Essay Role Of Microorganisms In Decomposition
The role of soil microorganisms
Although soil organisms comprise <1% of the total mass of a soil, they have a vital role in supporting all plants and thus animals. Some of their vital functions are described below.
Soil is alive
Every gram of a typical healthy soil is home to several thousand different species of bacteria. One square metre of soil can contain about 10 million nematodes and 45 000 microarthropods (springtails and mites). It has more species in it than 1 km2of rainforest. In addition to bacteria, soil is home to microscopic fungi, algae, cyanobacteria, actinomycetes, protozoa and nematodes, and macroscopic earthworms, insects and the occasional wombat.
All of these organisms can be divided between autotrophs (“self-feeders”), such as plants, algae and cyanobacteria, and heterotrophs (“different-feeders”), such as fungi and bacteria, which decompose organic matter.
Soil microbes break down organic matter
Microorganisms play an important role in the decomposition of organic matter. Different types of microbes are specialised to different types of organic matter, between them covering just about everything.
Soil microbes recycle nutrients
Soil microbes play a crucial role in returning nutrients to their mineral forms, which plants can take up again. This process is known as mineralization.
Soil microbes create humus
When the soil microbes have broken down all they can, what’s left is called humus, a dark brown jelly-like substance that can remain unchanged in the soil for potentially millennia. Humus helps the soil retain moisture, and encourages the formation of soil structure. Humus molecules are covered in negatively charged sites that bind to positively charged ions (cations) of plant nutrients, thus forming an important component of a soil’s cation exchange capacity. Humus is also suspected of suppressing plant diseases.
Soil microbes create soil structure
Some soil microbes secrete polysaccharides, gums and glycoproteins, which glue soil minerals together, forming the basis for soil structure. Fungal hyphae and plant roots further bind soil aggregates together. Soil structure is essential to good plant growth.
Soil microbes fix nitrogen
Agriculture depends heavily on the ability of certain microbes (mainly bacteria) to convert atmospheric nitrogen (N2 gas) to ammonia (NH3). Some live freely in the soil, while others live in association with plant roots – the classic example is Rhizobiumbacteria in the roots of legumes. The process of conversion is known as nitrogen fixation.
Biological nitrogen fixation contributes about 60% of the nitrogen fixed on Earth. In contrast, manufactured fertilisers contribute 25%. As the cost of energy continues to rise, so too the cost of manufactured nitrogen fertilisers will rise, so biological nitrogen fixation is likely to have ever increasing importance in food production.
Soil organisms promote plant growth
Some soil microbes produce a variety of substances that promote plant growth, including auxins, gibberellins and antibiotics.
Soil microbes control pests and diseases
The best known example of the use of soil microbes in pest control is the commercial production of the soil bacterium Bacillus thuringiensis (Bt) to control caterpillar pests of crops. Some strains of Bt are used to control beetles and flies as well. Several strains of the fungal genus Trichodermahave been developed as biocontrol agents against fungal diseases of plants, mainly root diseases. Various other genera of fungi are used for the control of insect pests.
My Agriculture Information Bank. 2011. Scope and Importance of Soil Microbiology. Agriinfo, India.
SESL Australia has evolved over 30 years as an environmental, soil, water and plant science laboratory and consultancy service. Established in Sydney in 1984 by Simon Leake, SESL has expanded into the ACT, QLD and VIC. The SESL team of environmental consultants have a clear company objective to provide accurate and timely sampling, analysis and interpretive reporting to solve client problems.
Environmental protection has the foremost importance in the present day life of mankind. Scientists have been researching for technologies naturally available for enhancement of agriculture, management of agricultural waste, etc. Indigenous Microorganisms (IMO’s)-based technology is one such great technology which is applied in the eastern part of world for the extraction of minerals, enhancement of agriculture and waste management. Indigenous microorganisms are a group of innate microbial consortium that inhabits the soil and the surfaces of all living things inside and outside which have the potentiality in biodegradation, bioleaching, biocomposting, nitrogen fixation, improving soil fertility and as well in the production of plant growth hormones. Without these microbes, the life will be wretched and melancholic on this lively planet for the survival of human race. That is why, environmental restoration and safeguarding target via the indigenous microbes in a native manner to turn out the good-for-nothing and useless waste into productive bioresources is the primary concern of this review. Based on the collection sites, the process of collection and isolation methods are different as they may vary from place to place. Ultimately, in this way to a meaningful and significant extent, we can bridge the gap between the horrifying environmental distress and the hostile activities that have been constantly provoked by human kind—by getting these indigenous microorganisms into action.
Keywords: Indigenous microorganisms, Biodegradation, Bioleaching, Biocomposting, Natural farming, Biofertilizer, Bioremediation
The uniqueness of microorganisms and their often unpredictable nature and biosynthetic capabilities, given a specific set of environmental and cultural conditions, have made them likely candidates for solving particularly difficult problems in life sciences and other fields as well. The responsible use of indigenous microorganisms to get economic, social and environmental benefits is inherently attractive and determines a spectacular evolution of research from traditional technologies to modern techniques to provide an efficient way to protect environment and new methods of environmental monitoring (Cai et al. 2013). Chemical fertilizers, pesticides, herbicides and other agricultural inputs derived from fossil fuels have increased agricultural production, yet the growing awareness and concern over their adverse effects on soil productivity and environmental quality cannot be ignored. The high cost of these products, the difficulties of meeting demand for them, and their harmful environmental legacy have encouraged scientists to develop alternative strategies to raise productivity, with microbes playing a central role in these efforts (Vaxevanidou et al. 2015). One application is the use of soil microbes as bioinoculants for supplying nutrients and/or stimulating plant growth. Some rhizospheric microbes are known to synthesize plant growth promoters, siderophores and antibiotics, as well as aiding phosphorous uptake. The last 50 years have seen quick steps made in our appreciation of the diversity of environmental microbes and their possible benefits to sustainable agriculture and production. The advent of powerful new methodologies in microbial genetics, molecular biology and biotechnology has only quickened the pace of developments (Patil et al. 2014).
The dynamic part played by microbes in sustaining our planet’s ecosystems only adds urgency to this enquiry. Culture-dependent microbes already contribute much to human life, yet the latent potential of vast numbers of uncultured—and thus untouched—microbes, is enormous (Patil et al. 2014). Culture-independent metagenomic approaches employed in a variety of natural habitats have alerted us to the sheer diversity of these microbes and resulted in the characterization of novel genes and gene products. Several new antibiotics and biocatalysts have been discovered among environmental genomes and some products have already been commercialized. Meanwhile, dozens of industrial products currently formulated in large quantities from petrochemicals, such as ethanol, butanol, organic acids and amino acids, are equally obtainable through microbial fermentation (Dong et al. 2011). This review illustrates recent progresses in our understanding of the role of indigenous microbes in sustainable environment (Fig. 1).
Different application aspects of indigenous microorganisms
Biodegradation of hydrocarbons
Role of indigenous microorganisms in remediation of contaminated soils
Degradation of organic compound by indigenous microbes without any artificial enhancement is termed as an “intrinsic bioremediation” and this is one of the best remedial actions for soil contamination. Generally, biodegradation means mineralisation of organic constituents to the soluble inorganic compounds or to transform organic constituents to other soluble organic compounds. In the process of biodegradation of an organic compound, a wide variety of microbial enzymes are involved in transforming both artificial and natural hydrocarbons into intermediate compounds which may be less or equally hazardous than the parental compounds. As biodegradation is a step-wise process, the intermediate compounds are converted into carbon dioxide, water and inorganic compounds which can be readily soluble. Under aerobic conditions, many organic compounds are completely oxidised into soluble inorganic compounds and oxygen acts as a terminal electron acceptor, whereas in anaerobic metabolism the organic compounds are incompletely oxidised into simple organic acids, methane and hydrogen gas as the by-products. Unlike in aerobic metabolism, nitrate, sulphate and bicarbonate act as the terminal acceptors, and the rate of degradation is usually limited by the inherent reaction rate of the active microorganisms.
At a given site, many factors affect the rate of biodegradation process, which are soil moisture, soil pH, availability of oxygen, availability of nutrients, contaminant concentration, and presence of suitable microbes. At higher rates, many hydrocarbons are readily degradable through aerobic metabolism, and only few hydrocarbons are biodegradable through anaerobic metabolism at lower rates. Indigenous microorganisms are inhabited by aquatic as well as oil-bearing deep sub-surface environments (Magot et al. 2000). Oxygen is the key factor that plays a crucial role in the biodegradative process. In relation to this, Aitken et al. (2004, 2008) reported that anaerobic degradation, particularly in methanogenesis, might be the main crude oil biodegradation process in reservoirs. The investigations held by Cai et al. (2013) showed that aerobic indigenous microorganisms also play a role in degrading the petroleum oils. In order to test the efficacy of oxygen/(aerobic microbes) using GC–MS analysis under water flooding wells of Dagang oil fields (oil reservoirs), the reporters initiated the study by partially activating the microbiota via flooding the water channels into oil reservoirs and observed that 99.0 % of n-alkanes and 43.03–99.9 % of Polycyclic aromatic hydrocarbons (PAHs) were degraded besides the change in biomarkers to their corresponding ratios, whereas the aerobic culture lasted for 90 days. The metabolite compounds like naphthenic acid, unsaturated fatty acids, aromatic carboxylic acid, alcohols, aldehydes and ketones were separated and identified from aerobic culture. The pathways of alkanes and aromatics were proposed suggests that oxidation of hydrocarbon to organic acid is an important process in the aerobic biodegradation of petroleum.
Indigenous microorganisms as a biofertilizer
Indigenous microorganisms do not contain a single culture of beneficial microorganisms but a mixture of different beneficial microorganisms; it is a village of good bacteria that are living together in harmony with the rest of nature. The term “indigenous microorganisms” refers to a group of beneficial microbes that are native to the area, thus the name indigenous (locally existing, or not imported); EMs or effective microorganisms on the other hand is a laboratory-cultured mixture of microorganisms. The main difference that divides these two ideas is that IMOs are naturally made, while EMs are man-made, but these two are very much the same with one another in all aspects. IMO-based Technology was actually developed and introduced by Dr. ChouHankyu in 1960s. He employed this technology in natural farms and observed amazing improvements in soil structure and plant health, as the soil upon IMO application regains its loaminess, tilth, structure and even the natural farmer friends, the earthworms, come into droves. Natural farming with IMO Technology is a distinctive approach in organic farming and it has been practised in more than 30 countries in their home gardens and also on a commercial scale. This technology was ritually followed by farmers of Korea, Japan, China, Malaysia, Thailand, Congo, Tanzania, Vietnam, Philippines, and Mongolia. Mr. Chou formulated and fine-tuned these practices and trained over 18,000 people at the Janong Natural Farming institute, south Korea. Later, the other scientist Dr. Hoonpark when in South Korea doing missionary work noticed the commercial piggeries and poultry farms with virtually no stinking smell up on IMO’s usage. This made him to bring IMO Technology to Hawaii. Dr. ChouHankyu has designed and introduced a new eco-friendly farming technology called Indigenous Microorganism technology which is beneficial to the farmers to develop sustainable agriculture and crop production (Cho and Koyama 1997). He developed this technology by the number of experiments conducted in his field studies. Finally, he concludes that natural farming is more advantageous over chemical farming. The techniques and methods employed by Chou are simple, practical, reliable, and economical.
Indigenous microorganisms are a group of innate microbial consortium that inhabits the soil and the surfaces of all living things inside and out which have the potentiality in biodegradation, nitrogen fixation, improving soil fertility, phosphate solubilisers and plant growth promoters (Umi Kalsom and Sariah 2006). Without these microbes, the life will be wretched and melancholic on this lively planet for the survival of human race. That is why, environmental restoration and safeguarding target via the indigenous microbes in a native manner to turn out the good for nothing and useless waste into productive bioresources is the primary concern of this review.
Indigenous microorganisms play an important role by protecting the normal host from invasion by microorganisms with a greater potential for causing disease. They compete with the pathogens for essential nutrients and for receptors on host cells by producing bacteriocins and other inhibitory substances, making the environment inimical to colonization by pathogens. They are the important component of world biodiversity (Sadi et al. 2006). These microorganisms increase the availability of nutrients to host plants (Vessey 2003) and increase the water-holding capacity, making the plants to have sufficient (or) enough water all the time. It improves the aeration to the plant roots such that exchange of gases takes place effectively and prevents soil erosion. Based on the collection sites, the process of collection and isolation methods are different as they may vary from place to place. Many environmental factors affect the rate of biodegradation potential and this involves both physical and chemical factors such as temperature, pH, organic matter, oxygen availability, availability of nutrients and so on. Indigenous microorganisms in each stage of composting were isolated and screened for the abilities to solubilise phosphate and produce indole-3-acetic acid (IAA). The potential microorganisms were selected for development of biofertilizer. The modified “Natural Farming” composting method is a simple, cheap, and fast method used to produce EFB compost that contains beneficial microorganisms with the potential to be developed into biofertilizer. Phua et al. (2011) particularly studied on the isolated indigenous microorganisms which may enhance plant growth through N2 fixation using the 15 N isotopic tracer technique, solubilise insoluble inorganic phosphate compounds or hydrolyse organic phosphate to inorganic P or stimulate plant growth through hormonal actions such as IAA production. Combination of microbial strains could be a good multifunctional biofertilizer for sustainable agriculture. The result derived from the IAA test showed that two isolates were IAA producers and six isolates produced clear zones on phosphate agar plates indicating phosphate-solubilising activity. Agro-waste management and enhancement of biodiversity are the approaches towards sustainability (Shukor 2009; Ong 2009).
Han et al. (2006) also showed that the combined treatment of Bacillus megaterium var. phosphaticum and B. mucilaginosus increased the availability of phosphorus and potassium in soil, and thus increasing the uptake and plant growth of pepper and cucumber. Sarma et al. (2009) reported that a combination of bioinocculents, namely, two Fluorescentpseudomonas strains, increased Vigna mungo yield by 300 % in comparison to the control crop. These results indicated that a combination of beneficial microorganisms might increase the nutritional assimilation of plant and total nitrogen in soil.
IMOs create the optimum and favourable environment to improve and maintain soil flora and soil fauna as well as the other microorganisms which in turn support the quality life of higher plants and animals including the human. Soil particles are lumped in aggregates and fostered to provide air and water retention, which in turn creates a good habitat for other symbiotic microbes. The IMOs are eco-friendly, environmentally safe and healthy with potential to create hunger-free environment. Better quality crops and livestock are assured due to the absence of synthetic chemical fertilizers and pesticides as inputs.
Bioleaching of heavy metals by indigenous microorganisms
For decades, concerned companies and local authorities have demonstrated interest in managing water from metallurgical and mining areas. After processing of mineral ores in metallurgical industries, the residual metals in effluent water would cause a substantial loss in revenue for metallurgical companies. Secondly, in view of environmental safety, these metals are potential pollutants of the water system. According to the South African National Standard (2005), an excess of calcium and iron in water could cause aesthetic or operational problems, while excess of magnesium in water could cause aesthetic and health problems. The process of removal of metals from the solutions through the physico-chemical techniques is called chemical leaching and if this process occurs through microorganisms, it is called bioleaching which can be done by indigenous, exogenous and genetically manipulated microorganisms. Compared to costly physico-chemical techniques, the biological techniques are found to be cheap and eco-friendly (Kefala et al. 1999; Cohen 2006; Alluri et al. 2007). Generally, metal removal efficiency greatly depends on the affinity between the metal and the microbial cell wall, and this can be achieved using indigenous microorganism isolated around mine areas.
Attempts are made at laboratory scale to remediate the high concentration of calcium, iron and magnesium in surface waters from metallurgical areas, using indigenous strains of Shewanella sp, Bacillus subtilis sp and Brevundimonas sp, which revealed variable abilities of these microorganisms in the removal process. Living and non-living biomass of all these strains will be tested for their effectiveness to clean out Ca, Mg and Fe predominant in surface water around mining areas in Nigel.
The inherent abilities of microorganisms are suitable for the removal of metals from solutions (Beveridge and Murray 1976; Langley and Beveridge 1999; Nies 1999). These abilities have been identified as passive or active for accumulation and biosorption, respectively, (Brandl and Faramarzi 2006). Indigenous strains are more suitable to overcome the challenges such as high concentration of metals, acidic conditions as they had adapted to conditions in situ. Bacillus strains have been widely used in the removal of metals (Pb, Cd, Cu, Ni, Co, Mn, Cr, Zn) from wastewaters (Philip and Venkobachar 2001; Srinath et al. 2003; Kim et al. 2007).
Metals are removed from the solutions through passive biosorption and active bioaccumulation. In biosorption, an anionic group (amino acids, hydroxyl, phosphate, etc.) on the bacterial cell membrane binds to the positively charged metal in solution where no energy is required during this process. Whereas in bioaccumulation, the metal is sequestered through the bacterial membrane into the cytoplasm of the cell; during this process, microorganisms use energy (ATP hydrolysis) to catalyse the reaction.
Bioleaching of heavy metals from sewage sludge using indigenous iron-oxidising microorganisms
Due to rapid population increase in the world, generation of potentially contaminated heavy metals is expected to be more in the sewage sludge than in the metropolitan cities. Prior to land application, traditional chemical methods such as EDTA extraction and acid treatment have been suggested for solubilisation of heavy metals from the sludge, but EDTA showed low removal efficiencies for Fe, Ni and Cr(Jenkins et al. 1981). The high cost and large consumption of chemical agents have made chemical methods unattractive. To overcome these problems, heavy metals in sewage sludge are removed through bioleaching process, the recently emerged strategy which is economical, easy operation, and non- hazardous to products (Babel and del Mundo Dacera 2006; Pathak et al. 2009). The experimental batch system studies by Xiang et al. (2000) showed that the isolated indigenous iron-oxidising bacteria have more ability in reducing the heavy metals from anaerobically digested sewage sludge from the Yuen Long wastewater treatment plant, HongKong. In this study, to maintain low pH and to accelerate the solubilisation of Cr, Cu, Zn, Ni and Pb, FeSo4 is added along with the isolated indigenous microorganisms. After 16 days of bioleaching, more than 80 % of Cu, Zn, Ni and Cd are removed as compared with that of the control. Similarly, Wen et al. (2013) studies on leaching kinetics show that solubilisation of heavy metals or removal efficiency is more by the indigenous iron-oxidising bacteria than without using indigenous microorganisms in the control ones which were collected from the Fuzhou Jingshan sewage water plant. In this study, after isolation of bacteria from the sludge, they were enriched by Wen et al. (2013) medium for three generations before the use of inoculum for bioleaching experiment (Ren et al. 2009). Solid concentration, pH, inoculum concentration, and FeSo4 effectively influence the bioleaching of metals. Effectiveness depends upon the metal species because of their different bindings in sludge; removal of Zn from the sludge was dominated by chemical leaching, while the removal of Cu, Pb and Cr was dominated by bioleaching (Wen et al. 2013).
The two species Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans have a great significance in bioleaching process (Tyagi et al. 1993; Chan et al. 2003). Here iron-based bioleaching is considered to be superior to sulphur-based bioleaching due to sludge acidification and heavy metal solubilisation in sulphur-based bioleaching (Wong and Gu 2008). To leach successfully, ammonium ferrous sulphate and ferrous sulphate are used to enrich the indigenous iron-oxidising microorganisms in sludge with a neutral pH (Pathak et al. 2009). Metal removal from dewatered metal plating sludge using A. ferrooxidans indicates that pH, oxidation–reduction potential (ORP), sulphate production, pulp density and agitation time were all important parameters in bioleaching (Bayat and Sari 2010).
Bioremediation of oil spills
Oil spills are treated as a widespread problem that poses a great threat to any ecosystem. Bioremediation has emerged as the best strategy for combating oil spills and can be enhanced by the following two complementary approaches: bioaugmentation and biostimulation. In bio augmentation, the addition of oil-degrading bacteria boosts biodegradation rates, whereas in biostimulation, the growth of indigenous hydrocarbon degraders is stimulated by the addition of nutrients (mainly N and P) or other growth-limiting nutrients (Nikolopoulou and Kalogerakis 2010). Crude oil is composed of a wide range of different compounds, which makes it difficult for the indigenous population to cope with this broad variety of substrates, and hence oil-degrading microorganisms could be added to supplement the indigenous population (Leahy and Colwell 1990). There is increasing evidence that the best approach for overcoming these barriers is the use of microorganisms from the polluted area. A new concept in bioaugmentation, known as "autochthonous bioaugmentation" (ABA), has been proposed by Ueno et al. (Ueno et al. 2007) and is defined as a bioaugmentation technology that exclusively uses microorganisms indigenous to the sites (soil, sand, and water) slated for decontamination. The success of oil spill bioremediation depends on the establishment and maintenance of physical, chemical and biological conditions that favour enhanced oil biodegradation rates in the marine environment. Through Biostimulation, the growth of indigenous oil degraders is stimulated by the addition of nutrients (nitrogen and phosphorous) or other growth-limiting co-substrates and/or by alterations in environmental conditions (e.g., surf-washing, oxygen addition by plant growth, etc.). The document issued by the Natural Biodegradation as a Remedial Action Option Interim Guidance (1994) illustrated the capabilities of an acclimated indigenous microbial consortium sampled from a pristine environment in the presence or absence of other rate-limiting factors (i.e., nutrients and biosurfactants) (biostimulation) as a potential strategy for the successful remediation of polluted marine environments (http://www.dnr.wi.gov/files/pdf/pubs/rr/rr515.pdf). Effectiveness of autochthonous bioaugmentation together with biostimulation versus biostimulation- only strategies for the successful remediation of polluted marine environments.
Many reports show that ozonation is effective in removing contaminants such as polyhydrocarbons in diesel-contaminated soils. (Hus and Masten 1997; Lim et al. 2002; Stehr et al. 2001; Sung and Huang 2002). As ozone has strong oxidising activity, it reacts with organic compounds to form oxidised products which are more or water soluble and bioavailable than parental compounds leading to a better biodegradation (Legube et al. 1981; Gilbert 1983). There are some reports given previously about the external introduction of microorganisms into ozonated soil (Nam and Kukor 2000; Stehr et al. 2001). But this external inoculation does not show promising result and caused a rapid decline of cell number and/or activity of inoculated cells (Van Veen et al. 1997). Therefore, employing already-acclimatised indigenous microorganisms could be an alternative to achieve successful remediation. Based on these ideas, (Ahn et al. 2005) developed the Pre-Ozonation and subsequent bioremediation technology for better degradation of polyhydrocarbons in the contaminated soils. Prolonged ozonation of diesel-contaminated soils for 0–900 min not only decreases the pH but also the viable indigenous bacterial concentrations. So, to increase the microbial number, the ozonated soils are incubated for 9 weeks and monitored by conventional culture-based methods (Plate count and Phenanthrene spray plate assay) and non-culture-based molecular methods (direct soil DNA extraction and catabolic gene probing). All taken together, this study is the first to monitor the potential of indigenous microorganisms to degrade pH in Ozonated soil.
Bioremediation of 2,4-D in soils using nanoparticles Fe3O4 and indigenous microbes
Fang et al. (2012) studied the degradation kinetics of 2,4-D in soils by Fe3O4 nanoparticles and indigenous microbes. In this study, the degradation efficiency of 2,4-D was investigated in three different treatments: indigenous microbes, Fe3O4 nanoparticles, or combined use of Fe3O4 nanoparticles and indigenous microbes. The results indicated that the combined use of Fe3O4 nanoparticles and indigenous microbes led to greater mineralisation of 2,4-D to its degradation products, 2,4-DCP,chlorophenol (2-CP, 4-CP) and phenol, than the treatments with Fe3O4 nanoparticles or indigenous microbes alone, and is more advantageous in remediation of soil contaminated with herbicides.
Arsenic (As) is a notorious toxic metalloid which is of geogenic and anthropogenic origin. It is prevalent in many regions of the world (Mandal and Suzuki 2002; Tripathi et al. 2007). Generally, inorganic arsenic species are believed to be more toxic than organic forms to living organisms, including humans and other animals (Goessler 2002; Meharg and Hartley‐Whitaker 2002). Microbes developed various intrinsic As tolerance mechanism to sustain in the adverse environmental conditions. Metal-resistant bacteria often have genes located on plasmids. Genetic system named ars operon is the main functional unit for As resistance (Mukhopadhyay and Rosen 2002). The toxicity of different arsenic species was often reported to vary in an order of arsenite > arsenate > mono-methylarsonate (MMA) > dimethylarsinate (DMA) (Penrose and Woolson 1974; Sturgeon et al. 1989).
Bioremediation of As by microorganisms has been widely hailed because of its cost-effective process and eco-friendly in nature (Valls and Lorenzo 2002). Conversion of metalloids to their volatile derivatives by organisms is a well-known phenomenon in nature (Challenger 1945). During arsenic volatilization, some species of fungi and bacteria methylate inorganic As species to relatively less-toxic volatile methylarsenicals (Rodriguez et al. 1999; Cernansky et al. 2009).
The investigations by Majumder et al. (2013) shows that the indigenous bacterial isolates AMT-08 and AGH-09 showed higher As volatilizing capacity under aerobic conditions; ADP-18 volatilized maximum As under anaerobic conditions, while AMT-04 performed well in both conditions. The bacterial strains isolated from arsenic-contaminated soils have shown much higher resistance to As volatalization than those isolated from soil, gold mines, and geothermal effluents in the related researches throughout world (Saltikov and Olson 2002; Simeonova et al. 2004). AMT-08 has been found most successful in managing the removal of the metalloid from soil throughout the entire incubation period; it removes 10 % (in 30 days) and 16 % (in 60 days) As when supplemented with farm yard manure. The strain AMT-08 has an increased As volatilizing ability with exogenous nutrients (farm yard manure) and successful exploitation of these hyper-tolerant isolates may deliver an eco-friendly tool for As mitigation within manageable expenditure as compared to the genetically engineered ones.
The bacterial strains under the present investigation were isolated from anaerobic soil environment (submerged paddy soil) which is predominated by AsIII over AsV and hence showed much higher tolerance to AsIII as compared to findings from related research established as a model microorganism for bioremediation of arsenic and one of the most arsenic-resistant microorganisms (400 mM for AsV and 60 mM for AsIII) described to date (Mateos et al. 2010).
Role of indigenous microorganisms in natural farming
Natural farming is the propagation of mycorrhizae, by adding specific inputs during the nutritive cycle of the plant. Mycorrhizae are “fungus roots” which act as an interface between plants and soil. They grow into the roots, increasing the root system many thousands of times over. They act symbiotically and convert the complex substrates to simpler ones. Miles of fungal filaments can be present in an ounce of healthy soil. Mycorrhizal inoculation of soil increases the accumulation of carbon by depositing glomalin, which in turn increases soil structure by binding organic matter to mineral particles in the soil. Natural farming with IMO is a distinctive approach to organic farming practised successfully in more than 30 countries, in home gardens and on a commercial scale. Amazing improvements have been seen in soil structure and plant health, as upon application of indigenous microorganisms in natural farming the soil regains its loaminess, tilth and structure, and the earthworms come in droves. Mr Cho formulated and fine-tuned these practices for 40 years and has trained over 18,000 people at the Janong Natural Farming Institute (janonglove.com), and the dedicated work of Dr. Hoon Park brought Natural Farming to Hawaii. Dr. Park was in South Korea doing missionary work and noticed commercial piggeries with virtually no smell that were using Natural Farming methods. Mr. Cho has spread Natural Farming worldwide and planted the trees in Gobi Desert, Mongolia but had failed three times earlier, under the harsh wind and with only few inches of rainfall a year. With Natural Farming methods, the trees had a 97 percent survival rate and are now 20 feet tall. Corn and barnyard grasses have been planted for livestock feed, and wells have been dug. Watermelon farming now provides a stable income to farmers there also. As he learned more about these practices, he realized that they could help eliminate hunger and poverty in extremely poor parts of the world.
Cultivation of indigenous microorganisms
IMO-1—Cultured in a simple wooden box of rice;
IMO-2—Mixed with brown sugar and stored in a crock;
IMO-3—Further propagated on rice bran or wheat mill run;
IMO-4—Mixed with clay soil/ant hill soil;
The result is then mixed with compost, added to potting soil, or spread on beds before planting. The entire process takes three to 4 weeks. Other inputs and sprays are made from fermented plant juices, made from the tips of growing plants mixed with brown sugar. There are also recipes for water-soluble calcium made from eggshells, fish amino acid made from fish waste, lactic acid bacteria and insect attractants made from rice wine. There is also water-soluble calcium phosphate made from animal bones which are used according to the nutritive/growth cycle of the plants. The fish amino acids are simply fresh fish waste, de-boned and packed into a container with brown sugar and fermented for a few months. The pigs’ excrement is so odourless, clean and dry, that you literally do not even have to clean it out. The benefits of using the Natural Farming methods include the following:
Lower costs to the farmer (by as much as 60 percent)
More desirable crops
Stronger, healthier and more nutritious plants
Zero waste emission.
The inputs are made from natural materials, which are not only safe for the environment, but actually invigorate and rehabilitate the ecology.
Biocomposting by indigenous microorganisms
Agro-industrial wastes have become a major problem in terms of disposal because most farmers dispose them through burning. This inexpensive method of crop residue disposal is practised in many parts of the world to clear the excess residue from land for faster crop rotation, control undesirable weeds, pests and diseases and to return some nutrient to the soil. Open burning emits a large amount of harmful air pollutants (particles and inorganic and organic gases), which have severe impact on human health, polycyclic aromatic hydrocarbons (PAHs) (Korenaga et al. 2001) and the danger of soil erosion due to repeated burning (Kahlon and Dass 1987). In addition, disposal in water bodies (for example, river or lake) may contribute to a decrease in water quality. Because of these concerns, there is a need to find efficient alternatives for agro-industrial waste management. Many alternatives for the disposal of these residues have been proposed, composting being one of the most attractive on account of its low environmental impact and cost (Bustamante et al. 2008; Canet et al. 2008; Lu et al. 2009) as well as its capacity for generating a valuable product used for increasing soil fertility (Weber et al. 2007) or as a growing medium in agriculture and horticulture (Perez‐Murcia et al. 2005). To manage Paddy husk and Corn Stalk residues through composting, a study was conducted by Hanim et al. (2012) to determine the physical and chemical properties of different composts and humic acid extracted from the final product. For this study, they took paddy husk, corn stalk and kitchen waste with different concentrations as the substrate (organic source) and to this they added the IMO compost in six different treatments i.e. T1 to T6.and the results showed that IMO compost from Corn stalk had better quality (chemical characteristics) compared to that of paddy husk.
Summary and conclusion
Currently, environmental sustainability is a contemporary issue that receives plenty of attention from the research scientists. This is a result of the amount of research going into assessing the impact that human activity can have on the environment. Although the long-term implications of this serious issue are not yet fully understood, it is generally agreed that the risk is high enough to merit an immediate response. As stated earlier, indigenous microorganisms-based technology is one such important technology and these organisms inhabit the soil with the abilities of biodegradation, bioleaching, biocomposting, nitrogen fixation, improving soil fertility and as well in the production of plant growth hormones. In addition, these are large group of naturally occurring and often unknown or ill-defined microorganisms that interact favourably in soils and with plants to render beneficial effects which are sometimes difficult to predict. Indigenous microorganisms usually denote specific mixed cultures of known, beneficial microorganisms that are being used effectively as microbial inoculants that could exist naturally in soil or added as microbial inoculants to soil where they can improve soil quality, enhance crop production and create a more sustainable agriculture and environment. IMOs coexist and are physiologically compatible and mutually complementary, and if the initial inoculum density is sufficiently high, there is a high probability that these microorganisms will become established in the soil and will be effective as an associative group, whereby such positive interactions would continue. If so, then it is also highly probable that they will exercise considerable control over the indigenous soil microflora in due course. Still lot of constructive research is required to make use of IMOs in sustainable environment.
Authors are very much thankful to Department of Virology, Sri Venkateswara University for providing necessary facilities to implement IMO research.
Conflict of interest
Authors hereby declare no conflict of interest.
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