Abstract
Soil contamination by organic and inorganic compounds is a universal concern nowadays. One such contamination is heavy metal exposure to the soil from different sources. The discharge of effluents from various factories in Punjab like tanning industries, leather industries, and electroplating industries generate a large volume of industrial effluents. These industrial units discharge their effluents directly or through the sewer into a water tributary (Buddha Nallah) and this water is being used for irrigating the crops. The heavy metals enter into the food chain thus contaminating all resources i.e. air, soil, food, and water. Preventive and remedial measures should be taken to reduce the effects of heavy metals from soil and plants. Organic soil amendments like FYM, Vermicomposting, Biochar, and poultry manure have been used to deactivate heavy metals by changing their forms from highly bioavailable forms to the much less bioavailable forms associated with organic matter (OM), metal oxides, or carbonates. These amendments have significant immobilizing effects on heavy metals because of the presence of humic acids which bind with a wide variety of metal(loid)s including Cd, Cr, Cu, and Pb.
Keywords
- remediation
- heavy metals
- organic manures
- soil
- plants
1. Introduction
Heavy metals are found naturally in the Earth’s crust. Any metals and metalloids with an atomic density greater than 4 g cm3 [1] and toxic at low concentrations are considered heavy metals. They cannot be destroyed or degraded. Mercury (Hg), thallium (Tl), lead (Pb), chromium (Cr), arsenic (As) and cadmium (Cd) are some examples of heavy metals. Heavy metals like (e.g., Copper, selenium, and zinc) are required to keep the metabolism of human body. At higher concentrations, they can cause poisoning. They enter into human bodies through drinking water, food and breathing. Industrial, consumer waste, and acid rain breaks the soil particles and releases heavy metals into water bodies like streams, reservoirs, rivers, and groundwater resulting in heavy metal contamination of water supplies. Heavy metals have several potentially harmful side effects. They can find their way into the environment in various ways and are dangerous due to their accumulation for bioaccumulation.
While comparing the chemical’s concentration in the atmosphere, bioaccumulation refers to a rise in the attention of a chemical in a biological organism over time. As molecules are taken up and broken down (metabolized) or discharged and accumulates in living things. As a result, toxicity symptoms may occur due to contaminated potable water, high atmospheric air concentrations near pollution sources, or ingestion through the foods etc.
There are two distinct categories of heavy metals and can be classified into: (i) elements that are necessary for plant growth are B, Cu, Fe, Mo, Ni, and Zn although poisonous to plants and animals if their concentrations reach definite approach. The difference between recommended and harmful levels for many of these elements is minimal; (ii) elements are unnecessary for animals or plants, such as As, Cd, Hg, and Pb. M, land application of treated wastewater (TWW), fertilizers, sewage sludge and manufacturing practices are sources of heavy metals in soils [2].
Heavy metal pollution in the soil is now a global environmental problem that has captivated public interest, owing to growing concerns about protecting agricultural products. Natural processes originating from parent sources and anthropogenic practices bring these components into the soil agro-ecosystem. Because of the potential for accumulation across the food chain, heavy metal exposure presents a significant risk to the public health and well-being of animals and humans. To solve the issue, physical, chemical, and biological remediation approaches have been used.
2. Origin of heavy metal contamination
Heavy metals are found generally in soil due to bioturbation, degradation and weathering of parent materials in small concentrations are considered as trace (less than 1000 mg kg−1) but very occasionally toxic [3, 4]. As a consequence of man’s destruction and amplification of essence’s slowly developing geochemical cycle, soils often accumulate heavy metals above-established background values which are sufficient to pose a risk to human health, livestock, crops, and other media [5].
Heavy metals eventually set off pollutants in the environment when:
The rates of production of these metals through artificial cycles become faster as compared to natural processes.
They are transported from mines to numerous places in the field where there is a greater risk of direct exposure.
Compared to those from the receiving area, concentrations of metals indisposed of goods are comparatively high.
The chemical form of metal in the receiving environment system makes it much more bioavailable [5].
The significant sources contributing to heavy metal accumulation in our ecosystems are:
2.1 Fertilizers
Plants needs both macronutrients and micronutrients to develop and complete their life cycle. Heavy metals (like Co, Cu, Fe, Mn, Mo, Ni, and Zn) required for plant growth and development [6] are insufficient in certain soils and can be applied as a foliar spray or soil application in fields. In intensive farming systems, substantial amount of fertilizers is used frequently to provide plants with adequate nutrients for plant growth development. However, few heavy metals such as Cd and Pb are present as impurities in the compounds used to supply essential elements, and regular application of fertilizer can remarkably boost their concentration into the soil [7]. Lead and cadmium are known to have little or no physiological activity. Phosphorus containing fertilizers unintentionally introduce Cd and some other certainly harmful elements [such as iron (F), mercury (Hg), and (Pb)] to the soil [8].
2.2 Pesticides
In historical agriculture and horticulture, several prevalent insecticides had a considerable amount of metal concentrations. For example, around 10 percent of the chemicals licensed are used as fungicides and insecticides in the United Kingdom in recent years were based on compounds containing Manganese (Mn), Copper (Cu), Zinc (Zn), Hg, and Pb. Fungicidal sprays containing Cu, for instance, Bordeaux mixture (copper sulfate) and copper oxychloride [7], are examples of such pesticides. For many years, lead arsenate was employed in fruit orchards to control parasitic insects. Compounds that contain arsenic have also been widely used to prevent livestock ticks and bananas in New Zealand and Australian countries, where wood timber has been conserved with Cu, Cr, and Arsenic (CCA) formulations. Many abandoned sites now surpass the background concentrations of the soil of these elements. Such pollution may lead to problems, significantly when areas are restored for agricultural or non-agricultural activities. The usage of such materials was more confined, restricted to specific sites or crops than fertilizers [9].
2.3 Manures and biosolids
Inadvertently, the manures application (e.g., animal manures or municipal sewage loam) onto the soil results in the build-up of heavy metals like chromium (Cr), arsenic (As), Cu, mercury (Hg), cadmium (Cd), lead, nickel (Ni), selenium (Se) and molybdenum (Mo) [10]. Some animal wastes like poultry, cattle, or pig dung produced in farming are often used as solids and slurries on crops and pastures [11]. While most manures are regarded as helpful fertilizers, Zn or Cu are given in diets as growth enhancers and added as supplements could have the capacity to bring about metal pollution of the soil, livestock and poultry industries [11, 12]. Manures produced by animals consuming those diets have significant concentrations of Zn, As, and Cu, leading to the substantial accumulation of heavy metals in the soil if it is frequently applied to restricted sections of land.
Biosolids are predominantly waste materials having organic origin created by wastewater treatment procedures that can also be reused to benefit the environment [13]. Biosolids materials are applied to the soil in many countries to reuse the biosolids produced by urban populations [14]. More than 30% of the wastewater is used as a fertilizer in the farming sector in the European Community [15]. Approximately 2.8 MT of dry sewage sludge utilized or get rid of per annum in the United States is anticipated to be land applied, and biosolids are utilized in agriculture throughout the country.
The possibility of composting biosolids with other organic substances like sawdust, stroke, or garden waste is also of considerable curiosity. Biosolids’ potential to contaminate the soils with heavy metals has prompted widespread review about their usage in agricultural sector [16]. The most frequent heavy metals in these are Zn, Cd, Cu, Ni, Cr, and Pb, and the metal content depend on the nature, intensity, and techniques used to treat biosolids [17]. These metals applied to soils as part of biosolids treatments can seep into the soil profile and pollute groundwater in certain conditions [18]. For example, increased amounts of Zn, Ni, and Cd in drainage leachates have been found in recent investigations on certain New Zealand soil amended with biosolids [19, 20].
2.4 Wastewater
Municipal and polluted wastewater is being applied to agricultural land for over four 100 years, a prevalent exercise in many sections of the world [21]. Such liquid waste is being used to irrigate 20 million hectares of agricultural land around the world. As per studies, wastewater irrigation-based agriculture is responsible for 50% of the vegetable supply to metropolitan parts in many African and Asian cities. Farmers are unconcerned about environmental impact or consequences and only focus on enhancing their production and profitability. Irrigation with such water leads to accumulation of heavy metal in the soil even though metals in industrial wastewaters are typically low.
2.5 Mining of metal, milling processes and industrial wastes
Across many countries have been vouchsafed by the mining and milling of metals and the fabrication, the legacy of vast disseminating pollutants of metal contamination in soil. At the time of mining, the residues of ores are straightaway released into natural depressed geologic formation and swamps, resulting in upraised contents [22]. Voluminous mining and smelting of Zn and Pb, thus polluting the soil, risk ecological and human health risks. Furthermore, various recovery methods applied at these sites can be long and exorbitant, and soil productivity may not be restored. Comprehend pathways comprise the absorption of plant material being grown in or direct absorption of polluted soil [10].
More materials are produced by diverse industries like petrochemicals, textile, tanning by fortuitous oil spills, petroleum-based products being used, pesticides, and pharmaceutical provisions significantly fluctuating in the constitution. Though some are inclined of on land, some have suitable for forestry or agriculture. Moreover, numerous are certainly precarious due to their concentration of weighty metals (Zn, Pb, and Cr) or poisonous biological compounds that are rarely, if by any chance, used on land. Rest are highly deprived of nutrients or possess no soil improving properties [11].
2.6 Airborne sources/origins
Metals can be found in the air due to stack or duct emissions of air, gas, or vapor streams, as well as fugitive emissions including dust from warehouses or garbage dumps. Metals emitted from the air are usually discharged as particles in the gas stream. Following high-temperature processing, several metals, such as Pb, Cd, and As, can also volatilize. Natural air currents can also disperse stack emissions over a large area until they are removed from the gas stream by dry and wet precipitation processes.
Agricultural lands near smelting sites have been discovered to have very high levels of Cd, Pb, and Zn. Airborne emissions of Pb from the combustion of fuel including tetraethyl lead are yet another major cause of soil pollution; this contributes significantly to the Pb concentration in urban areas. Tires, lubricating fluids are two sources of Cd and Zn that can be introduced into soils near highways [23].
3. Organic soil amendments
Organic soil amendments have been widely used to binding heavy metals by changing their forms from initially highly bioavailable forms to the much less bioavailable fractions associated with organic matter (OM), metal oxides, or carbonates [24]. These amendments have significant binding effects on heavy metals because it contains humic acids which bind with a wide variety of metal(loid)s including Cd, Cr, Cu, and Pb [25]. The commonly used soil amendments which are organic in nature are composts of different origins, manures, sawdust, sewage sludge, and wood ash [26]. The two major advantages of these amendments as compared to other soil amendments are relative of lower cost and they commonly facilitate the re juvination of contaminated soils. However, the residual effect of organic amendments on metal solubility should also be considered. Metal extraction depends upon the original OM content, the soil type, and the rate of OM transformation over time [27]. This is the important consideration that addition of a single organic amendment results in the production of many different organic substances. This is because, during the break down of organic matter, various organic acids are released which may alter metal availability [28]. Increased decomposition of OM decreased the surface area and CEC, this is due to an increase in dissolved organic carbon which results in the release of metals [29, 30]. Thus the nature and stability of OM amendments are also important for determining the long-term partitioning of metals between the solution and the solid phase. Various organic manures are used for remediation purposes like FYM, vermicompost, biochar and Poultry manure. In this chapter, the effect of organic manures on the remediation of heavy metal contaminated soils will be discussed one by one. Let us discuss them one by one:
3.1 Farm yard manure
Various organic amendments were used to remediate heavy metal contaminated soils like farm yard manure and composted organic amendments, The effect of organic manures to be applied depends upon the nature, mobility, and the bioavailability of metal, its microbial decomposition, and its further effects on soil chemical and physical proprieties [31]. Using amendments in contaminated soils, metal Immobilization is a remediation measure that decreases mobility and phytoavailability of metals in the soils and their plant uptake [32]. It is being used by farmers as source of nutrition to field crops. Low availability of this manure is a major problem on its use as a source of nutrients. FYM controls the production of crop and maintain properties of soil and it can be used to decrease heavy metal stress in plants. The FYM, pig and cow manure decreased available Ni content in soil due to the formation of strong metal complexes with OM [33]. In sandy loam soil, application of FYM significantly reduced Cd and Pb content in the shoots and roots of Amaranth [34]. Due to increased soil pH, complexation of metal with OM and co-precipitation with P content, the metal concentration in tissues of plants for metals (Cu, Zn, and Pb) will be decreased in
3.2 Vermicompost
Vermicompost (VC), the organic input, is produced from various organic wastes. It is a rich source of antibiotics, enzymes, immobilized microflora and various growth hormones like gibberellins which synchronize the growth of plants and microbes. It has the ability to improves the quality of growing plants and also increases growth resulting in improved metal toxicity. Vermicompost is a rich source of nutrients, increases the soil fertility. In contaminated soil, application of vermicompost improves soil physical and chemical characterstics of soils. Heavy metal contaminated soils are also bioremediated with vermicompost and spent mushroom compost. Bioremediation is done through vermiremediation. Vermiremediation is an applied science to get rid of heavy metals from soil.
3.3 Biochar
The biochar is highly aromatic, where the functional groups associated with it, which give the biochar a net negative charge, resulting in increased CEC in soil with increased adsorption capacity for both organic and inorganic compounds, and greater nutrient retention. Biochar has a porous body, charged surface, and many different surface functional groups and contains significant amounts of humic and fulvic-like substances [47]. It has also been used to remediate heavy metals from soils and water. Different kinds of biochar derived from plant residues and animal manures are used to reduce the mobility and availability of metal in contaminated soil and water. Mostly biochars are alkaline in nature and released the available form of P, K, and Ca. In general, application of biochar reduced the concentrations of zinc and cadmium by 45 and 300 fold [48]. It is due to sorption mechanism which is used for the withholding of metals by biochars. The Cu leaching was correlated with higher DOC contents [49]. Biochar, when applied to the soil, improves quality and productivity of soil because the oxides, hydroxides, and carbonates present in biochar can act as liming agents [50]. Biochar can reduce soil bulk density and thereby increases water infiltration, soil aeration, root penetration, and increase soil aggregate stability. Biochar spiked soil has soil pH > 7 which is found suitable for the rise of fungal hyphae. Adding higher amounts of biochar to soil increased the environment for microbes, with promoted growth via increased porosity [51]. Therefore, it is critical to consider both soil and biochar properties when it is used for the remediation of salt-affected soils and the source of the feedstock used to produce the biochar which is used as an organic amendment [52]. Generally, biochar application could be recommended as an appropriate amendment for in-situ remediation and immobilization of the heavy metals especially for lead and cadmium in contaminated soils [53].
3.4 Poultry manure
Poultry manure is also used to remediate heavy metals from soil. A study was conducted to study the effectiveness of the adding poultry manure on the bioavailability of trace metals from the contaminated soil after treatment with wastewater [54]. It was applied @ 10 and 20 t ha−1 and found that the addition of manure increased fenugreek biomass and decreased trace metal uptake depending on the combination of composted manures used. Trace metal concentrations in the fenugreek shoots were in the order of Pb > Ni > Zn > Cu > Cd. Soils amended with Poultry litter reduced trace metal concentrations more than composted manure which is true for the plant uptake. It was concluded that following the combined application of composted manure with residues of plant can be effectively used for remediating trace metal concentration in soils and crops. Chicken-manure biochar is used as a soil amendment to immobilize and detoxify heavy metals like cadmium and lead.
Certain plant species are also used to remediate heavy metals. They can accumulate a high amount of heavy metals in upper parts of plants. Indian mustard plant is used for phytoremediation [55]. So, Biocar can also remediate heavy metal toxic soils.
4. Effect of organic manures on soil health
The addition of organic manures to polluted soils has some beneficial effects on soil properties. The most important factor is soil pH that affect solubility of metal, plant nutrient uptake, plant biomass, microbial activity, and many other characteristics [56]. The increase in soil pH, due to manure addition is due to specific adsorption of organic anions on surfaces of hydrous Fe and Al and the simultaneous liberation of hydroxyl ions [57]. Depending upon the compost sources, pH may either increase or decrease. These amendments improved soil physical characteristics such as particle size distribution, cracking pattern, and porosity. Organic amendments are rich source of nutrients like N, P, and other secondary elements like Ca, Mg, and Fe which are required for plant growth and improves the soil fertility status. The essential nutrients in these amendments are in inorganic forms which are released slowly and subjected to leaching loss compared to inorganic fertilizers [58]. The build-up of soil organic matter through the addition of organic manures increased soluble organic carbon, microbial biomass carbon [59], population and species diversity of microorganisms like bacteria [60], soil respiration [61], and the activity of various soil enzymes [62]. The application of organic amendments to soils results in significant improvements in overall soil quality.
5. Conclusion
Heavy metals are detrimental to health issues even at very low concentrations due to their long-term persistence, hence they must be removed from environments to maintain the balance of the ecosystem and human health. As a bioremediation approach, removing heavy metals from the soils by using organic amendments was discussed. Organic amendments are very effective in mitigating the effects of heavy metals from the soil. Hence, the chapter concluded that the application of organic manures like FYM, Vermicomposting, biochar, poultry manure reduced the heavy metal toxicity. Large quantities of organic amendments are used as a source of nutrients and also as a conditioner to improve the soil physical properties and fertility of soils. These organic amendments can be used as a sink for reducing the bioavailability of heavy metals in contaminated soils through their effect on the adsorption, complexation, reduction, and volatilization of metals.
References
- 1.
Hawkes SJ. What is a “heavy metal”? Journal of Chemical Education. 1997; 74 (11):1374 - 2.
Gupta N, Khan DK, Santra SC. Determination of public health hazard potential of wastewater reuse in crop production. World Review of Science Technology and Sustainable Development. 2010; 7 (4):328-340 - 3.
Kabata-Pendias A. Trace Elements in Soils and Plants Trace Metals in Soils and Plants. 2nd ed. Boca Raton, Fla, USA: CRC Press; 2001 - 4.
Pierzynski GM, Vance GF, Sims JT. Soils and Environmental Quality. 2nd ed. London, UK: CRC Press; 2000 - 5.
D’Amore JJ, Al-Abed SR, Scheckel KG, Ryan JA. Methods for speciation of metals in soils. Journal of Environmental Quality. 2005; 34 (5):1707-1745 - 6.
Lasat MM. Phytoextraction of metals from contaminated soil: A review of plant/soil/metal interaction and assessment of pertinent agronomic issues. Journal of Hazardous Substance Research. 1999; 2 (1):1-1 - 7.
Jones LHP, Jarvis SC. The fate of heavy metals. In: The Chemistry of Soil Process. 1981. pp. 593-620 - 8.
Raven R, Berg LR, Johnson GB. Environment. Philadelphia, USA: Saunders College Publishing; 1993. p. 569 - 9.
McLaughlin MJ, Hamon RE, McLaren RG, Speir TW, Rogers SL. Review: A bioavailability-based rationale for controlling metal and metalloid contamination of agricultural land in Australia and New Zealand, Australian Journal of Soil Research 2000; 38, p. 1037-1086 - 10.
Basta NT, Ryan JA, Chaney RL. Trace element chemistry in residual-treated soil: Key concepts and metal bioavailability. Journal of Environmental Quality. 2005; 34 (1):49-63 - 11.
Sumner ME. Beneficial use of effluents, wastes, and biosolids. In: Communications in Soil Science and Plant Analysis. Marcel Dekker Inc.; 2000. pp. 1701-1715 - 12.
Chaney RL, Oliver DP. Sources, potential adverse effects, and remediation of agricultural soil contaminants. In: Contaminants and the Soil Environment in the Australasia-Pacific Region. Netherlands: Springer; 1996. pp. 323-359 - 13.
US Environmental Protection Agency. EPA A Plain English Guide to the EPA Part 503 Biosolids Rule Excellence in Compliance through. US Environmental Protection Agency. EPA-832/R-93/003; 1994 - 14.
Weggler K, McLaughlin MJ, Graham RD. Effect of chloride in soil solution on the plant availability of biosolid-borne cadmium. Journal of Environmental Quality. 2004; 33 (2):496-504 - 15.
Silveira MLA, Alleoni LRF, LRG G. Biossólidos e metais pesados em solos. Vol. 60. Scientia Agricola; 2003. pp. 793-806 - 16.
Canet R, Pomares F, Tarazona F, Estela M. Sequential fractionation and plant availability of heavy metals as affected by sewage sludge applications to soil. Communications in Soil Science and Plant Analysis. 1998; 29 (5-6):697-716 - 17.
Mattigod SV, Page AL. Assessment of metal pollution in soils. In: Applied Environmental Geochemistry. London, UK: Academic Press; 1983. pp. 355-394 - 18.
McLaren RG, Clucas LM, Taylor MD. Leaching of macronutrients and metals from undisturbed soils treated with metal-spiked sewage sludge. 3. Distribution of residual metals. Australian Journal of Soil Research. 2005; 43 (2):159-170 - 19.
Keller C, McGrath SP, Dunham SJ. Trace metal leaching through a soil-grassland system after sewage sludge application. Journal of Environmental Quality. 2002; 31 (5):1550-1560 - 20.
McLaren RG, Clucas LM, Taylor MD, Hendry T. Leaching of macronutrients and metals from undisturbed soils treated with metal-spiked sewage sludge. 2. Leaching of metals. Australian Journal of Soil Research. 2004; 42 (4):459-471 - 21.
Reed SC, Crites RW, Middlebrooks EJ. Natural Systems for Waste Management and Treatment. Ed. 2 ed. Nat Syst waste Manag Treat; 1995 - 22.
DeVolder PS, Brown SL, Hesterberg D, Pandya K. Metal bioavailability and speciation in a wetland tailings repository amended with biosolids compost, wood ash, and Sulfate. Journal of Environmental Quality. 2003; 32 (3):851-864 - 23.
E.P.A. Recent developments for In situ treatment of metal contaminated soils. US Environmental Protection Agency. 1997; 703 :64 - 24.
Walker DJ, Clemente R, Bernal MP. Contrasting effects of manure and compost on soil pH, heavy metal availability and growth of Chenopodium album L. in a soil contaminated by pyritic mine waste. Chemosphere. 2004; 57 (3):215-224 - 25.
Alvarenga P, Gonçalves AP, Fernandes RM, de Varennes A, Vallini G, Duarte E, et al. Organic residues as immobilizing agents in aided phytostabilization: (I) effects on soil chemical characteristics. Chemosphere. 2009; 74 (10):1292-1300 - 26.
Sabir M, Hanafi MM, Aziz T, Ahmad HR, Zia-Ur-Rehman M, Saifullah, et al. Comparative effect of activated carbon, press mud, and poultry manure on immobilization and concentration of metals in maize (Zea mays) grown on contaminated soil. International Journal of Agriculture and Biology. 2013; 15 (3):559-564 - 27.
Martínez CE, Jacobson AR, McBride MB. Aging and temperature effects on DOC and elemental release from a metal-contaminated soil. Environmental Pollution. 2003; 122 (1):135-143 - 28.
Misra SG, Pande P. Effect of organic matter on availability of nickel. Plant and Soil. 1974; 40 (3):679-684 - 29.
Martínez F, Cuevas G, Calvo R, Walter I. Biowaste effects on soil and native plants in a semiarid ecosystem. Journal of Environmental Quality. 2003; 32 (2):472-479 - 30.
McBride MB. Toxic metal accumulation from agricultural use of sludge: Are USEPA regulations protective? Journal of Environmental Quality. 1995; 24 (1):5-18 - 31.
Angelova VR, Akova VI, Artinova NS, Ivanov KI. The effect of organic amendments on soil chemical characteristics. Bulgarian Journal of Agricultural Science. 2013; 19 (5):958-971 - 32.
Rehman TH, Borja Reis AF, Akbar N, Linquist BA. Use of normalized difference vegetation index to assess N status and predict grain yield in rice. Agronomy Journal. 2019; 111 (6):2889-2898 - 33.
Narwal RP, Singh BR. Effect of organic materials on partitioning, extractability, and plant uptake of metals in an alum shale soil. Water, Air, and Soil Pollution. 1998; 103 (1-4):405-421 - 34.
Alamgir M, Islam M, Alamgir M, Kibria MG, Islam M. Effects of farmyard manure on cadmium and lead accumulation in Amaranth ( Amaranthus oleracea L.). Journal of Soil Science and Environmental Management. 2011;2 (8):237-240 - 35.
Rani N, Singh D, Sikka R. Effect of applied chromium and amendments on dry matter yield and uptake in maize-Indian mustard rotation in soils irrigated with sewage and tubewell waters. Agricultural Research Journal. 2018; 55 (4):677 - 36.
van Herwijnen R, Hutchings TR, Al-Tabbaa A, Moffat AJ, Johns ML, Ouki SK. Remediation of metal contaminated soil with mineral-amended composts. Environmental Pollution. 2007; 150 (3):347-354 - 37.
Clark GJ, Dodgshun N, Sale PWG, Tang C. Changes in chemical and biological properties of a sodic clay subsoil with the addition of organic amendments. Soil Biology and Biochemistry. 2007; 39 (11):2806-2817 - 38.
Gondar D, Bernal MP. Copper binding by olive mill solid waste and its organic matter fractions. Geoderma. 2009; 149 (3-4):272-279 - 39.
Hartley W, Dickinson NM, Riby P, Leese E, Morton J, Lepp NW. Arsenic mobility and speciation in contaminated urban soil are affected by different methods of green waste compost application. Environmental Pollution. 2010; 158 (12):3560-3570 - 40.
Kunhikrishnan A, Bolan NS, Müller K, Laurenson S, Naidu R, Il KW. The influence of wastewater irrigation on the transformation and bioavailability of heavy metal(loid)s in soil. In: Advances in Agronomy. 2012. pp. 215-297 - 41.
Cao X, Ma LQ. Effects of compost and phosphate on plant arsenic accumulation from soils near pressure-treated wood. Environmental Pollution. 2004; 132 (3):435-442 - 42.
Ye ZH, Wong JWC, Wong MH, Lan CY, Baker AJM. Lime and pig manure as ameliorants for revegetating lead/zinc mine tailings: A greenhouse study. Bioresource Technology. 1999; 69 (1):35-43 - 43.
Cheng-Kim S, Bakar AA, Mahmood NZ, Abdullah N. Heavy metal contaminated soil bioremediation via vermicomposting with spent mushroom compost. Science Asia. 2016; 42 (6):367-374 - 44.
Pattnaik S. Heavy metals remediation from urban wastes using three species of earthworm (Eudrilus eugeniae, Eisenia foetida, and Perionyx excavatus). Journal of Environmental Chemistry and Ecotoxicology. 2011; 3 (14):345, 356 - 45.
Singh J, Singh S, Vig AP, Kaur A. Environmental influence of soil toward effective vermicomposting. In: Earthworms-The Ecological Engineers of Soil. InTech; 2018. DOI: 10.5772/intechopen.75127 - 46.
Kizilkaya R. The role of different organic wastes on zinc bioaccumulation by earthworm Lumbricus Terrestris L. (Oligochaeta) in successive Zn added to the soil. Ecological Engineering. 2005; 25 (4):322-331 - 47.
Kammann CI, Schmidt HP, Messerschmidt N, Linsel S, Steffens D, Müller C, et al. Plant growth improvement mediated by nitrate capture in co-composted biochar. Scientific Reports. 2015; 5 (1):11080 - 48.
Beesley L, Marmiroli M. The immobilization and retention of soluble arsenic, cadmium, and zinc by biochar. Environmental Pollution. 2011; 159 (2):474-480 - 49.
Beesley L, Moreno-Jiménez E, Gomez-Eyles JL, Harris E, Robinson B, Sizmur T. A review of biochars’ potential role in the remediation, revegetation, and restoration of contaminated soils. Environmental Pollution. 2011; 159 :3269-3282 - 50.
Krishnakumar S, Rajalakshmi AG, Balaganesh B, Manikandan P, Vinoth C, Rajendran V. Impact of biochar on soil health. International Journal of Advanced Research. 2014; 2 (4):933-950 - 51.
Hairani A, Osaki M, Watanabe T. Effect of biochar application on mineral and microbial properties of soils growing different plant species. Soil Science & Plant Nutrition. 2016; 62 (5-6):519-525 - 52.
Amini S, Ghadiri H, Chen C, Marschner P. Salt-affected soils, reclamation, carbon dynamics, and biochar: A review. Journal of Soils and Sediments. 2016; 16 (3):939-953 - 53.
Lwin CS, Seo BH, Kim HU, Owens G, Kim KR. Application of soil amendments to contaminated soils for heavy metal immobilization and improved soil quality—A critical review. Soil Science & Plant Nutrition. 2018; 64 (2):156-167 - 54.
Haroon B, Hassan A, Abbasi AM, Ping A, Yang S, Irshad M. Effects of co-composted cow manure and poultry litter on the extractability and bioavailability of trace metals from the contaminated soil irrigated with wastewater. Journal of Water Reuse Desalination. 2020; 10 (1):17-29 - 55.
Yan A, Wang Y, Tan SN, Mohd Yusof ML, Ghosh S, Chen Z. Phytoremediation: A promising approach for revegetation of heavy metal-polluted land. Frontiers in Plant Science. 2020; 11 :359 - 56.
García-Gil JC, Ceppi SB, Velasco MI, Polo A, Senesi N. Long-term effects of amendment with municipal solid waste compost on the elemental and acidic functional group composition and pH-buffer capacity of soil humic acids. Geoderma. 2004; 121 (1-2):135-142 - 57.
Wong M, Swift R. Role of organic matter in alleviating soil acidity. In: Handbook of Soil Acidity. 2003 - 58.
Larney FJ, Olson AF, Miller JJ, DeMaere PR, Zvomuya F, McAllister TA. Physical and chemical changes during composting of wood chip-bedded and straw-bedded beef cattle feedlot manure. Journal of Environmental Quality. 2008; 37 (2):725-735 - 59.
Baker LR, White PM, Pierzynski GM. Changes in microbial properties after manure, lime, and bentonite application to heavy metal-contaminated mine waste. Applied Soil Ecology. 2011; 48 (1):1-10 - 60.
Cheng Z, Grewal PS. Dynamics of the soil nematode food web and nutrient pools under tall fescue lawns established on soil matrices resulting from common urban development activities. Applied Soil Ecology. 2009; 42 (2):107-117 - 61.
Iovieno P, Morra L, Leone A, Pagano L, Alfani A. Effect of organic and mineral fertilizers on soil respiration and enzyme activities of two Mediterranean horticultural soils. Biology and Fertility of Soils. 2009; 45 (5):555-561 - 62.
Antonious GF. Enzyme activities and heavy metals concentration in soil amended with sewage sludge. Journal of Environmental Science and Health-Part A Toxic/Hazardous Substances and Environmental Engineering. 2009; 44 (10):1019-1024