Microbial Degradation Activities Ong Kim Yao (4P3) Poh Yong Rui (4O3) Group 1-121 Background Microbes can degrade HDPE plastic by using the polymer as a carbon source (Arutchelvi et al., 2008) Exposure to UV radiation accelerates chemical degradation of HDPE plastic (Albano et al., 2005) Background Thermal exposure of HDPE plastics to accelerates light-induced degradation (Andrady, 1999) Sierra et al. (2003) suggested that biodegradation of polychlorinated biphenyls (PCBs) occurs faster in soil conditions Objectives • To determine the optimum conditions for maximum biodegradaton of plastics • To study the effects of different environmental conditions on the biodegradation of plastics • To study the effects of varying exposure time to UV irradiation on the biodegradation of plastics Hypothesis The following factors affect the rate of biodegradation of HDPE plastic: Exposure time to UV radiation Environmental conditions for biodegradation Types of microbe culture Types of plastic Variables Constant Variables • Amount of bacterial culture used • Amount of culture medium for bacteria/fungus • Amount of plastic used Independent Variables • Types of bacterial culture • Environmental conditions for biodegradation • Exposure time to UV radiation • Types of plastic Dependent Variables • Change in dry mass of plastic samples • Amount of dissolved O2 gas present in test container • Tensile strength and elongation at break Apparatus Sterile vials Inoculating loop Alcohol burner Incubator Forceps Oven (up to150°C) UV lamp (for 365 nm UV radiation) Electronic balance Autoclave Vernier dissolved O2 probe Datalogger Spatula Thermometer Spectrophotometer Rotary shaker Materials Bacterial cultures (Pseudomonas putida and Sphingomonas macrogoltabidus) Nutrient broth Loamy soil Wire mesh Ethanol Aluminium foil Paper towels HDPE plastic Deionised water Bleach M63 minimal media Cornware Petri dishes Nutrient agar powder Procedure Culture Bacteria Pre-treatment of Plastics Prepare Environmental Conditions Measure Dependent Variables Exposing plastic to Bacteria Set-up •No bacterial culture •Bacterial First set-upculture UV-irradiated HDPE plastic only •Heat-treated plastic which is not UV-irradiated Second set-up HDPE Heat-treated HDPE plastic only •Purpose: irradiation hashave an effect on plastic •Purpose: To To show show that that UV bacterial cultures an effect on degradation plastic degradation Set-up For soil conditions, the best conditions concluded from plastic biodegradation in liquid medium was used, as shown in the above diagram. Microorganism Culture Bacteria was cultured in sterile centrifuge tubes with nutrient broth. The cell density of the bacteria culture was adjusted to approximately 4 × 107 cells/ml. Standard Curve for Bacteria Growth Cell density / 10^8 cell/ml Graph showing Cell Density of P. putida against Optical Density 10.0 8.0 7.966666667 6.0 5.266666667 4.0 2.955 2.0 0.816666667 0.0 0 0 0.2 0.44 0.6 0.4 Optical density/AU 0.8 1 Standard Curve for Bacteria Growth Cell density / 10^8 cell/ml Graph showing Cell Density of S. macrogoltabidus against Optical Density 8.0 6.0 6.1 4.0 6.4 3.6 2.0 1.6 0.0 0 0 0.2 0.40.46 0.6 Optical density/AU 0.8 1 Culturing Bacteria 2ml of bacterial culture prepared earlier was inoculated in a sterile vial with 13.5ml of M63 minimal media and 4.5ml of NB. The control vial contained 15ml of M63 minimal media and 5ml of NB. Preparing Soil Conditions Soil was autoclaved to remove microbes. Sterile vial was filled with 20cm3 of loamy soil. Soil was adjusted to 50% of maximum water capacity. 2ml of bacterial culture was added to the soil each. Pre-treatment of Plastics HDPE Plastic Grocery Bags The entire experiment was repeated with cornware in place of Exposed HDPE plastics Exposed to 365nm to thermal radiation UV in the radiation oven at for 72, 96, 120 hours 115°C for 48 hours Cut up into small pieces Mass recorded weekly Exposing Plastic to Bacteria Plastic samples were placed in vials containing liquid medium or soil. Liquid medium and bacterial culture were changed every week to remove waste material and dead cells. Measure Dependent Variables Analytical Balance Dissolved O2 Probe Used to measure (every 7 days): Change in dry mass of plastic samples Amount of dissolved O2 present Measure Dependent Variables Scaled-up set-ups to measure Tensile strength Elongation at break Focus of set-up effects of different UV irradiation duration on degradation Same methodology as normal set-ups except for the following changes Measure Dependent Variables 80ml of liquid medium (with same ratio of NB and M63 medium). 100ml reagent bottles used. Plastic cut into rectangular shape. Measure Dependent Variables •Purpose of control: To show that different UV irradiation durations have an effect on plastic degradation Mass showed increase then decrease in samples exposed to bacteria, as compared to the Effects of Different Bacterial Exposure comparably constant graph of samples on the Biodegradation ofcontrol HDPE Results and Analysis Mass of plastic/g Plastics 0.04 0.03 Shows that bacterial exposure causes HDPE degradation P. putida 120h UV 0.02 S. macrogoltabidus 120h UV Control 120h UV 0.01 0 1 2 3 4 5 Time/week 6 7 P<0.05 Results and Analysis Greater changes in mass of HDPE samples exposed to UV when Effects of Different Duration of UV compared to samples without exposure Irradiation on the Biodegradation of Mass of plastic/g HDPE Plastics by P. putida 0.04 0.03 0h 72h 96h 120h 0.02 0.01 0 1 2 3 4 5 Time/week 6 7 P<0.05 Results and Analysis Mass of plastic/g Similarly, greater changes in mass of HDPE samples Duration of UV exposed to UV 0.05 Effects of Different Irradiation on the Biodegradation of HDPE Plastics S. irradiation macrogoltabidus Shows thatbyUV increases rate of HDPE degradation 0.04 0.03 0h 72h 96h 120h 0.02 0.01 0 1 2 3 4 5 Time/week 6 7 P<0.05 Change in mass: 96h>120h>72h>0h Results and Analysis Mass of plastic/g Effects of Different Duration of UV Irradiation on the Biodegradation of HDPE Plastics by P. putida 0.04 0.03 0h 72h 96h 120h 0.02 0.01 0 1 2 3 4 5 Time/week 6 7 Mass of plastic/g Change in mass: 72h>120h>96h>0h Results and Analysis 0.05 Effects of Different Duration of UV Irradiation on the Biodegradation of HDPE Plastics macrogoltabidus Shows by thatS.varying UV irradiation changes rate of HDPE degradation 0.04 0.03 0h 72h 96h 120h 0.02 0.01 0 1 2 3 4 5 Time/week 6 7 P<0.05 Results and Analysis T-test: p>0.05 for P. putida Probably due to early stage of degradation HDPE mass starting to fall Change in mass was not significant initially Expecting to see more changes in the following 3-4 weeks of exposure Results and Analysis Mass of HDPE sample exposed to P. putida Bacterial Exposure was lower Mass of plastic/g Effects of Different on the Biodegradation of HDPE Plastics 0.05 Suggests that P. putida is more efficient in degradation 0.04 0.03 P. putida 72h UV 0.02 S. macrogoltabidus 72h UV 0.01 0 1 2 3 4 5 Time/week 6 7 P<0.05 Results and Analysis p>0.05 for other UV exposure times Probably due to early stage of degradation as elaborated earlier Expecting P. putida to be more efficient in degradation Results and Analysis Increase in mass of samples exposed to Bacterial Exposure bacteria Mass of plastic/g Effects of Different on the Biodegradation of HDPE Plastics 0.04 0.03 P. putida 120h UV 0.02 S. macrogoltabidus 120h UV Control 120h UV 0.01 0 1 2 3 4 5 Time/week 6 7 Results and Analysis Increase in mass of samples exposed to Effects of Different Duration of UV bacteria Irradiation on the Biodegradation of Mass of plastic/g HDPE Plastics by S. macrogoltabidus 0.05 Increase is due to biofilm formation 0.04 0.03 0.02 0.01 0 1 2 3 4 5 Time/week 6 7 0h 72h 96h 120h Results and Analysis Biofilm Results and Analysis Formation of biofilm “is a prerequisite for biodegradation” to occur (Arutchelvi et al., 2008) Research showed a rise in density of biofilm attached to HDPE exposed to Pseudomonas sp. , and density remained constant for 30 days (Balasubramanian et al., 2010) Initial increase in mass might be attributed to the formation of biofilm Problems Dissolved oxygen readings not significant Readings fluctuated greatly Probably because oxygen tends to escape and re-dissolve in the medium in order to achieve dynamic equilibrium with the atmosphere Hence unable to reflect the degradation activities of the bacteria Problems Growth of mold in some samples Spores entered since containers cannot be airtight Try to prevent by keeping environment as sterile as possible References Aamer Ali Shah (2007). 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