Plastics and the Ocean. Группа авторов

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(Ghenai 2012) are shown in Table 1.8. Note however, that these values are based on LCA and therefore, may vary with location, time, and technology used (Figure 1.14).

Schematic illustration of manufacturing a package.
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

      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.

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