Plastics and the Ocean. Группа авторов
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The limited analysis has several shortcomings, but shows the plastic jug to have the second‐lowest embedded energy as well as carbon emissions. Not captured in Table 1.8 is the water demand, especially in pulping and bleaching of paperboard, as well as the impact of toxic releases from any of the steps. Paperboard enjoys the unique advantage of being based on a renewable feedstock, partly reflected in the value of E1 (it is also biodegradable in the environment). These estimates assume that only virgin materials are used, and if recycling is included, given the high contributions of of E1 and C1 to EE nd EC, these estimates can decrease considerably.
Figure 1.14 Schematic representation of manufacturing a package.
Table 1.8 Energy and carbon footprint associated with packaging milk in various containers. (The percentage of embodied energy and carbon associated with material production phase is shown in parantheses).
Container | Mass of package (kg) | Volume L | Embedded energy (1010 J) (E1%) | Carbon footprint (kg) (C1%) |
---|---|---|---|---|
HDPE jug | 0.051 | 0.946 | 2.95 (82.2) | 1219 (67.7) |
Aluminum can | 8.1 | 50 | 17.52 (95.9) | 10263 (94.7) |
Glass bottle | 0.41 | 1 | 5.82 (68.7) | 3820 (62.0) |
Paperboard carton | 0.057 | 0.942 | 0.65 (84.8) | 278 (73.4) |
Data from Ghenai, 2012
Using packaging with a high environmental cost is justified with food that also has high EE (MJ/kg) and a large carbon footprint (e.g. meats, cheese, coffee, chocolate) as it minimizes waste, and extends shelf life, assuming the consumer will responsibly dispose the packaging waste. If responsible disposal can be assured, plastics would indeed be the ideal packaging material available. A common product that does not conform to the above criteria is bottled water, a popular beverage in the US, with 13.85 Billion gallons sold worldwide in 2018. The environmental cost of the packaging, however, is several orders of magnitude higher than that of the water. The embodied energy of the PET bottle of ~8 MJ/L is enormous by comparison to that of the water of (<0.2 MJ/L) Also, the carbon footprint of the PET bottle is ~42 kg CO2‐e while it is negligible for the water! When transportation, labeling, display, and promotional costs are added, the environmental price tag of bottled water is unacceptably high, especially for water imported from other countries. It is still popular because of its convenience in serving large numbers of people and the misperception that it is more hygienic compared to tap water. An interesting, related comparison is between the environmental merits of paper grocery bags versus plastic bags is pointed out in Box 1.3.
Box 1.3 Paper or Plastic?
A cradle‐to‐grave LCA study in the US (Chet and Yaros 2014) compared the environmental impacts of HDPE bags, biodegradable PE/PLA bags, and Kraft paper bags (with 30% recycled fiber content). The embodied energy for the HDPE bag was 71% lower, and the gobal warming gas (GWG) emissions, 50% lower, compared to the heavier paper bag. Water demand in the manufacture of the HDPE bags was only ~5% of that used to make the paper bags. A 2018 Danish study (DEPA 2018) that included 7 bag types, as well as a 2011 British study (Edwards and Fry 2011), were in general agreement with the conclusions. A plastic bag was the better choice based on these criteria.
The two main problems with HDPE bags, not captured in such studies, are the recalcitrance of plastic bag litter in the environment (not an issue with biodegradable paper bags) and the toxicity of water/air emissions from the manufacture of either type of bag. The acid rain emissions (NOx and SOx) for HDPE bags was ~11% of that associated with paper bags (Chaffee and Yaros 2014). These values are are highly variable, depending on the location of manufacture and consumer littering behavior, and therefore difficult to quantify. The debate on whether the paper or the plastic grocery bags are better for the environment has been in the news for years. With ~5 trillion paper bags used globally each year (or over 150 000 bags a second!) clear guidance to the conscientious consumer will help the environment.
1.7.2 Plastics in Building
As with packaging, only a handful of different plastics are used in building construction; these, along with the percentage of global production used in building, are PVC (69%), HDPE (20%), PUR (29%) and PS (28%). The percentages shown are for that of the global production in 2015 (Geyer et al. 2017). Some LDPE and PP are also used in building, but to a lesser extent of only about 6% of their respective production volumes.
The most‐used resin type in building construction is PVC, both as (i) rigid unplasticized compounds, uPVC, in cladding (siding), window frames, water pipes/fittings, pipes, and rainwater goods; and (ii) plasticized, flexible compounds, pPVC, in laminates as membrane roofing, flooring tiles, and cable sheaths. PVC pipes are widely used in water transport because of their low cost and convenience in installation using quick connections compared to competing water pipes. Some chlorinaed PVC (or CPVC) is also used, especially in hot‐water applications, because of its relatively higher softening temperature compared to PVC. Plastic window or door profiles, also made of uPVC, are widely used because of their ease of installation and relatively low lifetime costs. Flooring made of PVC in laminate or engineered flooring, the most‐used flooring in the US, is also popular in Asia, Australia and some parts of Europe (Pickard and Sharp 2020). HDPE, competes with PVC as a material for pipe applications but has a relatively shorter service life, but is the plastic of choice in constructing storage tanks for water.
Table 1.9 gives a comparison of the environmental characteristics of several different pipe materials for the distribution of potable water. The savings in embodied energy (EE) on using lower‐density, lower melting, non‐corrosive, and easy‐to‐assemble PVC, in place of conventional ductile iron, concrete, or clay pipes is easy to appreciate (Uni‐Bell 2017).
Another important application is the use of plastic foam insulation in building and refrigeration, that exploits their low density as well as their very low thermal conductivity. The closed cells in polyurethane foam contain inert gases that are very good thermal insulators. Until recently, the inert gas used as a blowing agent for PU foam was Freon (especially, trichlorofluoromethane), but after these were identified as ozone‐depleting chemicals, pentanes were substituted in their place. The thermal conductivity of PU foam