar, V. & Velayutham, M. (1996) Fly Ash Utilisation in agriculture towards a holistic approach. National Seminar on Fly Ash Utilisation, Neyveli Lignite Corporation Limited, Neyveli.

Horticulture Expert The Growth Driver Of Indian Agriculture Sector

The horticulture sector, with a wide array of crops ranging from fruits and vegetables to orchids and nuts, mushrooms and honey – has been a driving force in the stimulating a healthy growth trend in Indian agriculture. India is currently producing 257.2 million tonnes of horticulture produce from an area of 23 million ha. What is significant is that over the last decade, the area under horticulture grew by about 3.8%per annum but production rose by 7.4% per annum. Given the increasing pressure on land, the focus of growth strategy is on raising productivity by supporting high density plantations, protected cultivation, micro irrigation, quality planting material, rejuvenation of senile orchards and focus on post harvest management to ensure that farmers do not lose their produce in transit from farm gate to the consumers plate.

Fruits:

With a production of 76.4 million tonnes, fruits accounts for about 30 per cent of the total production of horticulture crops. The area under fruit crops during 2011-12 was 6.6 million ha, which is almost 29 per cent of area under horticulture in India. The area under fruit crops has increased from 4.0 million ha in 201-02 to 6.7 million ha in 2011-12 with corresponding increase in production from 43.0 to 76.4 million tonnes. A large variety of fruits are grown in India. Of these, banana, mango, citrus, papaya, guava, grape, sapota, pomegranate, pineapple, aonla, litchi, pear, plum, walnut, etc are important. India accounts for 13 percent of the total world production of fruits and leads the world in the production of mango, banana, papaya, sapota, pomegranate, acid lime and aonla.

The leading fruit growing states are Maharashtra which accounts for 16.0 per cent of production followed by Andhra Pradesh (13.0%), Gujarat (10.0%), Karnataka (9.0%), Uttar Pradesh (8.0%), Tamil Nadu (7.0%) and Bihar (5.0%) altogether contributes for about 68.0 percent of the total fruit production in the country. Banana is the major fruit accounting for 35 per cent of total production followed by mango (4.0%), citrus (11.0%), papaya (6.0%), others (17.7%) in the country. It may also be mentioned that in the Himalayan states of Himachal and J&K the GDP from apples, plums, pears and stone fruits exceeds that of GDP from cereal crops.

Vegetables:

Vegetables are also an important constituent in horticulture sector which are mostly low gestation and high income generating crops. Many vegetables are now grown under protected cultivation like green houses and shade nut houses with a scope for off season production, which fetches remunerative prices.
Vegetables occupied an area of 8.9 million ha during 2011-12 with a total production of 155.9 million tonnes having average productivity of 17.4 tonnes/ha.

Vegetable production registered a quantum jump of 77 per cent between 2001-02 and 2011-12.

More than 40 kinds of vegetables belonging to different groups are grown in India in tropical, sub tropical and temperate regions. Important vegetable crops grown in the country are potato, tomato, onion, brinjal, cabbage, cauliflower, peas, okra, chilies, beans, melons, etc. The leading vegetables growing states are West Bengal which accounts for 15% of production followed by Uttar Pradesh (12%), Bihar (10.0%), Andhra Pradesh (8.0%), Madhya Pradesh (6.5%), Gujarat (6.4%), Tamil Nadu (5.8%), Maharashtra (5.7%), Karnataka (5.0%) and Haryana (3.0%) altogether contributes about 83.4% of the total vegetable production in the country. Among vegetables, potato is the major vegetable accounting for 27.0% followed by tomato (12%), onion (11.0%), brinjal (8.0%), cabbage (5.4%), cauliflower (4.7%), okra (4.0%), peas (2.5%) and others (25.4%) in the country. India is the second largest producer of vegetables after China and is a leader in production of vegetables like peas and okra. Besides, India occupies the second position in production of brinjal, cabbage, cauliflower and onion and third in potato and tomato in the world. Vegetables such as potato, tomato, okra and cucurbits are produced abundantly in the country.

Spices:

India is the largest producer, consumer and exporter of spices and spice products in the world. Over 100 plant species are known to yield spices and spice products among which around 50 are grown in India. India is known as the home of spices producing a wide variety of spices like black pepper, chilies, ginger, turmeric, garlic, cardamom and variety of tree and seed spices. Major spice producing states are Andhra Pradesh (19.0%), Gujarat (15.0%), Rajasthan (14.7%), Karnataka (8.0%), Madhya Pradesh (7.7%) and Tamil Nadu (7.0%). The spice production in India is currently estimated at 5.95 million tonnes from an area of about 3.21milion ha.

The production of spices in the country has registered a substantial increase over the last ten years with average annual growth of 5.8%. Chili is the major spice crop occupying about 25% of area under cultivation and contributing 22% of total spice production in the country. Garlic accounts for 8.0% of area with 21.0% share in production, while turmeric accounts for 6.8% of area with 19.6% share in production.

Flowers:

India has made noticeable advance in the production of flowers, particularly cut flowers, which have a good potential for exports. During 2011-12, floriculture covered an area of 0.32 million ha with a production of 2.6 million tonnes of loose flowers and 75066 million numbers of cut flowers. This sector is generating higher income and employment opportunities especially for women.

While India has been known for growing traditional flowers such as jasmine, marigold, chrysanthemum, tuberose and aster, the commercial cultivation of cut flowers like roses, orchids, gladiolus, carnation, gerbera, anthurium and lilium has become popular in recent times. The important flower growing states are West Bengal, Karnataka, Maharashtra, Andhra Pradesh, Tamil Nadu, Odisha, Uttar Pradesh, Jammu & Kashmir, North East, etc. Major area is devoted to production of marigold, jasmine, roses, chrysanthemum, tuberose, etc. The area under cut flowers having stems has increased manifold. Orchids, anthurium, lilium, gerbera and seasonal bulbous flowers are increasingly being grown both for domestic and export markets.
Growth in Exports:

Not only have these impressive production figures ensured a steady supply for the domestic market, they have also made Indian horticulture exports globally competitive. Over the last decade, there has been a significant improvement in export earnings in horticulture.
The horticulture division is working closely with APEDA and state governments to ensure that infrastructure and institutional support for export is available to ensure that farmers can leverage export markets for higher incomes.

Human Resource Key Performance Indicators For Finance

Finance, always topical , of interest to everyone regardless of sex, color or creed, monetary values that are monitored by key performance indicators. Human resource operators manage and monitor real time trade environments.

Finance is an irremovable sector of the rich tapestry of life some say finance is management of finance in a modular scientific format. It is modular as the science extends across public finance, business finance and personal finance. Astute finance managers implement an array of KPIs which may be supported by real time alerts when trading in real time stock markets and exchanges. Financial modules will depending on the trading environment be subjected to risk factors. Time factors influence the timeline which is best suited to buy or sell finance. When trading in finance a potpourri of commodities one may wish to trade in are gold, reinsurance, government bonds, rubber markets, stock markets and of course currency markets. There is also a number of alternative commodity trading options, as in agriculture and farming both products and livestock are trading commodities. A fisherman generates finance by dealing in fish. A computer manufacturer generates finance by selling computers and PCs. Collectively when
there is no finance there is likely to be no business.

Human resource is one of the backbones of business, similar to the foundations of a building once the foundations are implemented one can then start building on the foundation base platform. Business can be established by adopting similar principles namely set up a human resource team of workers, then build up your business by using the skill sets and benefits that the HR foundations enable you to build a business upon. One element of control in business that requires 365/24/7 monitoring and control are costs, all FDs Financial Directors and Financial controllers need data to process costs, audit sales, audit profit and loss balance sheets. When KPIs are integrated into system data and audit data can be easily delivered to the financial controller. Methods of data transfer include email transfer, SMS delivery, Cloud computer storage gateway delivery etc etc.

Un audited finance should never exist in 2010 all the necessary control and monitoring resources are available for access. Regardless of whether it is a human resource or a computerized system that generates KPIs Key Performance Indicators.

Ensure that all your finance issues are controlled and monitored by specialized computer applications and systems that will manage, monitor and alert control your companies finance division.

There is an inherent synergy between Human Resource, Key Performance Indicators, for Finance. They are that when one combines together HR with KPIs and Finance one achieves a cohesion of three elements that when properly blended into a companies financial business process produce accurate managed data analysis Warning to one and all when dealing in finance it is essential to understand that trading in finance has many risk areas, most risk factors can be negated if one ensures that the necessary management tools and resources are implanted and/or absorbed into the financial control process.

When you control your financial software applications, you will have your company finances under control

Control all your personal and company finances now!

Agriculture Not Be A State Subject

CII today organized a Seminar on Reforms in the APMC (Agricultural Produce Market Committee) Act , and its impact in the Southern States. This is an initiative of the Agri Business Sub-Committee, CII-Southern Region. Speaking at the occasion, Mr. Shankarlal Guru, Chairman-International Society for Agricultural Marketing said Agricultural sector is in urgent need of reforms by the respective State governments to help drive the economy to a higher growth rate that is expected by the policy makers, but a comprehensive agenda for reforms in this crucial sector is yet to emerge. Hence, the need for Agriculture to be made a central subject and not a state subject, thus alienating it from politics, said Mr. Guru. Contract farming should be encouraged as it will help bring technology and modern practices into the agriculture sector – opined Mr. Guru.

The APMC Act in each state of India requires all agricultural products to be sold only in government – regulated markets. These markets impose substantial taxes on buyers, in addition to commissions and fees taken by middlemen, but typically provide little service in areas such as price discovery, grading or inspection. A key impact of this regulation is the inability of private sector processors and retailers to integrate their enterprises directly with farmers or other sellers, eliminating middlemen in the process. Farmers also are unable to legally enter into contracts with buyers. This leaves no incentives for farmers to upgrade, and inhibits private and foreign investments in the food process sector.

Also addressing the audience was Mr. Sivakumar, Chairman Agri Business Sub-Committee, CII-Southern Region and Chief Executive – Agri, ITC Ltd. Said that Agri business in India is at a transition point. Having sailed through the shortage economy to an economy with surplus in grains, it is important that Governments at the Centre and State recognize the need for inclusive growth to take agriculture forward in India. Setting the context for the day’s discussion, Mr. Sivakumar emphasized that in spite of employing about 57% of the population of the country, agriculture on contributes 27% to the GDP of India. This distortion makes agriculture not a lucrative employment generator and hence, keeping with the global view, India needs to carve out opportunities in agri-exports sector. Contract farming and direct marketing to retail chains and processing units are the need of the hour he said.

Regulations to keep pace with these needs are required, which need alternative marketing mechanisms. Hence, reforms in the APMC Act are recommended in various fields, he added.

Making a presentation on “Aligning State Policies with emerging new marketing models”, Prof. S Raghunath from the Indian Institute of Management-Bangalore, emphasized the need for an effective and efficient distribution system for agri-produce and provision for supply-demand transparency. Since the main objective of the APMC Act was to prevent exploitation of farmers by various intermediaries, reforms were required in the Act, with changing face of agriculture and the agricultural supply chain, opined Prof Raghunath. India is the largest producer of vegetable in the world, with a total share of 15% of global produce. 8% of world’s fruits are produced in India, ranking it second in the world market. In spite of this, there is a high cumulative wastage of 40% in India, informed Prof. Raghunath. Inadequate infrastructure and lack of organized supply chain were the main cause for such a disparity, he said. Thus, reforms in this sector need to catch up with the pace of development in the economy and dis-intermediation and participation of organized players in the sector will remove the lacunae, opined Prof. Raghunath.

Centre asks states to amend APMC Act

In a move to allow farmers to directly sell their produce to industry, contract farming and setting up of competitive markets in private and cooperative sector, the Centre has asked the state government to amend the Agricultural Produce Marketing Act.

Under the present Act, the processing industry cannot buy directly from farmers. The farmer is also restricted from entering into direct contract with any manufacturer because the produce is required to be canalised through regulated markets. These restrictions are acting as a disincentive to farmers, trade and industries.

The government has recently approved a central sector scheme titled Development/strengthening of agricultural marketing infrastructure, grading and standardisation.

Under the scheme, credit linked investment subsidy shall be provided on the capital cost of general or commodity specific infrastructure for marketing of agricultural commodities and for strengthening and modernisation of existing agricultural markets, wholesale, rural periodic or in tribal areas.

The scheme is linked to reforms in state law dealing with agricultural markets (APMC Act). Assistance under the new scheme will be provided in those states that amend the APMC Act.

The Centre has asked the state governments to inform as to whether necessary amendments to the APMC Act have been carried out, in order to notify the reforming states for applicability of the scheme.

Along with the Centre, the industry is also interested in the amendment to the APMC Act as it restricts the growth of trade in agricultural commodities.

The policy regime pertaining to internal trade is particularly restrictive. The agricultural sector continues to be hamstrung by a plethora of controls, which were introduced during the era of shortages, said the PHDCCI.

Meanwhile, a decentralised system of procuring wheat and rice would make the Public Distribution System more cost effective, the government has said.

Is Composting The Future Of Landfill Diversion

As there’s pressure from society regarding organic waste collection and the production of greenhouse gases mixed with targets of landfill diversion, a few are really trying to observe the manner in which they’ll attain their objectives. Generally, composting tasks are the greatest fix for creating landfill diversion initiatives, yet unless a local composting place exists already for getting the organic waste, not many can pay to construct a new place. A composting project takes a long time from idea to implementation. Before you can make an intelligent decision there are many things you should know.

Along with the beginning costs of a composting operation, earning community acceptance is critical. If locals complain about the smell, noise, more vermin, traffic, and fire risk, the task may be over prior to ever getting out of the committee.
Expenses include transportation, new procedure implementation, collection, quality control, consultation, tests, and more. After operating for a year, most find themselves over-budget.

It is another story in the Memphis area. A new in-vessel vertical composting unit has been designed by Agra Cycle. (VCU for short) named the Vee-Stack. While primarily operating within the UK and Australia, VCU’s has an over 30 years global presence, and is known for its extremely high composting standards. They have found ways to make the manufacturing process less expensive than those made overseas.
The Vee-Stack will help corporations and municipalities meet landfill diversion goals, provide greenhouse gas reduction, organic waste composting, and sustainable recycling and agricultural processes that provide carbon credits.Public Relations is where the key is. The PR for an environmentally sound, sustainable recycling project are enormous and timely. Composting is a bi-partisan activity which everyone can lend support to; and, it creates a better sense of community awareness. Those citizens who come forward without any motivations for improving the soil and cleaning the environment creates pride.

According to Agra-Cycle, “There are two keys to operational success using a Vee-Stack. The first is with the organic waste processing: there must be a balanced proportion of carbon and nitrogen. Then the pH values must be adjusted, followed by precise moisture control, and finally loading into the Vee-Stack. Agra-Cycle takes care of a big headache for the customer.

The second part happens with the normal draft induction process. Air enters the Vee-Stack from the bottom which greatly enhances the composting process in the chamber. If you know what a chimney fire is then you get a good concept of how the Vee-Stack operates. When thermal patterns increase in the stack, microbes which do well at greater temps become alive. In most cases this is referred to as the Stoichomatic range. For traditional composting techniques, these thermal ranges pose a fire threat and must be avoided no matter what, yet with in vessel building these temperatures are harnessed for process promotion. The fear of fire is eliminated from this process due to the high moisture content. The microbes eat all the smelly gases and hydrogen sulfides that create problems with other methods of composting. The machine basically functions as it’s personal bio filtration system. The Vee Stack is totally self contained; and, it even gathers and recycles leechate back into the system so that it can be composted, also.

Sustainable recycling involving local companies and communities, to prevent landfills, that is our goal. The Vee Stack can be custom made according to what you need and the size requirements. We also watch over, upkeep, manage the Vee Stack and take away the finished substance. Process your organic wastes consistently and for much less than you are currently paying for disposal by using the specialized knowledge and experience provided by Agra-Cycle.About ten tons of organic waste per day can be processed by continuous use of Vee Stack. The effects increase with the addition of more units. Depending on the organic waste used, the process can take between 14-21 days to complete.
Along with the said advantages, the cost incurred in getting rid of waste comes down by about 25%. Now this is how we define sustainable. Agra-Cycles is the sole proprietor of this technology and they are very committed to the mission of implementing sustainable recycling project in their home state of Tennessee, not as a preference but as a priority. Based in Tennessee, non-profit corporation Agra-Cycle promotes agriculture which can be sustained as well as providing resources of an educational nature. Every contribution is completely tax deductible. Please contact your tax professional for the most up to date tax laws.
Copyright 2010 Greg Traver