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Journal articles on the topic 'Non-biodegradable'

Author: Grafiati

Published: 4 June 2021

Last updated: 8 February 2022

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1

Loca, Dagnija, Eduards Sevostjanovs, Marina Makrecka, Olga Zharkova-Malkova, Liga Berzina-Cimdina, Velta Tupureina, and Marina Sokolova. "Microencapsulation of mildronate in biodegradable and non-biodegradable polymers." Journal of Microencapsulation 31, no. 3 (October 14, 2013): 246–53. http://dx.doi.org/10.3109/02652048.2013.834992.

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2

Stejskal, Bohdan. "Determination of proportion of biodegradable and non-biodegradable cemetery waste fraction." Acta Universitatis Agriculturae et Silviculturae Mendelianae Brunensis 58, no. 2 (2010): 181–84. http://dx.doi.org/10.11118/actaun201058020181.

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Municipal waste landfilling is the most common practice of municipal waste disposal in the Czech Republic. As a member state of the EU the Czech Republic must comply with the legislative requirements set for waste management. EU Council Directive 1999/31/EC requires member states to limit the amount of bio-degradable waste into landfill.To achieve the objectives of the Plan of Waste Management of the Czech Republic, various methods has been proposed. Prior to the waste processing, it is necessary to know the waste material composition, and after that select the most appropriate method and procedure for waste utilization or disposal.Therefore an analysis of graveyard waste composition has been carried out, where, by repeated measurements of samples weighing more than 500 kg (the total amount of analyzed waste was 3107 kg), it was found out that the graveyard waste consists of almost 77 % of bio-degradable matter. It is operationally impossible to separate bio-degradable matter from non-bio-degradable materials. Therefore it is desirable to collect compostable cemetery green waste separately from the waste coming from the decoration of gravestones that may be energetically utilized.

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3

Sun, Yuanze, Na Cao, Chongxue Duan, Qian Wang, Changfeng Ding, and Jie Wang. "Selection of antibiotic resistance genes on biodegradable and non-biodegradable microplastics." Journal of Hazardous Materials 409 (May 2021): 124979. http://dx.doi.org/10.1016/j.jhazmat.2020.124979.

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4

Stephen, Pramod. "Non- Biodegradable Things to Protect Environment." Acta Scientific Nutritional Health 3, no. 9 (August 8, 2019): 54. http://dx.doi.org/10.31080/asnh.2019.03.0401.

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5

Rahman, Md Hafizur, and Prakashbhai R. Bhoi. "An overview of non-biodegradable bioplastics." Journal of Cleaner Production 294 (April 2021): 126218. http://dx.doi.org/10.1016/j.jclepro.2021.126218.

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6

Rodrigues, Roberta K., Lucas A. S. Silva, Gabriel G. Vargas, and Bruno V. Loureiro. "Drag Reduction by Wormlike Micelles of a Biodegradable and Non‐Biodegradable Surfactants." Journal of Surfactants and Detergents 23, no. 1 (September 11, 2019): 21–40. http://dx.doi.org/10.1002/jsde.12354.

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7

Kluin, Otto S., Henny C. van der Mei, Henk J. Busscher, and Daniëlle Neut. "Biodegradable vs non-biodegradable antibiotic delivery devices in the treatment of osteomyelitis." Expert Opinion on Drug Delivery 10, no. 3 (January 6, 2013): 341–51. http://dx.doi.org/10.1517/17425247.2013.751371.

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8

Kumar, Akshay, A. R. Kiran, Mahesh Hombalmath, Manoj Mathad, Siddhi S. Rane, Arun Y. Patil, and B. B. Kotturshettar. "Design and analysis of engine mount for biodegradable and non-biodegradable damping materials." Journal of Physics: Conference Series 1706 (December 2020): 012182. http://dx.doi.org/10.1088/1742-6596/1706/1/012182.

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9

Zhao, Shijie, Else Marie Pinholt, Jan Erik Madsen, and Karl Donath. "Histological evaluation of different biodegradable and non-biodegradable membranes implanted subcutaneously in rats." Journal of Cranio-Maxillofacial Surgery 28, no. 2 (April 2000): 116–22. http://dx.doi.org/10.1054/jcms.2000.0127.

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10

Velichanskaya, A. G., D. A. Abrosimov, M. L. Bugrova, A. V. Kazakov, E. V. Pogadaeva, A. M. Radaev, N. V. Blagova, T. I. Vasyagina, and I. L. Ermolin. "Reconstruction of the Rat Sciatic Nerve by Using Biodegradable and Non-Biodegradable Conduits." Sovremennye tehnologii v medicine 12, no. 5 (October 2020): 48. http://dx.doi.org/10.17691/stm2020.12.5.05.

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11

Feng, Jun, Xu-Li Wang, Feng He, and Ren-Xi Zhuo. "Non-Catalyst Synthesis of Functionalized Biodegradable Polycarbonate." Macromolecular Rapid Communications 28, no. 6 (March 16, 2007): 754–58. http://dx.doi.org/10.1002/marc.200600774.

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12

Sekara, Agnieszka, Robert Pokluda, Eugenio Cozzolino, Luisa del Piano, Antonio Cuciniello, and Gianluca Caruso. "Plant growth, yield, and fruit quality of tomato affected by biodegradable and non-degradable mulches." Horticultural Science 46, No. 3 (September 30, 2019): 138–45. http://dx.doi.org/10.17221/218/2017-hortsci.

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Research in southern Italy assessed the effects of biodegradable mulch on fruit yield and quality of two greenhouse tomato cultivars, ‘Coronel F<sub>1</sub>’ and ‘Kero F<sub>1</sub>’. Three mulching types (two MaterBi biodegradable black films, MB N2/12 amnd MB N8; black polyethylene film, low-density polyethylene (LDPE)) and not mulched control were compared. ‘Coronel F<sub>1</sub>’ showed higher values of fruit yield, total crop biomass and leaf area index (LAI). MB N8 and LDPE films led to the highest fruit yield and growth indexes, whereas not mulched control to the lowest. Fruit dry residue and soluble solids were highest under MB N2/12 and MB N8, titratable acidity was highest under MB N8. Fruits grown under MB N8 and LDPE mulches attained the highest levels of colour components “L” and “b” respectively, and MB N8 the highest fruit firmness. MB N2/12 and MB N8 showed the highest levels of antioxidants and antioxidant activity. Biodegradable polymers improved root growth conditions and fruit quality, showing suitable features for sustainable vegetable production.

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13

Maqsood, Muhammad, and Gunnar Seide. "Biodegradable Flame Retardants for Biodegradable Polymer." Biomolecules 10, no. 7 (July 11, 2020): 1038. http://dx.doi.org/10.3390/biom10071038.

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To improve sustainability of polymers and to reduce carbon footprint, polymers from renewable resources are given significant attention due to the developing concern over environmental protection. The renewable materials are progressively used in many technical applications instead of short-term-use products. However, among other applications, the flame retardancy of such polymers needs to be improved for technical applications due to potential fire risk and their involvement in our daily life. To overcome this potential risk, various flame retardants (FRs) compounds based on conventional and non-conventional approaches such as inorganic FRs, nitrogen-based FRs, halogenated FRs and nanofillers were synthesized. However, most of the conventional FRs are non-biodegradable and if disposed in the landfill, microorganisms in the soil or water cannot degrade them. Hence, they remain in the environment for long time and may find their way not only in the food chain but can also easily attach to any airborne particle and can travel distances and may end up in freshwater, food products, ecosystems, or even can be inhaled if they are present in the air. Furthermore, it is not a good choice to use non-biodegradable FRs in biodegradable polymers such as polylactic acid (PLA). Therefore, the goal of this review paper is to promote the use of biodegradable and bio-based compounds for flame retardants used in polymeric materials.

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Aragao-Santiago, Letícia, Hervé Hillaireau, Nadège Grabowski, Simona Mura, Thais L. Nascimento, Sandrine Dufort, Jean-Luc Coll, Nicolas Tsapis, and Elias Fattal. "Compared in vivo toxicity in mice of lung delivered biodegradable and non-biodegradable nanoparticles." Nanotoxicology 10, no. 3 (November 17, 2015): 292–302. http://dx.doi.org/10.3109/17435390.2015.1054908.

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15

HUZAISHAM, NUR ATHIRAH. "APPLICATION OF WASTE BANANA PEELS AS BIODEGRADABLE PLASTIC." Science Proceedings Series 1, no. 2 (April 24, 2019): 128–30. http://dx.doi.org/10.31580/sps.v1i2.786.

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The world today seems unimaginable without plastics or synthetic organic polymer, however their large-scale production and use only dates back to 1950 (1). The resulting rapid growth in plastics production is remarkable, surpassing most other man-made materials. The study presents the utilization of banana peel as biodegradable plastic to substitute the existing non-biodegradable plastic. The objectives of this research are to aims to develop and produce biodegradable plastic that will substitute the existing non-biodegradable plastic to help in saving the environment as well as to compare the properties of biodegradable plastic based on banana peel with the commercial biodegradable plastic. The use of waste banana peel in this study is mainly to replace the synthetic materials used in the conventional biodegradable plastic. Furthermore, the environmental pollutions can be reduced due to the usage of waste banana peels to produce a new value-added biodegradable plastic. Keywords : Banana peel, biodegradable plastic, pollution, environment

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16

Noh, In Sup. "Vascular Tissue Regeneration of the Hybrid ePTFE Graft for Adult Patients." Key Engineering Materials 288-289 (June 2005): 55–58. http://dx.doi.org/10.4028/www.scientific.net/kem.288-289.55.

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Vascular Tissue engineering has drawn high interest due to its high demand in its vascular graft applications. We tissue-engineered a hybrid vascular graft consisting of tissues layers and non-biodegradable ePTFE by in vitro cell culture. Tissue formation was obtained by culturing vascular smooth muscle cells on the biodegradable polylactide scaffolds on the ePTFE surfaces. The fabricated hybrid ePTFE graft consisted of three layers, i.e. two biodegradable polylactide layers and a non-biodegradable ePTFE layer. The biodegradable layer was fabricated to have a porous structure with 30-60 µm pore sizes. Connection of biodegradable layers and ePTFE was obtained by filtering the polylactide solution through the porous ePTFE wall. For a better tissue formation coating of gelatin was performed on the luminal polylactide scaffolds. The generated tissues replaced the biodegradable layers on both inside and outside surfaces of the ePTFE.

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17

Salpavaara, Timo, Aleksi Hänninen, Anni Antniemi, Jukka Lekkala, and Minna Kellomäki. "Non-destructive and wireless monitoring of biodegradable polymers." Sensors and Actuators B: Chemical 251 (November 2017): 1018–25. http://dx.doi.org/10.1016/j.snb.2017.05.116.

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18

Jurado, E., V. Bravo, J. M. Vicaria, A. Fernandez-Arteaga, and A. I. Garcia-Lopez. "Triolein solubilization using highly biodegradable non-ionic surfactants." Colloids and Surfaces A: Physicochemical and Engineering Aspects 326, no. 3 (September 2008): 162–68. http://dx.doi.org/10.1016/j.colsurfa.2008.05.024.

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19

Dwivedi, Poushpi, P. K. Mishra, Manoj Kumar Mondal, and Neha Srivastava. "Non-biodegradable polymeric waste pyrolysis for energy recovery." Heliyon 5, no. 8 (August 2019): e02198. http://dx.doi.org/10.1016/j.heliyon.2019.e02198.

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20

Hernández-Pedraza, Miguel, José Adán Caballero-Vázquez, Jorge Carlos Peniche-Pérez, Ignacio Alejandro Pérez-Legaspi, Diego Armando Casas-Beltran, and Jesús Alvarado-Flores. "Toxicity and Hazards of Biodegradable and Non-Biodegradable Sunscreens to Aquatic Life of Quintana Roo, Mexico." Sustainability 12, no. 8 (April 17, 2020): 3270. http://dx.doi.org/10.3390/su12083270.

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Sunscreens have spread widely into aquatic systems over the last 18 years in Quintana Roo, Mexico. This contamination is caused by intensive use as a result of leisure activities, as sunbathers apply the substances intensively (up to 83.75% of tourists and locals). Moreover, 25% of the compounds are mainly released into the water through topical products washing off. On average, 300,000 tourists arrive every week in Quintana Roo, increasing the contamination. In addition, there are no recent studies on sunscreen toxicity and the hazards this represents for the native zooplankton of Quintana Roo. In order to assess their adverse effects, acute toxicity was assessed for nine sunscreens (five non-biodegradable and four biodegradable) in four zooplankton species (Brachionus cf ibericus, Cypridopsis vidua, Diaphanocypris meridana, and Macrothrix triserialis). In total, 21 LC50 values were obtained, which are the baseline values for estimating risk and for determining the expected maximum permissible concentration. Our data on toxicity to freshwater species compared to marine species indicate that freshwater species are more sensitive than marine species. In conclusion, biodegradable sunscreen posed a moderate risk, and non-biodegradable posed a high risk. Our outcomes suggested that the maximum permissible concentrations for the contamination of sunscreens were 8.00E-05 g/L for non-biodegradable and 1.60E-04 g/L for biodegradable sunscreens.

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21

Oyamada, Shizu, Xiaodong Ma, Tim Wu, Michael P. Robich, Cesario Bianchi, Frank W. Sellke, and Roger J. Laham. "IN VIVO BIOCOMPATIBILITY COMPARISON BETWEEN NOVEL BIODEGRADABLE POLYMER AND EXISTING NON-BIODEGRADABLE POLYMER COATED STENTS." Journal of the American College of Cardiology 55, no. 10 (March 2010): A122.E1140. http://dx.doi.org/10.1016/s0735-1097(10)61141-2.

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22

Reynolds, D?M. "The differentiation of biodegradable and non-biodegradable dissolved organic matter in wastewaters using fluorescence spectroscopy." Journal of Chemical Technology & Biotechnology 77, no. 8 (2002): 965–72. http://dx.doi.org/10.1002/jctb.664.

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23

Pokhrel, Shanta. "A review on introduction and applications of starch and its biodegradable polymers." International Journal of Environment 4, no. 4 (December 11, 2015): 114–25. http://dx.doi.org/10.3126/ije.v4i4.14108.

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Biodegradable polymers play a very important role in plastic engineering by replacing non biodegradable, non renewable petrol based polymers. Starch is a renewable, biodegradable, low cost natural polymer with high availability. Natural polymers can be blended with synthetic polymers to improve their properties significantly. This article reviews advance in starch and starch based blends and presents their numerous potential applications. Therefore, this review helps to understand the importance and characteristics of starch and its biodegradable polymers (blends) by its various aspects such as structural properties and wide applications.International Journal of Environment Vol.4(4) 2015: 114-125

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24

Dinnes, Donna Lee M., J. Paul Santerre, and Rosalind S. Labow. "Influence of biodegradable and non-biodegradable material surfaces on the differentiation of human monocyte-derived macrophages." Differentiation 76, no. 3 (March 2008): 232–44. http://dx.doi.org/10.1111/j.1432-0436.2007.00221.x.

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25

Zellin, Göran, Amel Gritli-linde, and Anders Linde. "Healing of mandibular defects with different biodegradable and non-biodegradable membranes: an experimental study in rats." Biomaterials 16, no. 8 (January 1995): 601–9. http://dx.doi.org/10.1016/0142-9612(95)93857-a.

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26

García-Estrada, Paulina, Miguel A. García-Bon, Edgar J. López-Naranjo, Dulce N. Basaldúa-Pérez, Arturo Santos, and Jose Navarro-Partida. "Polymeric Implants for the Treatment of Intraocular Eye Diseases: Trends in Biodegradable and Non-Biodegradable Materials." Pharmaceutics 13, no. 5 (May 12, 2021): 701. http://dx.doi.org/10.3390/pharmaceutics13050701.

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Intraocular/Intravitreal implants constitute a relatively new method to treat eye diseases successfully due to the possibility of releasing drugs in a controlled and prolonged way. This particularity has made this kind of method preferred over other methods such as intravitreal injections or eye drops. However, there are some risks and complications associated with the use of eye implants, the body response being the most important. Therefore, material selection is a crucial factor to be considered for patient care since implant acceptance is closely related to the physical and chemical properties of the material from which the device is made. In this regard, there are two major categories of materials used in the development of eye implants: non-biodegradables and biodegradables. Although non-biodegradable implants are able to work as drug reservoirs, their surgical requirements make them uncomfortable and invasive for the patient and may put the eyeball at risk. Therefore, it would be expected that the human body responds better when treated with biodegradable implants due to their inherent nature and fewer surgical concerns. Thus, this review provides a summary and discussion of the most common non-biodegradable and biodegradable materials employed for the development of experimental and commercially available ocular delivery implants.

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27

Chen, Rui, Long-Fei Ren, Jiahui Shao, Yiliang He, and Xiaofan Zhang. "Changes in degrading ability, populations and metabolism of microbes in activated sludge in the treatment of phenol wastewater." RSC Advances 7, no. 83 (2017): 52841–51. http://dx.doi.org/10.1039/c7ra09225c.

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28

Lee, Hyang Moo, Young Hyun Kim, Kyung Won Kim, and In Woo Cheong. "Study on Biodegradable Polyurethane Foam for Non-lethal Weapon." Adhesion and Interface 17, no. 1 (March 30, 2016): 21–28. http://dx.doi.org/10.17702/jai.2016.17.1.21.

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29

Slepička, P., Z. Malá, S. Rimpelová, and V. Švorčík. "Antibacterial properties of modified biodegradable PHB non-woven fabric." Materials Science and Engineering: C 65 (August 2016): 364–68. http://dx.doi.org/10.1016/j.msec.2016.04.052.

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30

Yoon, Hyung Ku, Kwang Pyo Jeon, Kyung Hoon Kang, Jin Il Kim, Dong Soo Kim, and Young Kwan Koh. "Biodegradable Internal Fixation For Displaced Non: Comminuted Malleolar Fracture." Journal of the Korean Orthopaedic Association 33, no. 2 (1998): 309. http://dx.doi.org/10.4055/jkoa.1998.33.2.309.

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31

Al Jibouri, Ali Kamel H., Simant R. Upreti, and Jiangning Wu. "Optimal control of continuous ozonation of non-biodegradable pollutants." Journal of Process Control 66 (June 2018): 1–11. http://dx.doi.org/10.1016/j.jprocont.2018.02.009.

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32

Chang, P. H., Y. H. Huang, C. L. Hsueh, M. C. Lu, and G. H. Huang. "Treatment of non-biodegradable wastewater by electro-Fenton method." Water Science and Technology 49, no. 4 (February 1, 2004): 213–18. http://dx.doi.org/10.2166/wst.2004.0266.

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A novel electro-Fenton method, called the Fered-Fenton method, applying H2O2 and electrogenerated ferrous ions for treating organic-containing wastewater was investigated. By combining electrochemical reduction and chemical oxidation, the process can regenerate ferrous ions and remove organic compounds simultaneously in a batch reactor. Because the generation rate of ferrous ions is one of the key parameters in evaluating the oxidation efficiency of the reaction system, the initial current efficiencies (ηi) for iron (III) reduction are examined first. It shows that increasing initial ferric ion concentration can achieve high initial current efficiency. In addition, ηi decreased (ca. 20-100%) with increasing current density of cathode (ca. 40-199 A/m2). For illustration, the wastewater from chemical (i.e. electroless) nickel plating was treated in this investigation owing to its non-biodegradability and high organic concentration. The average pH, COD and Ni concentrations of this wastewater were about 5.0, 30,000 and 2,000 mg/L, respectively. Experimental results indicate that traditional Fenton method only removed 60% of COD when using 5,000 mg/L of ferrous ions. However, the COD removal efficiency was promoted after the electricity was introduced into the system (i.e. Fered-Fenton method). Moreover, Ni concentration was reduced from 2,080 to 0.3 mg/L, indicating that the removal efficiency was higher than 99.9%.

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33

STEINBUCHEL, A. "Non-biodegradable biopolymers from renewable resources: perspectives and impacts." Current Opinion in Biotechnology 16, no. 6 (December 2005): 607–13. http://dx.doi.org/10.1016/j.copbio.2005.10.011.

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34

Matsui, S., Y. Okawa, and R. Ota. "Experience of 16 Years' Operation and Maintenance of the Fukashiba Industrial Wastewater Treatment Plant of the Kashima Petrochemical Complex – II. Biodegradability of 37 Organic Substances and 28 Process Wastewaters." Water Science and Technology 20, no. 10 (October 1, 1988): 201–10. http://dx.doi.org/10.2166/wst.1988.0138.

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Twenty-eight process wastewaters and thirty-seven organic substances identified in the wastewater of the Kashima petrochemical complex were subjected to biodegradability tests. The tests consisted of the activated sludge degradability method and a supplementary test using the respiration meter method. Both tests utilized the activated sludge of the Fukashiba industrial wastewater treatment plant, which was acclimatized to the wastewater and organic substances. The 28 process wastewaters were classified into biodegradable, less biodegradable, and non-biodegradable according to the percentage TOC removal and the BOD5/TOC ratio of the wastewater. The 37 organic substances were also classified into biodegradable, less biodegradable and non-biodegradable according to TOC and CODMn removal. In general, chlorinated compounds, nitro-aromatics and polymerized compounds were difficult to biodegrade. From the biodegradability tests of the factory wastewaters, it was found that the refractory CODMn loads of these factories contributed to the load remaining in the effluent of the wastewater treatment plant. Various improvements were made to reduce the discharge of refractory substances from the factories.

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35

Dai, Xiaohu, Ying Xu, Yiqing Lu, and Bin Dong. "Recognition of the key chemical constituents of sewage sludge for biogas production." RSC Advances 7, no. 4 (2017): 2033–37. http://dx.doi.org/10.1039/c6ra26180a.

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The easy biodegradable organic matter, non-biodegradable organic matter, metal ions, and micron-sized silica particle and their interactions were the key factors for limiting the biogas production from anaerobic sludge digestion.

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36

Myszograj, Sylwia, Ewelina Płuciennik-Koropczuk, and Anita Jakubaszek. "Cod Fractions - Methods of Measurement and Use in Wastewater Treatment Technology." Civil And Environmental Engineering Reports 24, no. 1 (March 28, 2017): 195–206. http://dx.doi.org/10.1515/ceer-2017-0014.

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Abstract The paper presents the results of studies concerning the designation of COD fraction in raw wastewater. The research was conducted in four municipal mechanical-biological sewage treatment plants and one industrial sewage treatment plant. The following fractions of COD were determined: non-biodegradable (inert) soluble SI, biodegradable soluble fraction SS, particulate slowly degradable XS and particulate non-biodegradable XI. The methodology for determining the COD fraction was based on the ATV-A131 guidelines and Łomotowski-Szpindor methodology. The real concentration of fractions in raw wastewater and the percentage of each fraction in total COD are different from data reported in the literature.

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Płuciennik-Koropczuk, Ewelina, Anita Jakubaszek, Sylwia Myszograj, and Sylwia Uszakiewicz. "Cod Fractions In Mechanical-Biological Wastewater Treatment Plant." Civil And Environmental Engineering Reports 24, no. 1 (March 28, 2017): 207–17. http://dx.doi.org/10.1515/ceer-2017-0015.

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Abstract The paper presents results of studies concerning the designation of COD fraction in the raw, mechanically treated and biologically treated wastewater. The test object was a wastewater treatment plant with the output of over 20,000 PE. The results were compared with data received in the ASM models. During investigation following fractions of COD were determined: dissolved non-biodegradable SI, dissolved easily biodegradable SS, in organic suspension slowly degradable XS and in organic suspension non-biodegradable XI. Methodology for determining the COD fraction was based on the guidelines ATV-A 131. The real percentage of each fraction in total COD in raw wastewater are different from data received in ASM models.

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38

Pandharipande, Ms Jui. "Micro- Level Audit of Segregation, Collection, Transportation, Treatment and Disposal of Municipal Solid Waste at Source of Dhantoli, Nagpur." International Journal for Research in Applied Science and Engineering Technology 9, no. VII (July 15, 2021): 1319–25. http://dx.doi.org/10.22214/ijraset.2021.36606.

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: A micro-level audit of the Municipal Solid Waste Management system was carried out for centrally situated Dhantoli locality of Nagpur, Maharashtra. Dhantoli being a very elite locality of Nagpur was facing problems due to increasing municipal solid waste. Waste quantification was carried out to find the total amount of waste generated per day from the locality and the percentage of biodegradable and non-biodegradable waste was also determined. The waste sample was analyzed for its characteristics and its results indicated that organic waste was highest among other components of the waste. The outcomes of the audit also highlighted the lacunae in the collection and transportation system of the locality. Considering all the parameters, a decentralized composting plant was suggested for the treatment and disposal of biodegradable waste; while for the non-biodegradable waste establishment of a Material Recovery Facility (MRF) center was proposed.

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39

Agarwal, Radhika, and Ar Anant Prakash. "Reuse & Recycle of Non-Biodegradable Waste As Construction Materials." International Journal of Engineering Research 7, special3 (2018): 235. http://dx.doi.org/10.5958/2319-6890.2018.00066.1.

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40

Li, Tianxin, Shuiyang Xu, Yongcun Zou, Xiaohua Chen, and Harrison Odion Ikhumhen. "Modified mesoporous clinoptilolite characterization for non-biodegradable organic material removal." Emerging Materials Research 6, no. 2 (November 2017): 314–21. http://dx.doi.org/10.1680/jemmr.16.00023.

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41

Finn, Aloke V., and Renu Virmani. "Biodegradable polymer drug-eluting stents: non-inferiority waiting for superiority?" Lancet 388, no. 10060 (November 2016): 2567–68. http://dx.doi.org/10.1016/s0140-6736(16)32063-3.

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42

Kostina, Nina Yu, Ognen Pop-Georgievski, Michael Bachmann, Neda Neykova, Michael Bruns, Jiří Michálek, Martin Bastmeyer, and Cesar Rodriguez-Emmenegger. "Non-Fouling Biodegradable Poly(ϵ-caprolactone) Nanofibers for Tissue Engineering." Macromolecular Bioscience 16, no. 1 (October 7, 2015): 83–94. http://dx.doi.org/10.1002/mabi.201500252.

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43

Lu, Xiao, Yingjun Wang, and Fangchun Jin. "Influence of a non-biodegradable porous structure on bone repair." RSC Advances 6, no. 84 (2016): 80522–28. http://dx.doi.org/10.1039/c6ra17747f.

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Schröder, H. Fr. "Surfactants: non-biodegradable, significant pollutants in sewage treatment plant effluents." Journal of Chromatography A 647, no. 2 (September 1993): 219–34. http://dx.doi.org/10.1016/0021-9673(93)83404-g.

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Chen, Tze-Haw H., Younsoo Bae, Darin Y. Furgeson, and Glen S. Kwon. "Biodegradable hybrid recombinant block copolymers for non-viral gene transfection." International Journal of Pharmaceutics 427, no. 1 (May 2012): 105–12. http://dx.doi.org/10.1016/j.ijpharm.2011.09.035.

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Huang, Fu-Wei, Hui-Yuan Wang, Cao Li, Hua-Fen Wang, Yun-Xia Sun, Jun Feng, Xian-Zheng Zhang, and Ren-Xi Zhuo. "PEGylated PEI-based biodegradable polymers as non-viral gene vectors." Acta Biomaterialia 6, no. 11 (November 2010): 4285–95. http://dx.doi.org/10.1016/j.actbio.2010.06.016.

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Basha, C. Ahmed, E. Chithra, and N. K. Sripriyalakshmi. "Electro-degradation and biological oxidation of non-biodegradable organic contaminants." Chemical Engineering Journal 149, no. 1-3 (July 1, 2009): 25–34. http://dx.doi.org/10.1016/j.cej.2008.09.037.

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Choi, Jeong-Hwan, Jong-Gook Kim, Hye-Bin Kim, Dong-Hun Shin, and Kitae Baek. "Dual radicals-enhanced wet chemical oxidation of non-biodegradable chemicals." Journal of Hazardous Materials 401 (January 2021): 123746. http://dx.doi.org/10.1016/j.jhazmat.2020.123746.

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Luten, Jordy, Cornelus F. van Nostrum, Stefaan C. De Smedt, and Wim E. Hennink. "Biodegradable polymers as non-viral carriers for plasmid DNA delivery." Journal of Controlled Release 126, no. 2 (March 2008): 97–110. http://dx.doi.org/10.1016/j.jconrel.2007.10.028.

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Abidin, A. Z., E. V. Yemensia, K. W. Wijaya, and A. P. Rahardjo. "Circular Economy on Non-Biodegradable Waste Management with MASARO Technology." IOP Conference Series: Materials Science and Engineering 1143, no. 1 (April 1, 2021): 012052. http://dx.doi.org/10.1088/1757-899x/1143/1/012052.

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