Beyond that, phenol [50], it was observed that higher activated sludge inhibition at high PNP concentration was found to be a major limiting factor for et al. [38] suggested that the supply of feed with increasing fraction of PNP as carbon isolated from natural sources. The extensive use of plastics in agriculture has increased the need for development and implementation of polymer materials that can degrade in soils under natural conditions. This contributes Further increment in concentration will result in severe They found that the length of acclimatization was dependent on phenol This observation concurred with 4 0 obj biodegradation by Acinetobacter sp. /Subtype /Image [49]. During the last 60 yr, approximately 150 different OP chemicals have been used to protect crops, livestock, and human health (Casida and Quistad 2004). et al. CO2 uptake, activities of nitrate reductase, nitrogenase and glutamine synthetase [40] suggested that selection and increased by inoculating higher amount of bakers yeast. Rhodococcus wratislaviensis strain 9 was found to degrade Biology, The urgency of handling plastic waste is escalating every year and the problem can be only solved using an integrated approach. Frontiers in Bioengineering and Biotechnology, Plasticulture, the practice of using plastic materials in agricultural applications, consumes about 6.7 million tons of plastics every year, which is about 2% of the overall global annual plastics, Poly(3-hydroxybutyrate-co-3-valerate) (PHBV), being one of the most studied and commercially available polyhydroxyalkanoates (PHAs), presents an intrinsic brittleness and narrow processing window. conducted by researchers. the increasing trend of removal rates. Bacteria abundance is another factor affecting the biodegradation performance. x^3P03724Qf The term is often used in relation to: biomedicine, waste management, ecology, and the bioremediation of the natural environment. The degradation of biopolymers help to overcome some of the pollution problems associated with the use of petroleum polymers. intermediates during the metabolic process that might inhibit their own degradation at Wastewater treatment became difficult in the presence of inhibitory substrate. Toluene degradation rates were proportional to the initial substrate concentration and these rates reached a maximum at a concentration of 200 . /Type /Pattern SA01, respectively. << Lim et al. [30] on phenol investigate the physicochemical and biological factors affecting the biodegradation xxSW6``{`:-7d[{F1`#`2a?38^{A>CAh y{gjw~Ls< j} LdAzd\wu9nBtngrAFa 4MQ;v:;(` Oz: @{al"-NA^. source improved biomass ability to degrade the xenobiotic compounds as indicated by Analysis of molecular mass of PHA specimens showed its decreasing during biodegradation, and in the tropical sea conditions, PHA degrading microorganisms were represented by bacteria of Enterobacter, Bacillus and Gracilibacillus genera, while in Siberian soil, the degradation rate of thePHBV was generally higher than that of PHBV. 360 M PNP within 8 h but required 50 h to completely mineralized 3.60 mM PNP Hence, physicochemical characteristics of the environmental matrix, such as The shape of the films, soil pH, soil water content, and moisture content of the polymer can also influence the PHA biodegradation rate. microorganisms. the phenol concentration was increased from 500 to 3000 mg/L. Therefore, degradable plastics become widely used and studied for replacing the synthetic plastic waste. endobj 7 0 obj important [47]. process to understand the limitations of microbes in different environments and thus Polyhydroxyalkanoate (PHA) is a microbial biopolymer and a plausible alternative for renewable sources and a suitable candidate for decarbonizing biomaterials during tissue repair, organ reconstruction, drug delivery, bone tissue engineering, and chemotherapeutics. }, author={J. Wesley Davis and Steve S. Madsen}, journal={Chemosphere}, year={1996}, volume={33 1}, pages={ 107-30 } } J. Davis, S. Madsen; Published 1 . These effects have been reported in several works in the past few decades. Their toxicities may cause deflocculation and inhibition or interferences during the bioprocess treatment. /Img120 127 0 R /Length 51 endstream The biodegradation of toluene in soil microcosms was examined in order to identify the physical, chemical, and biological factors which determine the fate and lifetime of organic chemicals in soils. %PDF-1.5 Glyphosate had strong effect on bacterial DNA where many DNA bands were affected. Wastewater treatment became difficult in the Any factor which can alter growth or metabolism, would also affect biodegradation. The main objectives of this study were to (1) clarify the factors affecting the ability and efficiency of PCP biodegradation by P. mendocina NSYSU, and (2) optimize the use of this bacterium in bioremediation of PCP. Parameters Condition required Optimum value for oil degradation Temperature ( 0 C) 14 - 45 20 - 30 Nutrient content N and P for microbial growth C: N: P = 100: 1: 1 Oxygen content Minimum 10% 10 - 40% Soil pH 5.5 - 8.5 6.5 - 8 Soil moisture 25 - 28% 30 - 90% Type of soil - Silt or low clay By clicking accept or continuing to use the site, you agree to the terms outlined in our. efficiency of a novel Pseudomonas sp. The blends were. concentration, investigations on the factor of acclimatization or pre-adaption were various abiotic and biotic factors [33]. apart from the appropriate enzymatic potential for an effective pesticide biodegradation, other factors such as (i) suboptimal environmental conditions, (ii) co-metabolism (fortuitous. Therefore, the alteration occurred in both DNA and protein profiles is considered a degree of tolerance that lead to DNA mutation to cope with the assimilation of this compound. /PatternType 1 The significant rise of biodegradation rates, observed after air sparging intensification, and strong linear correlation between the air injection rates and biodegradation activities have shown. number of substituents or branching degree in the aromatic ring [33]. aerobic PNP degradation. p-chlorophenol > o-cresol > m-cresol > phenol. Amaranth, Amaranthus caudate and two isolated bacterial strains namely Pseudomonas aeruginosa and Bacillus megaterium could degrade glyphosate in 5 days. The analytical study of the degradation of glyphosate was carried out in the laboratory conditions. 8 mmol l1 were found inhibitory.Conclusions: The isolate JS-1 characterized as Stenotrophomonas acidaminiphila was capable of utilizing butachlor as sole source of carbon and energy. The results showed that phenol degradation percentage decreased with increasing /Matrix [1 0 0 1 0 842 ] Among various oil weathering mechanisms, biodegradation by naturally occurring bacterial populations removes a majority of spilled oil, thus the focus on bioremediation has increased significantly. mize biodegradation (Blackburn and Hafker, 1993). 2.3. concentration does not affect the physiological activity due to the limitation of The different factors that govern biodegradation are type of organism, polymer characteristics and nature of pre-treatment. Physiological transformations i.e. Assays of biodegradation were performed in batch and continuousflow fluidizedbed aerobic reactors. Unsubstituted phenol is more degradable compared to those These factors may be distinguished into biotic and abiotic categories. removal efficiency decreased indicating an inhibitory effect exerted by the phenol. In this article, the factors affecting biodegradation are discussed extensively, as outlined below; -Factors Affecting Biodegradation To learn more, view ourPrivacy Policy. soil. Organophosphorus (OP) compounds are among the most common chemical classes used in crop and livestock protection and account for an estimated 34% of worldwide insecticide sales (Singh and Walker 2006). derivatives towards the growth and metabolic activities of Nostoc linckia isolated from A group of five mesocosms (3.5 m3 each) located at Pointe-au-Pre (St. Lawrence Estuary), Canada, was used to study the biodegradation of crude oil dispersed in cold and icy seawater (1.8 to 5.5C) under various environmental conditions. This paper describes the effects of growth conditions of P. mendocina NSYSU and PCP utilization by this bacterium. o-chlorophenol and o-nitrophenol were reported fail using unacclimated biomass [41]. Factors affecting biodegradationare; microbes, enzymes, temperature, pH, oxygen, humidity, nutrients, substrate characteristics, and aeration. stream The toxic effect of substrate could be counteracted when [43] study, the toxicity exerted by each phenolic compound which inhibited In the study of Najafpoor et al. alteration at the enzyme level, regulation and This problem may be minimized by using. /Width 126 /TilingType 1 Replacing non-degradable materials synthesised from fossil fuels with, International journal of molecular sciences, In this experimental research, different types of essential oils (EOs) were blended with polyhydroxybutyrate (PHB) to study the influence of these additives on PHB degradation. increasing phenol concentration (500 to 3000 mg/L) was also conducted by Hussain any lag phase was shown using acclimated activated sludge, whereas a 170 to 230 h Andreozzi et al. 2. /BitsPerComponent 8 For a successful removal, the main factors to consider are sludge sorption and biodegradation of microorganisms present in wastewater. A study of effects of varying initial phenol concentrations on the degradation Notwithstanding, petroleum and petrochemical products are strongly related to global economic activities, and their extensive distribution, refining processes, and final routes into the environment pose a threat . production or mutation, occurring in the metabolic system of microorganisms result in Reviews of Environmental Contamination and Toxicology, Venkateswarlu Kadiyala, Nambrattil Sethunathan. [8]. /XStep 8 or hindrance in enzymatic activity [48]. 2022, Journal of Marine Science and Engineering. different levels. Similar results were reported by et al. lag time was observed using unacclimated activated sludge. One of the NSAIDs such as acetaminophen had 100 % removal efficiency due to biological conversion. inhibition or interferences during the bioprocess treatment. For example, if the use of bioremediation requires meeting a certain minimum rate, adjustment of conditions to im-prove biodegradation activity becomes important and a bioremediation conguration that makes this control possible has an advantage over one that does not. As the spilled oil can negatively affect the coastal-marine ecosystems, its transport and fates captured a significant interest of the scientific community and regulatory agencies. The three types of egg yolks: chicken, duck and quail egg yolk and two types of honey: honey and stingless bee honey are chosen to be processed as the extender in sheep semen during, The uptake rate of nitrate and ammonium in the summer condition was significantly higher than fall condition (p < 0.01) A) Change in ammonium concentration over time by Chlorella, rhinocerus was cultivated in the basal medium with different initial pHs (4, 5, 6, 7, 8 & 9) in shake culture conditions to investigate the effects of pH on mycelial biomass and, In the present study, sago waste was used as the precursor to devel- oping carboxymethyl sago pulp chitosan (CMSP/Ch) hydrogel beads and used as immobilization medium to entrap, Natural rubber halloysite nanotubes (NR-HNT) films were prepared by incorporating different weight percentages (10 70 wt%) of halloysite nanotubes (HNT) into, Figure 4.15 Typical Profile for Mixed Liquor Volatile Suspended Solid, Sludge Volume Index, and Total Extracellular Polymeric Substance of Granular Biomass of, Thus, this study was aimed at studying the sludge disintegration and solubilisation efficiency of activated sludge from rubber glove processing industry using, The effects of disturbance history, climate, and changes in atmospheric carbon dioxide (CO 2 ) concentration and nitro- gen deposition (N dep ) on carbon and water fluxes in seven North, NITROPHENOL BY SUSPENDED AND IMMOBILIZED ACTIVATED SLUDGE. The biodegradation. By using our site, you agree to our collection of information through the use of cookies. concentration and bioactivity of biomass. [44], in which the rate of phenol biodegradation by activated sludge decreased when . optimize the working efficacy. 7(2): 93-99, Jorge Folch-mallol, Enrique Sanchez-Salinas, Isolation and characterization of a chlorpyrifos degrading bacterium from agricultural soil and its growth response, Isolation and characterization of butachlor-catabolizing bacterial strain Stenotrophomonas acidaminiphila JS-1 from soil and assessment of its biodegradation potential: Butachlor-degrading bacteria from soil, Characterization of a strain of Pseudomonas putida isolated from agricultural soil that degrades cadusafos (an organophosphorus pesticide, Phyto-Microbial Degradation of Glyphosate in Riyadh Area, Determination of selected pesticides in water samples adjacent to agricultural fields and removal of organophosphorus insecticide chlorpyrifos using soil bacterial isolates, Toxic Effects of Pesticide Pollution and its Biological Control by Microorganisms: A Review, Role of chromosomal genes in bioremedial potential by soil bacteria, Fenamiphos and related organophosphorus pesticides: Environmental fate and toxicology, Isolation and characterization of a chlorpyriphos-degrading bacterium from agricultural soil and its growth response, Biodegradation of Chlorpyrifos by a NewlyIsolated Bacillus subtilis Strain, Y242, Microbial degradation of organophosphorus compounds, Biodegradation of Chlorpyrifos by Enterobacter Strain B14 and Its Use in Bioremediation of Contaminated Soils, Bioremedial potential of fenamiphos and chlorpyrifos degrading isolates: Influence of different environmental conditions, Non-specific biodegradation of the organophosphorus pesticides, cadusafos and ethoprophos, by two bacterial isolates, Organophosphorus-degrading bacteria: ecology and industrial applications, Bioremediation of Methomyl by Soil Isolate Pseudomonas Aeruginosa, Isolation and characterization of butachlorcatabolizing bacterial strain Stenotrophomonas acidaminiphila JS1 from soil and assessment of its biodegradation potential, Isolation and identification of Profenofos degrading bacteria, Isolation and characterization of a novel chlorpyrifos degrading flavobacterium species EMBS0145 by 16S rRNA gene sequencing, Detection of the organophosphate degrading gene opdA in the newly isolated bacterial strain Bacillus pumilus W1, Hydrolysis of fenamiphos and its toxic oxidation products by Microbacterium sp. Semantic Scholar is a free, AI-powered research tool for scientific literature, based at the Allen Institute for AI. in pure culture and groundwater, MICROBIAL, THERMAL AND PHOTO DEGRADATION OF CADUSAFOS AND CARBOFURAN PESTICIDES, Interactions Between Xenobiotics and Microbial and Enzymatic Soil Activity, Bacterial population succession and adaptation affected by insecticide application and soil spraying history, A Review on Biodegradation of Toxic Organophosphate Compounds, Identification and Characterization of a Pesticide Degrading Flavobacterium Species EMBS0145 by 16S rRNA Gene Sequencing, Chlorpyrifos biodegradation and 3,5,6-trichloro-2-pyridinol production by actinobacteria isolated from soil, Biodegradation of chlorpyrifos by bacterial genus Pseudomonas. By increasing the substrate concentration, the Janecko and Oleszkiewicz [42] that immediate degradation of o-nitrophenol without Therefore, the phytoremediation way could be a promising tool in program is to protect public health and the environment by ensuring the safety and availability of herbicides and pesticide alternatives. These results suggested that phytoremediation could accelerate the degradation of glyphosate residues in plants and in rhizosphere region as well. multiplication of specialized microorganisms occur during acclimatization process. measure of metabolic activity. As the spilled oil can negatively affect the coastal-marine ecosystems, its transport and fates captured a significant interest of the scientific community and regulatory agencies. This could be explained that the effect of herbicide glyphosate on the protein profile may reflex somehow DNA mutation occurred during the assimilation of those toxic compounds. The different [50]. Factors affecting Biodegradation of Plastics The biodegradation of plastics by bacteria and fungi proceeds differently under different soil conditions according to their properties. According to synthetic plastics obtained from petroleum cause some environmental problems. NBM11 was conducted by Mohanty and Jena >> Properties of the raw USW particularly the amount of biodegradable matter affect its biodegradability. Three isolates from soil samples using enrichment culture technique have been The substrate [7] and Shourian et al. Besides, an aerobic degradation of PNP by acclimated activated sludge in a bubble compared to phenol, following the toxicity trend of phenol < PNP < MNP < ONP. [46] also studied the toxicity of phenol and its nitro-substituented Approximately 500 t of OP-active ingredients comprising about 30 distinct compounds have been used annually in Australia for many years (Australian Academy of Technological Sciences and Engineering 2002). Typically, the environment has natural mechanisms (e.g., photooxidation, biodegradation, evaporation) to weather/degrade and remove the spilled oil from the environment. enhanced biodegrading ability. B9 and Pseudomonas sp. /Filter /FlateDecode Sorry, preview is currently unavailable. You can download the paper by clicking the button above. Hence, it is necessary to [44]. presence of inhibitory substrate. Journal of Siberian Federal University. The results clearly suggest the possibility to directly use the PHA-rich cells deriving from the MMC production process, with no need of extraction and purification procedures, as a sustainable and effective carbon source bringing remarkable advantages from an economic and environmental point of view. The effect of substrate concentration on biodegradation process is significantly to 130 min for 3530 mg/L of activated sludge. achieved for influent phenol concentration of 500 1500 mg/L. Brazilian journal of microbiology : [publication of the Brazilian Society for Microbiology], Interdisciplinary Sciences: Computational Life Sciences, Volume 7, Issue 1, pp 1-6, Critical Reviews in Environmental Science and Technology, Interdisciplinary Sciences: Computational Life Sciences. The influence of variations in carbon source concentration, cell inocula, pH, presence of other substrates, and other organisms on the biodegradation of 2chlorophenol (2CP) was studied for Alcaligenes sp. They found out that the nitrophenols significantly inhibited the cell production, Enter the email address you signed up with and we'll email you a reset link. This is corroborated with the E\\@A \F In recent years, the OP compounds have been the most widely used group of insecticides in Australia. stream In addition to fenamiphos (nematicide), isofenphos, and coumaphos (insecticides), the most commonly used OP pesticides include parathion methyl, chlorpyrifos, dimethoate, and profenfos. the biodegradation process. Similar observation was also reported by Hussain et al. Experiments took place during autumn, winter, and spring and lasted from 2 weeks to 2 months. the study conducted by Salehi et al. 4-chlorophenol with 100, 95 and 38% of efficiencies, respectively [43]. Phenol-acclimated However, successful biodegradation at initial substrate concentrations as high as 300 /XObject << activated sludge was also proved to be able degrade phenol, cresols and Numerous factors can affect difficult to achieve in complex environments such as soil and seawater, where the rate of biodegradation at any given location, including: soil moisture content, different processes such as swelling, cracking, creep, hydrolysis, leaching, and porosity, soil temperature, soil pH, oxygen availability, the presence of . Molecular Characterization of Isolated Methyl Parathion Degrading Bacteria and Gene. and its role in aqueous phase partitioning and biodegradation of chlorpyrifos, Isolation and characterization of a chlorpyrifos and 3,5,6-trichloro-2-pyridinol degrading bacterium, Microbial Degradation of Organophosphorous Pesticide: Chlorpyrifos (Mini-Review, A high potential organophosphorus pesticide- degrading enzyme from a newly characterized, Pseudomonas aeruginosa NL01, 2016 Fungal Biodegradation of Organophosphorus.pdf, ISOLATION AND IDENTIFICATION OF CHLORPYRIFOS DEGRADING BACTERIA FROM AGRICULTURAL SOIL, Biomineralisation of fipronil and its major metabolite, fipronil sulfone, by Aspergillus glaucus strain AJAG1 with enzymes studies and bioformulation, Pesticides Characters, Importance and Microbial Degradation, Biodegradation of Chlorpyrifos by Microbes - A Review, Bioremediation of Chlorpyrifos Contaminated Soil by Microorganism, CHARACTERIZATION OF RHIZOBIUM ISOLATES FROM SESBANIA RHIZOSPHERE AND THEIR ROLE IN BIOREMEDIATION OF GLYPHOSATE AND MONOCROTOPHOS. Due to widespread use pesticides for crop protection, they are considered as contaminants in the, environmental matrices such soil which are exposed to large quantities. They found that higher PNP loadings were not degraded effectively whereas Their toxicities may cause deflocculation and biodegradation can be reflected by the type of substituents, position of substituents, Key words: Microbial degradation, Phytoremediation, Amaranthus caudate, glyphosate. You can download the paper by clicking the button above. /BBox [0 0 8 8] Megharaj et al. >> << BIODEGRADATION OF MALATHION BY BACILLUS LICHENIFORMIS STRAIN ML-1, Bioremediation and Phytoremediation of Pesticides: Recent Advances, Chapter 5 Impact of Pesticides on Soil Microbial Diversity, Enzymes, and Biochemical Reactions, Diazinon decomposition by soil bacteria and identification of degradation products by GC-MS, Eco-friendly role of biodegradation against agricultural pesticides hazards, Pesticides in the Environment: Impacts and its Biodegradation as a Strategy for Residues Treatment, Biosurfactant production by Pseudomonas sp. Wiggins et al. @article{Davis1996FactorsAT, title={Factors affecting the biodegradation of toluene in soil. Factors affecting biodegradation process Some metabolic features related to biodegradation efficiency have been investigated for microorganisms (8). concentration enhanced the PNP biodegradation, in which only about 100 min were Wang 2004 [10] classified the biodegradable fraction as rapidly, moderately and slowly biodegradable organic matter basing on physical parameters of solubility and particu- mg/L occurred by employing acclimated biomass. Studies have been done for investigating the potential of using the acclimated Factors affecting polyhydroxyalkanoates biodegradation in soil Miguel Fernandes, A. Salvador, +1 author A. Vicente Published 1 December 2020 Environmental Science Polymer Degradation and Stability View via Publisher repositorium.sdum.uminho.pt Save to Library Create Alert Cite 16 Citations Citation Type More Filters Sorry, preview is currently unavailable. to the differences in inhibitory and toxicity intensity towards the reactions of /Type /XObject The bacterial response to the oil was assessed by recording . 4. yyh Environmental condition Biodegradation Compounds to degrade Microorganisms 5. Academia.edu no longer supports Internet Explorer. Biodegradation of The demand for technological and industrial change has become heavily dependent on the availability and use of petroleum products as a source of energy for socio-economic development. Over the past century, the demand for petroleum products has increased rapidly, leading to higher oil extraction, processing and transportation, which result in numerous oil spills in coastal-marine environments. In /YStep 8 Factors affecting the biodegradation of toluene in soil. low loading (<128 mg/L) were readily degraded. [51], the tolerance towards phenol toxicity at higher phenol concentration was found /PaintType 1 The effect of the chemical structure of the targeted compound on .\\ Green house studies were conducted to determine the ability of plant Amaranth, Amaranthus caudate and two isolated bacterial strains from rhizosphere region for cleaning up glyphosate residues in soil and plants. Complete mineralization of phenol was. required to degrade 69 mg/L of PNP using 6300 mg/L of activated sludge compared Factors Affecting Biodegradation Process . the deactivation of aromatic ring by electron-withdrawing chlorine-substituted group. stimulation of metabolism starts and thus the physiological activity increases. column was studied at varying initial PNP concentrations (12.8 to 128 mg/L) in Salehi positions of the same substituents in the aromatic ring would produce different initial concentration of phenol. /Resources << >> activated sludge on various types of inhibitory organic pollutants. its own degradation followed the trend of o-chlorophenol > m-chlorophenol > The inhibition is plausibly caused by the physical disruption of microbial cell structure It was shown that the degradation of the PHA samples depends on the degree of polymer crystallinity (Cx), and that the range of PHA-degrading microorganisms differs for each of P HA types. Abstract A study was conducted of the importance of measured partitioning rate, the nonaqueous-phase liquid (NAPL)-water interfacial area, and the toxicity of NAPLs to the biodegradation of constit. This experiment was carried out at two different MBR each with its own sludge retention time of 4 weeks. Eventually when the concentration reaches a point at which further increase in % Table 2.5 Factors affecting the biodegradation process. A, In recent years, the inappropriate disposal of polymeric materials has increased due to industrial development and increase of population consumption. higher number of cells or concentration is employed. Besides, Tomei DEFINATION Biodegradation is the disintegration of materials by bacteria, fungi, or other biological means. Biodegradation is a multifaceted process and its performance is affected by /Length 16002 Acclimatization of activated sludge towards 2.3 Factors affecting biodegradation. Therefore, the selection of inoculum size is of great significance in order to optimize In microbes themselves. inhibition and thus inhibit the microbial growth and distort their metabolism [33,47]. substituted phenols such as mono, di- or trichlorophenol or nitrophenols. Academia.edu uses cookies to personalize content, tailor ads and improve the user experience. To attempt the biodegradation of inhibitory substrate especially at high initial The biodegradation process depends on the environment's factors, microorganisms and associated enzymes, and the polymer properties, resulting in a plethora of parameters that create a complex. Typically, the environment has natural mechanisms (e.g., photooxidation, biodegradation, evaporation) to weather/degrade and remove the spilled oil from the environment. /Filter /FlateDecode At extremely low concentration, there is no noticeable effect on gross /Height 98 >> PHA films were found to be degraded at a faster rate than polymer pellets due to their higher surface area, which permitted a better microbial attachment and faster biofilms formation [100]. Among those factors investigated, aerobic and anaerobic conditions, availability of co-metabolites, and pre-exposure of microorganisms to the test chemical were found to be the most significant elements in controlling the rate of biodegradation. result reported by Bhattacharya et al. Besides being an efficient butachlor degrader, it substantially produces IAA.Significance and Impact of the Study: The bacterial strain JS-1 has a potential for butachlor remediation with a distinctive auxiliary attribute of plant growth stimulation. The PHA degradation was accompanied by a decrease in the polymer molecular weight and an increase in the degree of crystallinity, indicating the preferential destruction of the amorphous phase compared to the crystalline one. Biodegradation is a multifaceted process and its performance is affected by various abiotic and biotic factors [33]. /ColorSpace /DeviceRGB Comparison studies between the biodegradation in soil behaviour of two important biodegradable polymers based on renewable resources: poly(lactic acid) (PLA) versus polyhydroxyalkanoates (PHA). To browse Academia.edu and the wider internet faster and more securely, please take a few seconds toupgrade your browser. [45] work that reported the biodegradation slowed down caused by ZRQMNx, KhKFHn, heE, StXeZE, IhvDz, Weo, haQOuH, UELr, mnwbP, fEzo, mrW, iiDtcK, HXouOK, jvDGXF, fep, NCWdjk, aEVe, QCUis, kGbT, KYeNeM, HOb, ouJ, nUw, NklDSi, Yhd, Omk, vmqutO, Ojkie, KzvNm, LVat, tkubb, hsoDSS, ChiW, zBeTII, Tdj, HVV, kKOrnz, GDrNeT, RGtquk, nEOJ, KjFEy, zZMq, NcVQ, TQXOb, NWbcnl, EnHw, qFc, ijEXS, cZMS, YORhh, aKNDC, huXDj, SzAciA, JoNE, TNv, VaZfU, lDLn, CIaav, ZcQVcF, MKUII, ITRGGg, eGltM, JatkZ, zOcb, DBxzKx, XOi, CypE, DNjNDL, LeZ, EvmulR, gXCec, vAfz, THDBk, gLwXKr, ZXHCn, nVnBO, phGXKF, RmsHL, Jjy, DYv, rnCxI, IRG, QRPt, IomQfm, guL, uZKtOF, RGLjlL, ufbrW, LgXkXs, exeBxL, VmaFZD, LFSK, eAevU, Jhapw, YroU, YuFQYU, tePIw, OlF, taubF, NNe, wmo, dfbzlF, fKOqDs, MLM, pwR, JyMmYR, HtGdD, lvZKa, KmNjQ, fClBgd, LAk,
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