ABOUT NEW GREEN MATERIALS

Một phần của tài liệu Green chemistry and engineering a practical design approach (Trang 624 - 628)

These emerging materials represent distinct opportunities for more sustainable product and process designs. As we have seen, some promising materials might be promoted as green or environmentally friendly, but in many instances it is not entirely clear if these materials represent a more sustainable alternative to the traditional materials. For a complete sustainability assessment of new materials, it is necessary to obtain a comprehensive data set for hazard identification, impact assessment, and mitigation. It is necessary for these assessments to be conducted from a life cycle perspective so that the broader implications of new materials are included. Innovation is one of the main drivers for sustainability and cannot be discouraged. At the same time, this innovation needs to be framed by the tenants of sustainability, green chemistry, and green technology, so that the development of new materials accounts for their potential impacts to humans, other species, and the environment.

In Chapter 22 we explore in greater detail the advantages, impacts, needs, and uncertainties of a big sector related to some of the materials we have explored in this chapter: renewable materials.

PROBLEMS

21.1 One potential application for nanoparticles in the electronic manufacturing indus- try is their use in specialty polishing operations, such as chemical–mechanical planarization (CMP), which is critical to semiconductor and chip manufacture.

CMP relies on a slurry of oxide nanoparticles for both chemical reaction and mechanical abrasion between the slurry and the film to obtain smooth and flat silicon wafers. CMP is also used to polish magnetic hard disks. What are the disadvantages and advantages of CMP from a green engineering/green chemistry perspective?

21.2 Some microorganisms have been found to produce nanoparticles. For example, bacterial proteins have been used to produce magnetite in laboratories, yeast cells can

create cadmium sulfide nanoparticles, and gold and silver nanoparticles have been obtained from fungus and viral proteins, respectively. What are the advantages and disadvantages of these potential future methods of producing nanoparticles from a green chemistry/green engineering perspective?

21.3 Carbon nanotubes (CNTs) have potential uses in a wide range of applications (e.g., composite materials, batteries, memory devices, electronic displays, transparent conductors, sensors, medical imaging). However, some scientists have expressed concerns regarding the effects of some CNTs. What are those concerns?

21.4 In Section 21.3 it was noted that applications for PTT are being developed mainly in the fibers and films sectors. What specific commercial applications would this mean for the public?

21.5 Bohlmann performed a streamlined LCA comparison of PLA vs. PP yogurt contain- ers using energy as a surrogate for environmental impact. The results he obtained are given in Table P21.5A.

(a) What conclusions can you draw from the results?

(b) Bohlmann also prepared a sensitivity assessment on the energy production for lactic acid, accounting for the base case (using triple-effect evaporators in the calculations) and the worst case (double-effect evaporators) (Table P21.5B).19 What additional conclusions can you draw from the sensitivity assessment?

21.6 A cradle-to-grave LCA of a few poly(3-hydroxybutyrate) (PHB)-based composites was performed for comparison with petrochemically derived polymers used in cathode-ray tube (CRT) monitor housings [produced conventionally from high-

TABLE P21.5A Bohlmann’s Results

Energy Category PLA PP

Fuel production (MJ/kg) 3.9 6.6

Fuel use (MJ/kg) 47.5 30.8

Transportation (MJ/kg) 4.7 4.8

Feedstock (MJ/kg) 0.6 51.5

Total (MJ/kg) 56.7 93.7

Total (MJ/ton yogurt) 2225 3261

TABLE P21.5B Bohlmann’s Best and Worst Case Analysis

Gross Energy Base Case Worst Case

Energy for lactic acid production (MJ/kg) 30.4 44.1

Total energy for PLA (MJ/kg) 56.7 75.3

impact polystyrene (HIPS)] and internal automotive panels [normally produced from glass-fiber-filled polypropylene (PP-GF)] (Figure P21.6). What conclusions can you draw from the data?

REFERENCES

1. Harper, T., et al.Nanotechnology Opportunity Report. Cientifica Ltd., London, Mar. 2002.

2. Ritter, M. N. GB-201 Opportunities in Nanostructured Materials. Part A: Electronic, Optoelec- tronic and Magnetic Applications; Part B: Biomedical, Pharmaceutical and Cosmetic Applica- tions; and Part C: Energy, Catalytic and Structural Applications. Business Communications Co., Norwalk CT, 2001.

3. Cordis. European Technology Platform. NanoMedicine.http://cordis.europa.eu/technology-plat- forms/pdf/nanomedicine.pdf.

4. Rittner, M. N. Nanoparticles—What’s now? What’s next?Chem. Eng. Prog.2003, 39S–42S.

0 1 2 3 4 5 6 7 8 9

PP PHB-4

PHB-3 PHB-2

PHB-1

0 20 40 60 80 100 120 140 160 180 200

PHB-4 PHB-3

PHB-2 PHB-1

HIPS

Nonrenewable energy (MJ/functional unit) GWP (kg CO2-eq/functional unit)

(b) (a)

FIGURE P21.6 Comparative LCA for (a) automotive parts and (b) CRT housing. HIPS, high-impact polystyrene; PP, polypropylene; PHB-1 to PHB-4, poly(3-hydroxybutyrate) composites.

5. Lewinski, N. Nanomaterials: What are the environmental and health Impacts?Chem. Eng. Prog., 2008, 37–40.

6. Nanotechnology Citizen Engagement Organization. Nanotechnology Health and Safety Proto- cols and Good Practices.http://www.nanoceo.net/nanorisks/OHS-Protocols-Best-Practices, ac- cessed May 3, 2009.

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Congressional Research Service Report for Congress, 2008.

9. U.S. Environmental Protection Agency. Fact Sheet for Nanotechnology Under the Toxic Substances Control Act. http://www.epa.gov/oppt/nano/nano-facts.htm, accessed May 3, 2009.

10. National Cancer Institute, National Institutes of Health, U.S. Department of Health and Human Services,Cancer Nanotechnology Plan: A Strategic Initiative to Transform Clinical Oncology and Basic Research Through the Directed Application of Nanotechnology. U.S. DHHS, Washington, DC, July 2004.

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12. Patel, M. K., Crank, M. Projections for the production of bulk volume bio-based polymers in europe and environmental implications.J. Biobased Mater. Bioenergy, 2007, 1(3), 437–453.

13. Terasawa, I., Tsuneoka, K., Tamura, A., Tanase, M. Development of plant-based plastics technology, “Green Plastic”.Mitsubishi Motors Tech. Rev., 2008, 20, 91–96.

14. Vink, E. T. H., Rabago, K. L., Glassner, D. A., Gruber, P. R. Applications of life cycle assessment to NatureWorksTMpolylactide (PLA) production.Polym. Degrad. Stabil., 2003, 80, 403–419.

15. Harding, K. G., Dennis, J. S., von Blottnitz, H., Harrison, S. T. L. Environmental analysis of plastic production processes: comparing petroleum-based polypropylene and polyethylene with biologically-based poly-b-hydroxybutyric acid using life cycle analysis.J. Biotechnol., 2007, 130, 57–66.

16. Bohlmann, G. M. Biodegradable packaging life-cycle assessment.Environ. Prog., 2004, 23(4), 342–346.

17. Klứverpris, J. H., Wenzel, H., Nielsen, P.H. Life cycle inventory modelling of land use induced by crop consumption: 1. Conceptual analysis and methodological proposal.Int. J. Life Cycle Assess., 2008, 13(1), 13–21.

18. Fargione, J., Hill, J., Tilman, D., Polasky, S., Hawthorne, P. Land clearing and the biofuel carbon debt.Science, 2008, 319, 1235–1238.

19. Bohlmann, G. Biodegradable Polymer Life Cycle Assessment. Process Economics Program Report 115D. SRI Consulting, Menlo Park, CA, 2001.

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