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Impact of Iron and Steel Slag on Crop Cultivation: A Review

Mir Syeda Yuhannatul Humaria1 *

1 Kolhan University, Chaibasa, Jharkhand India

DOI: http://dx.doi.org/10.12944/CWE.9.1.31

This review paper addresses the issuesto analyze the impacts of Iron and Steel slag on crop cultivation. The use of steel slag in agriculture produces not only economic but also ecological advantages. The value of silicon (Si) application for rice (Oryzasativa) has been demonstrated when soil soluble Si is low.Impact of solid waste on crop cultivation depends on the availability and quantity of different constituents like PH, Ammonia, Nitrites, Nitrates, Permanganate Value (PV), Biochemical Oxygen Demand (BOD5 or BOD), Chemical Oxygen Demand (COD), Total Suspended Solids (TSS) and Turbidity, Total Dissolved Solids (TDS) etcpresent in the solid waste.This has also been discussed in this review paper.

Iron and Steel Slag; Linz-Donawitz Converter; Silicon; Silicate; Chlorosis; Chelates

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Humaria M. S. Y. Impact of Iron and Steel Slag on Crop Cultivation: A Review. Curr World Environ 2014;9(1) DOI:http://dx.doi.org/10.12944/CWE.9.1.31

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Humaria M. S. Y. Impact of Iron and Steel Slag on Crop Cultivation: A Review. Curr World Environ 2014;9(1). Available from: http://www.cwejournal.org/?p=5746


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Received: 2014-01-30
Accepted: 2013-02-23

Introduction

Slag is generated during iron and crude steel production.Its use in different application, such as in agriculture, reduces landfill slag and preserves natural resources. The main problem concerning the utilization of steel slag in agriculture consists of the possible leaching of heavy metals. The metals uptake by the plants is affected by the soil properties. For example the Cr and V contents into potatoes are reduced in soils with higher content of organic matter and with a heavy texture. In addition, the uptake of Cr, V and Cd by potatoes is favoured by low pH.
Composition and pH of a slag particle (Buck 1997) Figure 1: Composition and pH
of a slag particle (Buck 1997)

Click here to View figure

Materials and Methods

The use of steelmaking slag as fertilisers and as liming agents

A small amount of slag is used as fertiliser in agriculture and this use depends on the market situations. Due to the low market value of fertilisers, the long distances transportation is a limiting factor. In addition natural lime stone fertilisers are in competition to the slag use. Therefore, the development of new markets for the slag, in order to ensure its utilisation in the future, is required. In this respect the steel industry is committed to minimize the amount of slag which has to be deposited, by improving its use through the increase of its properties (Drissen et al., 200). Until the eighties steel was produced via the Thomas-Bessemer process, through the open hearth furnaces. The resulting slag containing phosphate has been used as fertiliser for about 70 years.

The current steelmaking process is based on the Basic Oxygen Steelmaking process, where a basic slag is produced in the Linz-Donawitz converter. The LD slag contains about 1-3 wt% of P2O5, which is too low to be used as phosphate fertilizer, but, at the same time, it is too high to be used in the BF or recycled in the sinter plants.

Converter lime fertilizer (using iron and steel slag)

Application

Advantage

Example of use

Wet rice farming

  • Iron oxides and manganese give vitality to roots.
  • Silicate, lime, phosphate, and magnesia create healthy rice plants.
  • Effective in improving iron-poor soil (preventing root rot, leaf blight, and autumn paddy degradation).
Fertilizer using converter slag

Dry field farming

  • Creates a general soil fertilizer containing a good balance of various fertilizer components needed by crops, including silicate, iron oxide, lime, magnesia, phosphate, manganese, and boron.
  • Helps improve acidic and deteriorated soil, creating a well-balanced soil that not only improves alkalinity but also promotes the breakdown of organic substances.

Steelmaking slag as a silicon source for plant

After oxygen, silicon (Si) is the most abundant element in the earth’s crust. Along with some other elements that are not considered essential, under particular agro-climatic conditions, it can increase the crop yields by promoting some physiological processes. Silicon sources for agricultural purposes must display some important features, such as high soluble Si content, low cost, availability for plants, balanced ratios and amounts of Ca and Mg, increase of phosphate mobility, suitable physical properties, easy application, and absence of heavy metals.

Because blast furnace slag contains fertilizer components CaO, SiO2, and MgO, it is used in rice cultivation as calcium silicate fertilizer. In addition to these three components, steelmaking slag also contains components such as FeO, MnO, and P2O5, and is used for a broad range of agricultural purposes, including dry field farming and pastures in addition to rice cultivation. Its alkaline property also remedies soil acidity. Required amounts of silicate
Required amounts of silicate Figure 2: Required amounts of silicate
Click here to View figure
 
Calcium silicate fertilizer (using blast furnace slag)

Characteristic

Advantage

Example of use

Silicate for healthy rice plants
  • Promotes photosynthesis by improving light-receiving condition of leaves.
  • Boosts root activity, reducing the wilting of lower leaves.
  • Creates strong stems that resist collapse.
  • Silicified cells form on leaf surfaces, preventing rice blight.
Fertilizer using granulated slag
Boosting dry matter production
  • Boosts dry matter production.
  • Improves ripening in later growth stages. (Increases thousand kernel weight.)
improving harvest quantities, appearance, and flavour
  • increases harvests by increasing the number of unshelled rice kernels and thousand kernel weight.
  • Improves appearance quality, increasing the ratio of highest grade rice.
  • Promotes ripening to improve flavour.

Discussion

Use of Slag as an Iron Fertilizer

The problem of iron (Fe) chlorosis can affect many crops on calcareous soils, resulting in substantial yield losses. Generally it has been corrected through the addition of Fe synthetic chelates, but these have resulted very expensive. Various studies have been focused on applying different Fe sources, in order to reduce the economic burden and to recycle some industrial by-products, such as converter slag (Wallace et al., 1982) (Sikka&Kansal, 1994). They are used not only as soil amendment but also as source of important plant nutrients, such as P, K, Mg and Fe oxides. An investigation pursued on 1984 showed that the application of a steel by-product (dust containing 430 g Fe kg-1) as fertilizer to alkaline soils, with or without sulphuric acid, increased dry matter yield of sorghum (Anderson &Parkpian, 1984). A similar treatment, through a mixture of sulphuric acid and iron sulphates, has allowed to correct Fe chlorosis in corn and alfalfa (Stroehlin& Berger, 1963).

While converter sludge has been used as Fe fertiliser in calcareous soils with positive results, recently the use of converter slag as source of Fe fertiliser in some calcareous soils incubation studies has led to relevant achievements. On this subject, pot experiments in a greenhouse have been carried out in China (Wang &Cai, 2006). Relevant results of this study have shown that the use of moderate steel slag or acidified slag as Fe fertilizer leads to the increase in Fe uptake and corn dry matter yield. This phenomenon is proportional to the application rate and is enhanced by the acidification of slag, although increasing application rates do not produce further improvements in yield and in Fe uptake. This suggests a possible optimized rate of these applied substances. On the other hand, in experiments conducted with the sandy loam dry matter yield significantly decreased. This can be explained because the Fe availability decreases with salt levels increase, resulting in a yield decrease and an increase of chlorosis in plants. Although further studies still have to be conducted in order to investigate the correct rates of converter slag for different crops and its possible residual environmental impacts to the soil, important results have been achieved by using this by-product as a source of available Fe (Torkashvand, 2011). In an incubation study, by adding to the soil converter slag (from Isfahan steel factory, Isfahan, Iran), containing about 24% of Fe oxides, along with elemental sulphur and organic matter, the soil pH has increased, due to the alkaline pH of slag. But during the incubation time the pH decreased. This can be due, according to some previous studies, either to the precipitation of the free carbonates as calcium carbonate (Abassapour et al., 2004) or to the hydrolysis of Fe3+ in the soil (Rodriguez et al., 1994). The decrease of soil pH probably results from the decomposition of organic matter applied and subsequent organic acids and CO2 release as well as the buffering ability of the calcareous soils. The observed yield increase in these soils may be due to the some nutrients availability as a consequence of pH increase.

Use of Steel Slag for Metal Stabilization in Contaminated Soils

Some investigations about the addition of steel slags in contaminated soils have been carried out. The stabilization technique is based on the incorporation of amendments, in order to minimize metals and metalloids, such as As, Cr, Cu, Pb, Cd and Zn that can be found in contaminated soils at wood treatment plants. In particular, when the copper sulphate and chromate copper arsenate are used to protect wood from insects and fungi, they can cause  he soil phytotoxicity. While the As can be stabilized by sorption on Fe oxides and also by the formation of amorphous Fe (III) arsenates, the Cr immobilization takes place through Cr  eduction from Cr (VI), which is mobile and toxic, to Cr (III), which is stable. The Cu stability in soil is pH dependent, because its mobility increases with decreasing pH. Carbonates, phosphates and clays can reduce the mobility and availability of Cu in soil. The proposed mechanism consists in precipitation of Cu carbonates and oxy-hydroxides, ion exchange and formation of ternary cation–anion complexes on the surface of Fe and Al oxyhydroxides. While Pb can be stabilized by using phosphorus-containing amendments, that reduce the Pbmobility, Zn can be immobilized in soil by using phosphorus amendments and clays. To this aim some chemical and mineralogical agents, such as industrial by-products have been applied. For instance, the use of alkaline materials, organic matters, phosphates, alumina-silicates and basic slag has been shown to limit the accumulation of Cu in plants cultivated in Cu-contaminated soils.

Conclusion

In this review the technical, economical, and environmental aspects of use of iron and steel slag in the field of crop cultivation. The availability nutrient/pollutant in soil depends on the nature of the chemical association between a metal with the organic residual and soil matrix, the pH value of the soil, the concentration of the element in the compost and the soil, and the ability of the plant to regulate the uptake of a particular element. The value of silicon (Si) application for rice (Oryzasativa) has been demonstrated when soil soluble Si is low. Slag is most effective used in field of agriculture to condition the soil.Slag is applied to most muck soils and associated sands that are to be planted to rice and sugarcane. There is a need to investigate the availability of silicon in sources which are potentially available for those where response to Si is also being demonstrated, dry weight. In addition to calcium silicate slag, thermo-phosphate - a fertilizer product that provides Si, P, and Mg - appears an excellent source for use.The use of steel slags in agriculture produces not only economic but also ecological advantages.

Referenecs
 
  1. www.nationalslag.org/.../nsa_185-5_bf_slag_as_agricultural_liming_mat
  2. http://www.intechopen.com/books/material-recycling-trends-and-perspectives/possible-uses-of-steelmaking-slag-in-agriculture-an-overview
  3. Aarabi-Karasgani, M., Rashchi, F., Mostoufi, N. &Vahidi, E. (2010). Leaching of vanadium from LD converter slag using sulfuric acid. Hydrometallurgy, Vol. 102, No. 1-4, pp. (14-21), ISSN 0304-386X
  4. Ali, M.T. &Shahram, S.H. (2007). Converter slag as a liming agent in the amelioration of acidic soils. International Journal of Agriculture and Biology, Vol. 9, No. 5, (2007), pp. (715-720), ISSN 1560-8530
  5. Peregrina, F.; Mariscal, I.; Ordonez, R.; Gonzalez, P.; Terefe, T.; and Espejo, R Agronomic Implications of Converter Basic Slag as a Magnesium Source on Acid Soils..Soil Science Society of America Journal 72(2): 402-411. (Mar. 2008-Apr. 2008)
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