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. 2022 Oct 28;14(21):4578. doi: 10.3390/polym14214578

Table 3.

Environmental impacts of starch polymer and nanofiller compared with LDPE polymer (Functional unit = 1 kg).

Impact Category Ozone Depletion (kg CFC-11 eq.) Global Warming Potential/Greenhouse Gas Emissions (kg CO2 eq.) Smog (kg O3 eq.) Acidification (kg SO2 eq.) Eutrophication (kg N eq.) Human Toxicity, Carcinogen (CTUh) Human Toxicity, Noncarcinogen (CTUh) Respiratory Effects (kg PM2.5 eq.) Ecotoxicity (CTUe) Water Consumption (Kg) Agricultural Land Use (m2yr/kg) Fossil Fuel Depletion/Non-Renewable Energy Use (MJ Surplus) Reference
PE waste management 1.28 × 10−5 3.82 × 103 5.77 × 10 1.39 × 10 c 1.05 × 10−4 [143]
Starch-based polymers production with PBS, PLA/PBAT, PHB, PLA, PBS/fiber, and recycled-PLA 1.8–3.7 1.2–1.9 d 0.3–1.3 33–72 [141]
Starch-stabilized Ag NPs manufacturing via microwave-assisted heating 1.24 × 10−7 8.44 × 10−2 2.37 × 10−1 2.51 × 10−1 1.21 × 10−1 4.44 × 10−6 8.02 × 10−4 6.41 × 102 5.85 × 105 7.08 × 102 [137]
Starch nanofiller preparation using various process 0.00 7.95–13.07 0.5–0.6 a 8.78–15.51 b 0.16–0.23 0.9–0.16 e 2216.99–3747.76 f 0.02 33.15–115.82 h 16–19 [132]
Nanofiller OMMT 1.52 1.139 g 40.079 [144]

a, kg/NOx eq.; b, H+ moles eq.; c, kg PO43- eq.; d, g P eq./kg; e, kg benzene eq.; f, kg toluene eq.; g, g PM; h, kg 2,4-D eq. PM2.5, particulate matter of size under 2.5 µm; 2,4-D, 2,4-dichlorophenoxyacetic acid used as a herbicide and pesticide.