Journal of Pollution Effects & Control

Journal of Pollution Effects & Control
Open Access

ISSN: 2375-4397

Review Article - (2020)Volume 8, Issue 5

Palm Oil Mill Effluents (POME) and its Pollution Potentials: A biodegradable Prevalence

Adegbola Grace Mosunmola1 and Simeon Kayowa Olatunde2*
 
*Correspondence: Simeon Kayowa Olatunde, Department of Pure and Applied Biology, Ladoke Akintola University of Technology, Nigeria, Tel: 2348060722089, Email:

Author info »

Abstract

Palm Oil Mill Effluent (POME) refers to the effluent obtained from palm oil production in the mill at the final stage. It shows the presence of residue oil and suspended solids, its potentials to pollute both ecological niches have been attributed to the most intricate environmental turmoil for the 21st century. The use of biotechnological processes involves microorganisms, with the sole aim of providing a solution to environmental pollution problems, this is rapidly growing in recent decades where POME hydrocarbons and its derivatives are concerned. This paper presents a state of the art review on palm oil mill effluent pollution, prevalence, remediation methods, its environmental potentials and biodegradation as a panacea. However, the significant development of its execution, major limitations together with the future expectation are summarized and discussed. Conclusively, hydrocarbons are been removed by both mechanical and chemical methods from the hydrocarbons-polluted site have restricted viability and can be expensive, thus, Biodegradation remains the promising technology for the treatment of polluted site because of its cost-effectiveness and complete mineralization.

Keywords

Biodegradation; Environmental pollution; Palm oil mill effluent and microorganisms

Introduction

Palm oil mill effluent (POME) which is also known as Palm oil effluent (POE), Palm oil slurry (POS), Palm oil sludge (POS), Oil palm slurry (OPS), oil palm sludge (OPS), decanter cake etc., Among all territorial name been given, Palm oil mill effluent seems to summarize it's content which is defined as the voluminous liquid waste that originates from the sterilization and clarification forms in milling oil palm. It is wastewater produced from palm oil milling exercises which require successful treatment before release into nature because of its exceptionally polluting properties. Thus, POME is being treated via palm oil mills before evacuating it into the streams and rivers. Palm oil mill effluent is termed to be a highly polluting material and researchers have done so much in their studies to find ways of removing its threat to the environment. The composition of the effluent is from different sources and are obtained from palm oil, water, sand and solid (suspended and dissolved). Water which composed of 93-95%, solidly composed of 3-4% and oil composed of 0.5-2% are various composition as a percentage of total sludge [1].

The use of biotechnological forms including microorganisms, with the target of taking care of environmental contamination issues, is quickly developing, in ongoing decades, where POME and its sideeffects are concerned. Microbial Degradation forms, which exploit microbial breaking down of organic and inorganic substances, can be defined as the use of microorganisms to remove environmental pollutants of soils, water and sediments [2].

The process by which microorganisms such as bacteria, fungi and other biological activity act on material by naturally disintegration is called Biodegradation. The biological treatment relies immensely upon a consortium of microorganism's activities, which operate the organic substances present in the POME as enhancements and in the end debase these organic issues into a simple by-product, for example, methane, carbon dioxide and hydrogen provided, and water. The biological treatment process requires a huge pond to hold the POME set up for the successful biodegradation, which routinely takes a couple of days depending upon the sort and native of the microorganisms [3]. Besides, to improve the viability of this medication procedure, incredible mono or joined the culture of plausible fungi and microscopic organisms in biodegradation treatment of POME waste. Accordingly, the problem of converting POME into an environmentally benevolent waste requested a proficient treatment and viable disposal strategies.

Prevalence of Pome

The palm oil industry has turned out to play an essential role in agricultural industries based in Indonesia and Malaysia which produce a great amount of oily liquid wastewater globally referred to as palm oil mill effluent (POME) [4-6]. Nowadays, the palm oil business is developing rapidly and transforming into an imperative agriculture-based industry in these two countries.

The numbers of palm oil factories have increased generally, at starting with 10 plants in 1960 moved to 410 operating mills in 2008 in Malaysia. At least 44 million tons of POME was produced and are expanding each year in Malaysia [7], especially as a result of the activity of the legislature to advance the palm oil industry. While the palm oil industry has been perceived emphatically for its commitment toward monetary development and quick improvement, it has additionally added to environmental pollution because of the creation of huge amounts of by-products during the process of oil extraction [7,8].

The two greatest oil palm producing nations are Malaysia and Indonesia situated in Asia. They are rich in endemic and forestdwelling species [9]. Malaysia is a tropical rainforest region and is Palm Oil prosperous nation with regular assets. Presently, Oil palm includes the biggest real acreage of cultivated land in Malaysia [10,11]. The total oil palm grounds from 1970 to 2000 has extended from 320 to 3338 ha. In the year 2003, there was more than 3.79 million ha of land under palm oil development, possessing over 33% of the complete developed region and 11% of the absolute land region of Malaysia [11,12]. Palm oil, palatable oil, is gotten from the substantial mesocarp of the fruit of oil palm (Elaeisguineensis).

One hectare of oil palm produces 10–35 tons of fresh fruit bunches (FFB) per year [13]. Malaysia produces about 41% of the world’s supply of palm oil and as at the year 2005, Malaysia accounts for the world highest percentage of global vegetable oils and fats trade [14]. The expectancy of oil palm is over 200 years and has about 20-25 years of economic life. It takes 11-15 months of the nursery period for plants and 32-38 years for the first harvest for the month of planting. It takes 5–10 years for palm oil plant to reach the highest yield. The global production of palm oil is shown in 2007 and ten years after is shown in Figures 1 and 2.

pollution-effects-control-oil-production

Figure 1: World palm oil production in 2007 [3].

pollution-effects-control-world-palm

Figure 2: World palm oil production in 2017 [15].

Various Means of Remediating Pome

Bacteria as Hydrocarbon Degraders

In recent years, many microbial ecologists have identified various microbial species that are effective degraders of hydrocarbons in natural environments. Hydrocarbon biodegradation and its level of persistence in the environment are influenced by different factors which include the presence of viable microbial biomass that are capable of degrading the hydrocarbon pollutants, hydrocarbon chemical structures and the optimal environmental conditions that can support the activities of microbial degradation [15,16]. Many of these microbial consortia have been isolated from heavily contaminated areas. They were isolated base on their capacity to utilize different carbon sources, for example, aliphatic and fragrant mixes and their chlorinated derivates. The driving force for hydrocarbons biodegradation is the capability of microorganisms to utilize hydrocarbons to satisfy their energy needs and cell growth. Consortia cultures of microorganisms complete more broad biodegradation of oil than unadulterated cultures [16]. In numerous ecosystems, there is now a satisfactory indigenous microbial community equipped for broad oil biodegradation, given that ecological conditions are positive for oil-debasing metabolic action [17].

Phytoremediation (Green aquatic plants)

Due to the organic nature, POME is highly polluting for example the ecosystem can be devastated by the high content of COD and BOD including heavy metals and its discharge to an environment.

Also, a huge amount of nutrients such as phosphorous, nitrogen and potassium are present in this waste [18], which is potential for algae growth medium. To decrease these waste loads, POME is commonly treated through biological procedures in facultative anaerobic ponds, anyway, the effluent emanating of these ponds is still greater than the threshold limit required by Indonesia Government.

Phytoremediation is defined as an economic method used to decrease the waste load in soil and wastewater. It includes the application of green aquatic plants such as water hyacinth, lotus, or by the free-living organisms i.e. microalgae or microscopic organisms that comprise the plant's rhizosphere to remove unsafe environmental toxins, for example, overwhelming metal, pesticides and xenobiotics, a natural compound, poisonous sweet-smelling contaminations and corrosive mine waste [19-21] shown the breakthrough research of phytoremediation by applying aquatic plants and as well decreased heavy metals (Al3+, Fe3+, Zn2+, Pb2+) in industrial wastewater using cumbungi (Typhadomingensis). Meanwhile, Kutty et al. [22] also agreed with the work of Ajayi and Ogunbayio [24] which utilized water hyacinth (Eichhorniacrassipes) as a bio-accumulator plant for municipal wastewater treatment. However, these research outputs focused majorly on the single phytoremediation to decrease waste contaminant, without taking any necessary action and as well on how to reapply further the effluent out of the remediation process.

The treated wastewater from sea-going plants phytoremediation despite everything contains high supplements which may be potential growth medium of microalgae. Study on the utilization of microalgae for wastewater treatment was analysed since the 1960s [23]. The recent application of microalgae for wastewater treatment has been shown by Hadiyanto et al., [22]. In that study, Hadiyanto et al., [24,25] showed that microalgae could reduce the contaminant load in palm oil mill effluent up to 70%. Furthermore, some researches such as Markou et al. [26] use olive Oil Mill Waste Water (OMWW) as a means for the growth of algae. Kitchen wastewater treatment with a variation of wastewater composition via the application of phytoremediation technology by Jongkon et al. [27].

Hadiyanto et al.,[22] study was set with a specific objective to diminish the waste contaminants by two stages phytoremediations, for example, amphibian plants and microalgae plants, respectively. By utilizing two phases of phytoremediation, they expected that the waste load can be decreased up to 98% while the biomass of green algae can likewise be acquired.

Biofilm technology

Biofilm technology used for the first time in year 1990s, for treating wastewater in Norway [28]. Numerous microbes use nutrients (organic and inorganic matters) to build a biofilm colony. Initially, the microbes connect to a reasonable surface; at that point, it begins building up the colony. Biofilm treatment has numerous focal points contrasted with ordinary POME treatment methods. For example, high movement biomass, strength to the environmental changes, diminished hydraulic retention time, low space required, adaptability in the treatment activity, and improved capacity to degrade recalcitrant compounds [29]. In 2010, the World Health Organization (WHO) had shown that 780 million people have no way to get suitable water for drinking. That issue had raised considerable concern to provide well treatment [30]. For producing high-quality water, the system involved the membrane treatment. Al-Amshawee et al., [31] had integrated Membrane with Biofilm treatment to produce a high-quality treatment.

Environmental Potentials of Pome Pollution

POME contains a great amount of acidic content, temperature, Biological Oxygen Demand (BOD), and Chemical Oxygen Demand (COD). At the point when it is released into streams it can defile drinking water for the human and animal community. The crude effluent contains 90-95% water and incorporates residual oil, soil particles and suspended solids. A modern oil palm plant produces about 2.5 t of effluent per ton of palm oil, or 0.5 ton of effluent per ton of new fresh fruit [16]. Palm oil plant effluent is an exceptionally a polluted substance and much exploration has been devoted to methods for reducing its danger to the human environment.

It tends to cause danger to the aquatic environment by making profoundly acidic conditions or causing eutrophication (where extreme algal growth happens on the surface of the water). POME contributes to global climate change when released into open-air holding ponds for remediation, thus causing methane, carbon dioxide and hydrogen sulphide to be released [32].

Biodegradation as a Panacea to Pome Pollution

Palm Oil as a lipid derives its distinctive properties from the hydrocarbon nature of a major portion of the structure. The molecules are composed of long chains of carbon atoms. The hydrocarbon group is modified by the presence of small numbers of more reactive polar groups [33]. The chains can exist in several bonds but have long saturated and unsaturated monocarboxylic aliphatic pure acids. Since the major portion of the lipids in the hydrocarbon, some microorganisms have been reported to degrade oil generally causing rancidity [34].

Even though Palm fruit has been recognised to be the major source of lipase producing microorganisms, yet, studies have shown that for organisms to degrade palm oil, it must be able to produce lipase, Besides the presence of lipids and other volatile compounds, the inhibitory effects of POME on living tissues could also be due to presence of water-soluble phenolic compounds. Nilanjana et al., [35] stated that the enumeration of microorganisms and assessment of the activity of soil enzymes provide an integrative measure of the biological status of the soil. Because of these, Oyeyiola et al., [36] observed that Bacteria, Algae, Fungi, Actinomycetes, Protozoa and Viruses are the types of predominant microorganisms found in the soil. Filamentous fungi, Yeast and Bacteria have been studied by numerous authors and their findings show that they are efficient in degrading a large number of organic substances commonly found in effluents generated by oil refineries [37].

However, Pooja et al. [38] pointed out that the degradation of hydrocarbons in soil may be limited by the inability of indigenous microorganisms to efficiently metabolize these substances due to a lack of nutrients for the degrading microbiota or to a low biovailability of hydrocarbons to degrading micro-organisms. Similarly, Eze et al., [37] studied the microbiological and physicochemical characteristics of soil receiving Palm Oil Mill Effluent in Umuahia, Abia State of Nigeria. They characterised and identified Pseudomonus aeruginosa, Staphylococcus aureus, Klebsiella species, Proteus species, Bacillus species and Citrobacter species as hydrocarbon-utilizing isolates and proceedings from their studies has served as baseline information in the present studies.

The response of resident bacteria to crude oil-polluted rivers with diesel oil was also examined [39]. They opined that bacteria species are more tolerant to varying concentrations of the diesel oil and therefore referred to such set of organisms as POME Tolerant Bacteria (PTB).

Major Challenges and Future Prospects

A variety of microorganisms have been investigated to be capable of biodegrading oil wastewater with high profits. Anaerobic and aerobic medicines are extraordinary and proficient biological techniques for POME treatment. Nonetheless, the suspended and colloidal segments are neither viably decayed biologically nor by other regular methods because their floating on the surface of the wastewater affects the microbial cycle [40]. It is the major challenge to cause setback of the treatment system. Especially, the significant component of biological intake, microorganism assumes a significant role and major factor of the system to control reactor stability and performance. In other words, a mix of wastewater treatment and inexhaustible bio-energies creation would be an additional bit of leeway to the palm oil industry. Furthermore, the prospect of the future lies in the fact that degrading microorganisms can be isolated from POME polluted area and the degrading ability of these microorganisms is a clear indicator that these bacteria can be applied in the bioremediation techniques for biodegradation of POME to enhance treatment.

Conclusion

Palm oil is one of the world's most rapidly expanding equatorial crops. Even though Nigeria was the incepted palm oil-producing country, Indonesia and Malaysia remains the two largest oil palm producing countries and is rich with numerous endemic, forestdwelling species. Discharging the effluents or by-products on the lands may lead to pollution and might cause deterioration of the environment. The treatment of these by-products requires a productive and efficient management system that will preserve the environment and check the deterioration of run water and air quality. Treatment of POME is highly important and environmental pollution must be avoided.

Therefore, the indigenous microbial strains are promising organisms for industrial usage. These microbes have direct applications in the industrial process such as bioremediation and biodegradation of wastewaters.

References

  1. Madaki YS, Lau Seng L. Pollution control: how feasible is zero discharge concepts in malaysia palm oil mills. Am J Engineering Research, 2013;2:239-252.
  2. Pala DM, Carvalho DD, Pinto JC, L. Sant’Anna G Jr. A suitable model to describe bioremediation of a petroleum-contaminated soil. International Biodeterioration and Biodegradation, 2006;58:254-260.
  3. Aziz AH. Reactive extraction of sugars from oil palm empty fruit bunch hydrolysate using Naphthalene-2-Boronic acid [Doctoral dissertation]. Universiti Sains Malaysia; 2007.
  4. Ahmad AL, Ismail S, Bhatia S. Optimization of coagulation-flocculation process for palm oil mill effluent using response surface methodology. Environmental Science and Technology. 2005;39:2828-2834.
  5. Rupani PF, Singh RP, Ibrahim MH, Esa N. Review of current palm oil mill effluent (POME) treatment methods: Vermicomposting as a sustainable practice. World Applied Sciences Journal. 2010;11(1),70-81.
  6. Mohammed RR, Ketabachi MR, McKay G. Combined magnetic field and adsorption process for treatment of biologically treated palm oil mill effluent (POME). Chemical Engineering Journal. 2014;243,31-42.
  7. Parthasarathy S, Mohammed RR, Fong CM, Gomes RL, Manickam S. A novel hybrid approach of activated carbon and ultrasound cavitation for the intensification of palm oil mill effluent (POME) polishing. Journal of Cleaner Production. 2016;112,1218-1226.
  8. Singh RP, Ibrahim MH, Esa N, Iliyana MS. Composting of waste from palm oil mill: A sustainable waste management practice. Reviews in Environmental Science and BioTechnology. 2010;9(4),331-344
  9. Shafiqah N, Nasir M. Development of membrane anaerobic system (MAS) for palm oil mill effluent (POME) treatment. Universiti Malaysia Pahang; 2013.
  10. Arif S, Tengku Mohd Ariff TA. The case study on the Malaysian palm oil. In: UNCTAD/ ESCAP Regional Workshop on Commodity Export Diversification and Poverty Reduction in South and Southe-East Asia, Bangkok; 2001.
  11. Hansen S. (2007) Feasibility study of performing a life cycle assessment on crude palm oil production in Malaysia (9 pp). The International Journal of Life Cycle Assessment. 2007;12(1),50-58.
  12. Yusoff S, Hansen SB. Feasibility study of performing of life cycle assessment on crude palm oil production in Malaysia. The International Jounal of Life Cycle Assessment. 2007;12(1),50-58.
  13. Abdullah AZ, Salamatinia B, Mootabadi H, Bhatia S. Current status and policies on biodiesel industry in Malaysia as the world’s leading producer of palm oil. Energy Policy, 2009;37(12),5440-5448.
  14. Sumathi S, Chai SP, Mohamed AR. Utilization of oil palm as a source of renewable energy in Malaysia. Renewable and Sustainable Energy Reviews, 2008;12(9),2404-2421.
  15. Chikere CB, Ekwuabu CB. Culture-dependent characterization of hydrocarbon utilizing bacteria in selected crude oil-impacted sites in Bodo, Ogoniland, Nigeria. African Journal of Environmental Science and Technology, 2014;8(6),401-406.
  16. Sohn JH, Kwon KK, Kang JH, Jung HB, Kim SJ. Novosphingobium pentaromativorans sp. nov., a high-molecular-mass polycyclic aromatic hydrocarbon-degrading bacterium isolated from estuarine sediment. International Journal of Systematic and Evolutionary Microbiology, 2004;54(5),1483-1487.
  17. Yejian Z, Hairen Y, Xiangyong Z, Zhenjia Z, Li Y. High-rate mesophilic anaerobic digestion of Palm Oil Mill effluent (POME) in expanded granular sludge bed (EGSB) reactor. International Conference on Agricultural and Natural Resources Engineering. Advances in Biomedical Engineering, 2011;3(5),214-219.
  18. Susarla S, Medina VF, McCutcheon SC. Phytoremediation: An ecological solution to organic chemical contamination. Ecological Engineering, 2002;18,647-658.
  19. Vangronsveld J, Herzig R, Weyens N, Boulet J, Adriaensen K. Phytoremediation of contaminated soils and groundwater: Lessons from the field. Environmental Science and Pollution Research International, 2009;16,765-794.
  20. Hegazy AK, Abdel-Ghani NT, El-Chaghaby GA. Phytoremediation of industrial wastewater potentiality by Typha domingensis. Internatinal Journal of Environmental Science and Technology, 2011;8,639-648.
  21. Kutty SRM, Ngatenah SNI, Isa MH, Malakahmad A. A nutrients removal from municipal wastewater treatment plant effluent using Eichhornia crassipes. World Academy of Science, Engineering and Technology, 2009;36,828-833.
  22. Hwang J, Church J, Lee S, Park J, Lee WH. Use of microalgae for advanced wastewater treatmentand sustainable bioenergy generation. Environmental Engineering Science, 2016;33(11),882-897.
  23. Ajayi TO, Ogunbayio AO. Achieving environmental sustainability in wastewater treatment by phytoremediation with water hyacinth (Eichhornia crassipes). Journal of Sustainable Development, 2012;5,80-90.
  24. Hadiyanto, Marcelinus C, Danny S. Phytoremediations of Palm Oil Mill Effluent (POME) by using aquatic plants and microalge for biomass production. Journal of Environmental Science and Technology, 2013;6(2),79-90.
  25. Markou G, Chatzipavlidis I, Georgakakis D. Cultivation of arthrospira (Spirulina) platensis in olive-oil mill wastewater treated with sodium hypochlorite. Bioresources Technology, 2012;112:234-241.
  26. Jongkon, P, Siripen T, Richard DL. The optimum N:P ratio of kitchen wastewater and oil-extracted fermented soybean water for cultivation of spirulina platensis: Pigment content and biomass production. International Journal of Agriculture and Biology, 2008;10,437-441.
  27. http://technomaps.veoliawatertechnologies.com/processes/lib/pdfs/productbrochures/anox/DE96X46q57VLAFRUI CYUamGQ.pdf.
  28. Lazarova V, Jacques M. Innovative biofilm treatment technologies for water and wastewater treatment. ChemInform, 2010;31.
  29. Broens H, Knops F, Hoof V. Economic evaluation of a new ultrafiltration membrane for pretreatment of seawater reverse osmosis. Desalination, 2007;203,300-306.
  30. Sajjad AA, Teow YH, Wahab A. Sustainable approach of recycling palm oil mill effluent (pome) using integrated biofilm/membrane filtration system for internal plant usage, Jurnal Teknologi (Sciences & Engineering) 2018;80(4),165-172.
  31. Chavalparit A. Palm oil mill effluent, Feedipedia, a programme by INRA, CIRAD, AFZ and FAO. 2015.
  32. Okoh A, Ajisebutu S, Babalola G, Trejo-Hernandez M. Potential of burkholderia cepacia RQ1 in the biodegradation of heavy crude oil. International Microbiology, 2001;4,83-87.
  33. Elijah IO, Enetimi IS, Sylvester CI, Oghenegueke V, Perewarebo T. Some selected physico-chemical and heavy metal properties of palm oil mill effluents. Greener Journal of Physical Sciences 2012;2(4),131-137.
  34. Das N, Chandran P. Microbial degradation of petroleum hydrocarbon contaminants: An overview. Biotechnology Research International, 2011,1-13.
  35. Ajijolakewu KA, Sani A, Oyeyiola GP, Ahmed RN, Arekemase MO, Odebisi-Omakanye MB, et al. Cellulase production potentials of the microbial profile of some sugarcane bagasse dumping sites in Ilorin, Nigeria. Notulae Scientia Biologicae, 2013;5(4),445-449.
  36. Eze VC, Owunna ND and Avoaja DA. Microbiological and physicochemical characteristics of soil receiving palm oil mill effluent in Umuahia, Abia State, Nigeria. Journal of Natural Sciences Research, 2013;3(7),163-169.
  37. Pooja P, Hardik P, Saurabh D. Microbioal ecology of hydrocarbon degradation in the soil: A review. Research Journal of Environmental Toxicology, 2016;10(1),1-15.
  38. Kayode-Isola TM, Eniola KIT, Olayemi AB and Igunnugbemi OO. Response of resident bacteria of a crude oil-polluted river to diesel oil. American-Eurasian Journal of Agronomy, 2008;1(1),6-9.
  39. Alade AO, Jameel AT, Muyubi SA, Abdul Karim MI, Alam MDZ. Removal of oil and grease as emerging pollutants of concern (EPC) in wastewater stream. IIUM Engineer Journal, 2011;12(4),161–169.

Author Info

Adegbola Grace Mosunmola1 and Simeon Kayowa Olatunde2*
 
1Department of Food science and Engineering Technology, Ladoke Akintola University of Technology, Nigeria
2Department of Pure and Applied Biology, Ladoke Akintola University of Technology, Nigeria
 

Citation: Mosunmola AG, Olatunde SK (2020) Palm Oil Mill Effluents (POME) and its Pollution Potentials: A biodegradable Prevalence. J PollutEffCont 8:258. doi: 10.35248/2375-4397.20.8.258.

Received: 09-Oct-2020 Accepted: 15-Nov-2020 Published: 22-Nov-2020 , DOI: 10.35248/2375-4397.20.8.258

Copyright: © 2020 Mosunmola AG, et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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