For valuing S and E, we would ideally have the same level of detailed information that we have on F. At present, however, we are still far removed from that level. For most companies, GHG emissions are available to some extent, but company level data on the other planetary boundaries are typically missing. On S, indicators are often given, but typically only in relation to a company’s own operations; and reference to the SDGs is usually made, but not data that is actually useful in establishing the company’s contributions to (not) achieving them. As we will see, Inditex is no exception in that it does provide quite some data, but not of the right nature to value S and E.
11.4.1 Quantification: E and S in Their Own Units
When expressing E and S in its own units, we ideally obtain an overview like the one in Table
11.9, that is having yearly amounts for various types of E and S, both historically and projections for the coming years. The list is based on the issues identified in the External impacts part in Sect.
11.2.
Table 11.9
Expression of E and S in their own units
Actually filling out a table like Table
11.9 is quite difficult: in practice, most companies only give historical data for some types of E; and then only for their own operations, not for their value chain. And for forward-looking data, they might give guidance or targets on, for example, GHG emissions. Indeed, for Inditex we find some historical numbers for 2019 and 2020 in the annual report, as well as some targets. For the 2021–2030 projections, we aim to make estimates based on relations with other company KPIs and company targets. The projections need to be linked to the company’s activity levels. This link is imprecise: we can use sales as a proxy, and then ideally only the volume component of sales, so excluding price; but even then, there might be a mismatch between production volumes (which tend to drive emissions and other impacts) and sales volumes. In fact, Inditex discloses the amount of garments it places on the market, which is a proxy for sales volume.
In Table
11.10, we try to quantify the impacts that Inditex makes and start out with the activity levels, which help to put E and S into perspective. Unfortunately, this is a very sobering exercise: we only find usable data for GHG emissions. And even there the picture is clouded by the company’s focus on Scope 1 and 2 (which is in direct control of Inditex), as it effectively hides its much larger Scope 3 emissions in its supply chain (98 to 99% of its total emissions) at the back of its AR 2020.
11 Its ‘main decarbonisation commitments’ involve reducing Scope 1 and 2 by 90% by 2030, but the more important Scope 3 only by 20% by 2050—the company focuses on the former, while the latter is what matters.
Table 11.10
E and S in their own units
Our assumptions are set accordingly, with a 2.5% annual reduction in Scope 3 emissions. This still results in 9.5 million tonnes of Scope 3 emissions by 2050. The other issues remain a series of question marks, for which we can look for proxies in external sources, which we will do in the next sub-section on monetisation.
The question marks mean that these impacts are not reported in the company’s disclosure, which raises the question to which extent the company considers them. After all, the company’s clothing products require cotton plantations, which use large amounts of water and nitrogen. There are emissions in transport and storage. And there is the waste generated across its supply chain, of which the company does report Scope 1 and 2, but not Scope 3; and does not split by waste type, which makes the data useless for our purposes. This also makes it impossible to determine the attribution of E and S: to what extent are they attributable to this company, and to what extent to other parts of the value chain?
Hence, the question of the user of an annual report should not just be: what’s in the company’s annual report? It should very much also be: what should be in their annual report that is currently not there? And how to communicate to the company that it should include it? As a rule, this amounts to timeseries data on the company’s contributions to planetary and social boundaries, ideally in a way that is relatable to its operations volumes. The guiding principle is double materiality: inwardly and outwardly material social and environmental factors should be included.
11.4.2 Monetisation: E and S in Monetary Terms
The third step to arrive at calculating EV and SV is monetisation, which is the expression of impacts in monetary units. To do so is challenging, especially if the non-monetary units are missing. But even then it can be done. The Impact-Weighted Accounts Framework (IWAF)
(IEF,
2022) provides monetisation factors or shadow prices, which can be multiplied by the original units to arrive at monetary values. Table
11.11 lists some of IWAF’s shadow prices—see Appendix A5.1 for a full list of shadow prices with explanations.
Table 11.11
Examples of shadow prices, 2021
Well-being of employment | $2647 per life satisfaction point (scale 0–100) |
Effects on human health | $119,000 per DALY (disability-adjusted life year) |
Occupational health & safety incidents | Fatal occupational accidents: $3,540,000 per accident Occupational injuries with breach of H&S standards: $3840 per accident |
Contribution to/limitation of climate change | $224 per tonne of CO2 equivalent (eq) |
Contribution to/limitation of pollution—air pollution | Human toxicity: $119,000 per DALY Nitrogen deposition NH3 from animal husbandry: $18.10/kg NH3 eq Particulate matter (PM) formation: $75/kg PM2.5 eq |
Contribution to/limitation of pollution—water pollution | Freshwater eutrophication: $290/kg P eq to freshwater Marine eutrophication: $20.10/kg N eq to marine water |
Contribution to/limitation of availability of scarce natural resources | Land occupation—tropical forest $3030/(MSA*ha*yr) Land occupation—other forest $1450/(MSA*ha*yr) Scarce blue water use $1.49/m3 |
Contribution to/limitation of poverty | Underpayment in the value chain—Wage gap of workers earning below minimum wage $1.56 per $1 of wage gap |
Contribution to/limitation of human rights violations | Underage workers—below minimum age (12 or 13) for light work in non-hazardous economic work $21,600/child FTE Forced workers—$17.200/FTE Harassment—workers who experienced severe physical sexual harassment $85,800/worker Lack of freedom of association $527/violation |
From Table
11.11, we can directly apply the shadow price for contribution to climate change, which is €204 (=$224/1.1) per tonne of CO
2 equivalent in 2021. The carbon price is projected to increase with 3.5% per year (see Chap.
5). Total emissions (the top line in Table
11.12) are taken from Table
11.10. Following IEF (
2022), we assume that Scope 3 carbon emissions are 50% attributable to Inditex, as primary company in the supply chain (see Chap.
5). Table
11.12 shows how the resulting flows are calculated and discounted at the social discount rate of 2.2% (see Chaps.
4 and
12) to arrive at the present value of Inditex’s contribution to climate change, which amounts to −€101.3 billion.
Table 11.12
E flows and EV for climate change
Of course, that large negative number is a result of the assumptions we made (still resulting in 9.5 million tonnes of CO
2 equivalent, as stated in Sect.
11.4.1), which are in turn driven by Inditex’s targets. For the other environmental and social issues, we lack the required data and cannot make such specific calculations. The rest of E is not there or hard to attribute (e.g., waste), and so is all of S. Hence, we don’t have the volumes of units to multiply with the monetisation factors. This applies not just to Inditex but is also typical for most companies. So, for the remaining issues we need to take shortcuts, such as using data of comparable companies or industry averages. In this case, we look for apparel data elsewhere. A publication by Impact Institute (
2019)
on the true price of jeans is quite helpful. Table
11.13 lists the components of the true price of jeans.
Table 11.13
Components of the true price of jeans
The data from Table
11.13 allow us to calculate the proportions of negative S and E impacts in the true price of jeans, which we can extrapolate to apparel in general and Inditex in particular. We admit that this is a stretch, but it is the best we can do now given our current information.
Table
11.14 provides the proportions of E and S in the true price. The top panel expresses the amounts as percentage of E, which is €10.9 (see E total in Table
11.13). The first line shows the GHG emissions (climate change) from Table
11.13 as a percentage of E: 15% (=€1.61/€10.9). The second line shows the S total for each stage of the production process in Table
11.13 as a percentage of E: 202%. So, total S is twice as high as total E.
Table 11.14
Proportions of E and S in the true price of jeans
The bottom panel expresses E and S as a percentage of the sales price, which is €80 per jeans. The GHG emissions are 2% (=€1.61/€80) of sales. Other E are 12% of sales. To prevent overestimation, we include only 50% of bonded labour in the S calculation, which is 20% of sales.
The above can be projected on Inditex in several ways. For example, we could assume that the other E impacts (i.e. E excluding GHG emissions) are 12% of sales of €29.6 bn in 2021 (Table
11.6): €3.5 bn per year. Or that the other E impacts are 6× larger than GHG emission impacts of €2.0 bn in 2021 (Table
11.12): €12.0 bn per year. However, we also observe that GHG emission impacts as a percentage of sales are much higher at Inditex (7% of sales, calculated as € 2.03 bn from Table
11.12 divided by €29.6 bn from Table
11.6) than in jeans (only 2% of sales in Table
11.14). This is partly due to much higher carbon prices, but does not fully explain the difference. We therefore feel that it’s better to stay on the lower side and go with the 12% of sales assumption for the other E impacts.
Next, we give Inditex the benefit of the doubt that it will materially bring down that number over time, with a 4% annual improvement. In addition, we assume that they are only 50% attributable to Inditex (as we do in Table
11.12). After all, not all these emissions are directly due to Inditex’ activities; a part is at suppliers—although then too, Inditex shares part of the responsibility. Chapter
5 explains that 50% of the E and S effects should be attributed to the integrated valuation of Inditex, as primary company in the supply chain, and the other 50% to the integrated valuation of other companies in the supply chain. Based on these assumptions, we calculate total E flows in Table
11.15. They amount to circa −€3.7 bn per year and a total EV of −€182.5 bn.
Table 11.15
Calculating E flows and EV for Inditex
For calculating S flows, we take a similar approach. The results are shown in Table
11.16. In the true price of jeans, S accounts for 28% of sales. However, that number is inflated by a very high number for bonded labour, which accounts for over half (€11.95 out of €22.20) of the negative S in the true price of jeans. To be on the conservative side, we take only half of that amount for the negative impacts of apparel. We arrive at negative S impacts of 20.3% of sales attributable to Inditex, which we apply in Table
11.16. Again, we give Inditex the benefit of the doubt that it will materially bring down that number over time, with a 4% annual improvement. We also attribute 50% of the negative S impacts to Inditex, because part of the negative S impacts occur at suppliers for which Inditex bears some responsibility as primary company in the supply chain. Based on these assumptions, we calculate total S flows in Table
11.16. They amount to circa −€2.9 bn per year and total negative SV of −€137.2 bn.
Table 11.16
Calculating negative S flows and negative SV for Inditex
The above numbers only include the negative S impacts of Inditex. However, the company also creates positive S impacts, such as the client value of its products (on top of what people pay for them), taxes, and the well-being of employment. The calculation of positive SV is shown in Table
11.17.
Table 11.17
Calculating positive S flows and positive SV for Inditex
Paid taxes of €0.5 billion were 2.2% of sales in 2020,
12 but that number is not representative due to the Covid-19 pandemic. The corporate tax expense amounted to about €1.0 billion in the preceding years, or 3.7% of sales. The property and environmental taxes were 0.6% of sales. Combining the taxes, we arrive at a tax rate of 4.3% of sales.
The consumer surplus is a measure of consumer welfare and is defined as the social valuation of a product in excess of the price actually paid. As explained in Chap.
5, the consumer surplus is calculated as
\( \left(\frac{Sales}{Price\ elasticity\ of\ demand}x\frac{1}{2}\right) \). Khaled and Lattimore (
2006) find an average price elasticity of men’s and women’s clothing of 3.452. In the case of Inditex, the consumer surplus amounts to €2.955 billion (=€20.4 billion/3.452*0.5). This value has been created together by Inditex and its supply chain partners. We assume that the consumer surplus is 50% attributable to Inditex (and can be included in its integrated valuation), i.e. €1.478 billion, or 7.2% of sales.
The well-being of employment refers to additional well-being experienced by employees resulting from their employment at the company. We assume two life satisfaction points of €4813 (=2*$2647/1.1) (see Table
11.11). If we apply this to Inditex’ workforce of 144,116, we arrive at €694 million, or 3.4% of sales. However, since 2020 was a year with dramatically lower sales (i.e. inflating employees/sales), we have to correct this number for the lower sales of 31% in 2020 (which is a combination of a 28% drop in sales combined with an average sales growth of 3%) and use 2.3% (=3.4%*[100%–31%]) from 2021 onwards.
Adding up these numbers gives positive S flows of 13.9% of sales, which is over €4 billion per year—and growing; and a positive SV of €282.9 billion. Admittedly, positive SV benefits from growth, whereas negative SV (and negative EV) are based on more or less stable flows, since the reductions are already partly factored in.
Again, the above numbers are based on very rough assumptions, and hence very imprecise. However, they are the best estimate we have at this stage. And they point the way forward towards better data. For example, having academic evidence on the social value of apparel could help us make better assumptions. This applies even more strongly to data disclosed by the company on E and S in their own units.