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Core Microbiome


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is used in bioremediation to break down toxic pollutants and other harmful substances, minimizing the toxicity of metallic contaminants in organic residues, wastes, and by-products. After the composting process stabilizes the waste, it can be disposed to landfills or farmland (Ankidawa and Nwodo 2011). The stabilized organic matter can also form complexes and restrict metal flow and enhance absorption in plants.

      The microbial activity during composting helps in the decomposition of pesticides in the soil. A report suggests that the pesticide content is present in composts following the breakdown of pesticides during composting (Wu and Ma 2000). The addition of compost is known to enhance the degradation of two herbicides viz., benthiocarb S-4-chlorobenzyl diethylthiocarbamate (benthiocarb) and 4-chloro-2-methylphenoxyacetic acid (MCPA) in soils. The soil amended with compost improved the breakdown of a fumigant (1, 3-dichloropropene) in comparison with the soil without compost. The concentration of pesticides was at safe levels for plants in soils due to the application of compost.

      4.2.5 Compost in Horticulture as the Supply of Minerals to Crops and Other Plants

      Compost application is beneficial in horticulture as an effective means of recycling; it also minimizes the use of chemicals and harmful fertilizers. Compost has been trialed for the grapevine (Powell et al. 2007). Based on the benefits of compost, it can enhance water absorption and minimize the need for irrigation. Compost is also an exciting peat substitute. Compost added to soil has improved the biomass of crops and has increased N, P, and K uptake (Miller et al. 2015). There is a report on a significant increase in the growth and biomass of Anemone coronaria L. cv. Red meron (Aydinsakir et al. 2009).

      Phosphorus is a crucial central element for plant growth. Compost usually provides 6–8 kg of plant-available phosphorus, which is around 65–90 kg super-phosphate. Compost use increases soil phosphorus supply by releasing inorganic phosphorus through the mineralization of organic phosphorus (Wang et al. 2010).

      Compost normally contains 0.8–1.2% potassium. Therefore, with 1.0% (w/w) potassium content, 10 m3 of mature compost will contain 40 kg of potassium, providing 36 kg of plant-available potassium, equivalent to 90 kg of potassium sulfate. When applied to soil, municipal waste compost increased the amount of nitrogen, phosphorus, and potassium available for plants (Soheil et al. 2012). Compost-amended soils contain nutrients (macro and micronutrients) for plant growth (Brown and Cotton 2011).

      Compost is used in orchards and vineyards. There has been a report on improved growth and yield of citrus, avocado, apples, and table and wine grapes due to the application of compost during planting (Buckerfield and Webster 2003). The application of compost and compost mulches in fruit and vineyards can be advantageous when growing conditions are less stringent; soils are more impoverished, especially when less water is available. Thus, compost can be used to increase uniformity and, hence, enrich the entire orchard and vineyard.

      Adding compost to vegetable cultivation has reduced the use of chemicals and harmful pesticides by 80%. It has also minimized the detrimental effects of intensive cropping on soil performance and quality of water. Compost also increased the ability to hold cations, viz., potassium due to which there was a 20% reduction in the requirement of potassium for vegetable crops.

      Compost has improved the yield of lettuce, carrot, broccoli, etc. There is a report on the increase in red pepper yield due to compost application (Park et al. 2018). The soil mixed with 25% compost showed an increase in the yield of cabbage and onion (Smith et al. 1992). Increased growth on the use of compost as fertilizer has been reported on onion and lettuce (Brechin and McDonald 1994), tomatoes (Manios and Kapetanios 1992), barley (Hountin et al. 1995), and rice (Charfen 1981).

      4.3 Use of Compost in Mulching

      4.4 Perspectives

      The compost-turning machines market is estimated to reach around US$ 150 million by 2028. These developments will also increase the volume of sales of waste-management equipment. The drum type compost machine will become the dominant compost machine in the market. It is expected that there will be a tremendous demand for compost-turning machines. Agriculture will benefit due to the use of compost-turning machines. Different types of waste generated in cities can be used to make value-added products, i.e., compost by solid-state fermentation (SSF) method (Farrell and Jones 2009). These value-adding products (composts) are considered to be eco-friendly, economical, and non-toxic, and they help promote sustainable agriculture without causing any pollution and not causing any harm to plants and the environment.

      4.5 Conclusion

      Compost is an excellent soil conditioner and can enhance the growth of crops and many plants due to the supply of various nutrients, viz., nitrogen, phosphorus, and potassium, and minerals, and this will thus be very helpful to many farmers. The use of chemical fertilizers can be minimized, thanks to the application of compost to the soil, and it is also very cost-effective. Also, compost increases microbial diversity, which is vital for the soil ecosystem. The application of compost will be beneficial for organic farming and agricultural sustainability.

      References

      1 Adugna, G. (2016). A review on impact of compost on soil properties, water use and crop productivity. Academic Research Journal of Agricultural Science and Research 4: 93–104.

      2 Anastasi, A., Varese, G.C., and Marchisio, V.F. (2005). Isolation and identification of fungal communities in compost and vermicompost. Mycologia 97: 33–44.

      3 Ankidawa, B.A. and Nwodo, E. (2011). Recycling biodegradable waste using composting technique. Journal of Environment Science and Resources Management 4: 40–49.

      4 Awasthi, M.K., Pandey, A.K., Khan, J., Bundela, P.S., Wong, J.C., and Selvam, A. (2014). Evaluation of thermophilic fungal consortium for organic municipal solid waste composting. Bioresource Technology 168: 214–221.

      5 Aydinsakir, K., Unlu, A., Yilmaz, S., and Ari, N. (2009). The effects of compost applications on yield and quality characteristics of Anemone coronaria L. cv. red meron. Acta Horticulturae 807: 359–364.

      6 Bellamy, P.H., Loveland, P.J., Bradley, R.I., Lark, R.M., and Kirk, G.D. (2005). Carbon losses from all soils across England and Wales 1978–2003. Nature 437: 245–248.

      7 Bonilla, N., Gutierrez-Barranquero, J.A., de Vicente,