Research Article |
Corresponding author: Henry I. Penikas ( penikas@gmail.com ) © 2023 Non-profit partnership “Voprosy Ekonomiki”.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY-NC-ND 4.0), which permits to copy and distribute the article for non-commercial purposes, provided that the article is not altered or modified and the original author and source are credited.
Citation:
Penikas HI, Vasilyeva EE (2023) Measuring climate-credit risk relationship using world input-output tables. Russian Journal of Economics 9(1): 93-108. https://doi.org/10.32609/j.ruje.9.83891
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The Basel Committee recommended the use of input-output tables to properly measure climate risks. However, the majority of previous studies only limits the use of input-output tables to carbon emissions and this is not applied in climate risk ratings. The existing climate (E) risk ratings (scores) was modified or transformed from Sustainalytics to the full climate risk scores using input-output tables. Positive relationship between credit risks and the full climate risk estimates at the industry level was identified, and this justifies the interest rate discount granted to firms in the green industries. Thus, for the purpose of lending the full degree of greenness derived from input-output tables should be considered, not substituting this by the easily observable and publicly available marginal climate risk ratings like those provided by Sustainalytics.
climate risk, input-output tables, WIOD, Poisson regression, ESG.
Climate risk and climate change risk play an important role on the global agenda specifically after the year 2018 when the respective Nobel Prize in economics was awarded (
Moreover, the broader debates of climate risk led to the introduction of the “green swan” special term see
Nevertheless, the Basel Committee initiated discussions on how to create a financial “cushion” against the climate-change-related financial risk implications (
Though climate change is globally discussed, putting it right now on central banks’ agendas and adjusting banking regulations with respect to it might be a premature step. For instance, there was a U.S. Federal Reserve nominee who actively promoted the stance, argued that it should be the central bank (i.e., the Federal Reserve Board (FRB) in the U.S.) that has to take responsibility for the issue (
The key point from the above discussion is that climate change may pose a challenge to the financial system, but whether it should fall to the central bank to handle it is a contentious issue. So the central banks need to probe the topic more deeply themselves, as well as motivate stakeholders to raise their financial literacy with respect to climate risk.
In line with this, the Bank of Russia actively promotes such an agenda by organizing conferences where people are able to share their views as well as gain insights from those colleagues who are strongly involved in the subject. For instance, during the summer 2022, a conference was administered by the Bank of Russia together with the New Economic School.
Overall, the Bank of Russia collects all the relevant information about sustainable development in general and climate risk in particular at its website.
By promoting the climate change discussion forums, the Bank of Russia stresses on how important the issue is to the Russian economy. Such a priority as part of ESG domain is coined in the Bank of Russia prospective monetary policy measures (
The Bank of Russia’s activity within climate risk measurement and management may well illustrate how broad the subject area is. This paper seeks to answer a particular research question relevant to finance, risks, and the financial stability managed by central banks. Specifically, it is to evidently determine if there is any climate-credit risk relationship. Thus, it investigates whether “greener” (more climate-friendly) projects and companies are worth a credit risk discount (i.e., should receive loans at lower rates or not) benchmarked to their “brown” peers.
The limitation of this study is that previous relationships may not demonstrate the likely effects after the green transition, i.e., when green energy and green production come to be preferred over “brown” rivals.
Available climate risk ratings and well-known credit ratings were used in this study. The limitation is that each climate risk rating as well as credit rating might have its specificities, and this may cause different paths and dependence signs. However, in our opinion, it is particularly important to study alternative data sources or study alternatives to conventional methodologies to ascertain whether the earlier findings, conclusions and statements are reliable. For instance, if the various studies are able to demonstrate that the climate-credit risk has a positive relationship, then green projects and companies should be favored over “brown” ones when pricing debt obligations. However, if these studies arrive at contradicting findings, this may signal that it is irrational to differentiate the green projects and companies from the “brown” ones based exclusively on the risks they pose to the climate.
This study contributes to the literature in terms of methodology as well as content. Methodologically, three building blocks that were previously treated separately were combined. Available climate risk ratings from Sustainalytics, and not the widespread carbon (CO2) emissions was used in this study. By using input-ouput tables climate risk was fully studied. Full climate risk against the default probability was benchmarked. This helps to arrive at a conclusion that there is a positive climate-credit risk relationship at the industry level.
However, it is important to indicate that the findings herein do not mean that it is sufficient to consider neither firms with the highest climate risk ratings nor the most creditworthy company as the “greenest.” To make such a statement, one needs to transform the marginal risk into the full estimate. And this is neither a straightforward, nor a simple arithmetic exercise that can be easily processed by a single person.
There are three major streams of literature that interconnect the discussion of the relationship between full climate and credit risks. The first one focuses on climate risk of financial implications. The second discusses green finance and credit risk. The third is devoted to the use of input-output tables. However, none of these works dealt with the three issues simultaneously (Table
# | Paper | Input-output | Climate risk | World trade | Credit risk (bonds) | Green finance (equity) | ||
---|---|---|---|---|---|---|---|---|
CO2 emissions | Other ratings, incl. Sustainalytics | |||||||
1 |
|
– | + | – | – | – | – | |
2 |
|
– | + | – | – | + | – | |
3 |
|
– | + | – | – | + | + | |
4 |
|
– | + | – | – | + | + | |
5 |
|
– | + | – | – | + | + | |
6 |
|
– | + | – | – | + | + | |
7 |
|
– | + | – | – | + | + | |
8 |
|
– | – | + | – | + | – | |
9 |
|
– | + | + | – | + | – | |
10 |
|
– | + | + | – | + | – | |
11 |
|
– | + | + | – | + | – | |
12 |
|
– | + | + | – | + | – | |
13 |
|
– | + | + | – | – | + | |
14 |
|
– | – | + | – | + | – | |
15 |
|
– | + | + | – | – | + | |
16 |
|
– | – | + | – | + | + | |
17 |
|
+ | + | – | + | – | – | |
18 |
|
+ | – | – | – | – | – | |
19 |
|
– | + | – | – | – | – | |
20 |
|
– | + | – | – | – | – | |
21 |
|
+ | + | – | + | – | – | |
22 |
|
+ | + | – | + | – | – | |
23 |
|
+ | + | – | + | – | – | |
24 |
|
+ | + | – | + | – | – | |
25 |
|
+ | + | + | – | + | + | |
26 | Current paper | + | – | + | – | + | + |
Wassily Leontief should be considered the pioneer of climate risk debate as in his Nobel Lecture (
However, most scholars credit Professor Nordhaus for his works in the field of climate risk research, which earned him the Nobel Prize in economics (
The second stream of literature focuses on green finance as a tool to fund climate-friendly or climate-improving projects like in
However, all these papers are limited to studying the so-called marginal climate risks. These are the risk values directly observed or derived from existing climate (E) ratings. The limitation of such an approach is the mistreatment of formally green industries that nevertheless consume certain “brown” inputs. From the full climate risk perspective such industries are by no means green, although it is difficult to compute full climate risk. If such data was present the authors could have redone or extended their research and most probably adjusted their concluding statements and recommendations.
The third stream of research focuses on the use of input-output tables (IOTs). The Basel Committee sees IOTs as a possible way to derive full climate risk (
This paper merges the various approaches from the three literature streams mentioned above. First, the marginal climate risk estimates from the climate risk ratings were used, which as far as this paper is concerned are more comprehensive than the mere CO2 emissions. Second, the paper transits from these marginal climate risk estimates to the full ones by using IOTs. Third, the relationship between the derived full climate risk measures and the creditworthiness measure was tracked, i.e., the probability of default (PD). Thus, we can make recommendations on the loan pricing and climate-risk-related financial regulation.
Two different datasets were used: the climate and credit risk data and IOTs. The climate and credit risk data were retrieved from Yahoo Finance
Data from Forbes Global 2000,
Half of the companies have the E risk scores. For each, the credit ratings were collected and the historical default rate was assigned as the probability of default (PD) proxy to each of them. See
The data focus might be seen as a non-representative of a particular company or industry. However, two advantages of such an approach must be taken into account. First, the larger the company, the higher the probability of it having a climate risk rating. Second, psychologically, people tend to processing information from a reduced-dimensional information. That explains why people prefer indexes to sets of inputs. The financial sector performance is conventionally studied by the dynamics of the stock indexes. Those are often either the simple or weighted sums or the averages of the stock quotes of the largest companies. The example is the Moscow Exchange (MOEX) index. It includes 50 stocks (MOEX, 2022, p. 11, par. 3.3.1). That is why it is a conventional approach in finance to focus on the largest companies. As climate risk is on the global agenda, it is natural to consider the world’s largest companies, e.g., the Global 2000 list, as we did.
Fig.
The straight-forward credit-climate risk relationship is not stated. The respective trend line is almost horizontal (see panel A at Fig.
For that purpose the World Input-Output Database (WIOD) from
The recent version of WIOD tables which covers 2000–2014 was processed. The last 2014 release, which consists of 56 industries and 43 countries according to WIOD classification, was used.
The climate risk data stands for 2022, while IOTs — only for 2014. However, there is no time to wait another 8 years when the IOTs of 2022 could be utilized for benchmarking against 2022 climate risk data. Thus, the “second best” option available was employed.
To proceed in a unified format, the industry and country classifiers from the climate (Bloomberg) risk part of the dataset and that from the WIOD ones were merged. For the countries, some of the Bloomberg countries were grouped to arrive at the WIOD classification.
While for the industries, the procedure was longer as two groupings were made. A group of Bloomberg industries could correspond to a single WIOD classification. Moreover, this could take place in the opposite direction. Consider Table
WIOD | Bloomberg | |||||
Code | ISIC_Rev_4 | WIOD_industry_name | ind_code | ind_name | ||
r05 | C10-C12 | Manufacture of food products, beverages and tobacco products | 10 | Beverages | ||
36 | Food processing | |||||
69 | Tobacco | |||||
r07 | C16 | Manufacture of wood and of products of wood and cork, except furniture; manufacture of articles of straw and plaiting materials | 38 |
Furniture and fixtures | ||
r22 | C31_C32 | Manufacture of furniture; other manufacturing |
To evaluate the sign of the relationship between the credit risk and the full climate risk we need to proceed in three steps:
1. Derive the marginal climate risk per industries and countries;
2. Obtain the full climate risk;
3. Benchmark the full climate risk to the credit risk.
To derive the marginal climate risk, a Poisson regression with the company-level climate (E) risk scores as the dependent variable and the country and industry dummies as the independent ones was run. The Poisson regression is preferred to the classical ordinary least squares (OLS) one as we need the output variable of the climate risk to be non-negative (this requirement is violated when proceeding with OLS).
We include the intercept when running the regression. We run full sample estimation with no validation at the testing set as explained by
Then we transit from the marginal risk estimates to the full ones. To do so, the input-output-based cost computation introduced by Wassily Leontief was used.
The production structure of the economy is characterized by the production function. More precisely, by the technological coefficients aij = xij/yj. The coefficient aij shows how much the monetary contribution of i-th factor xij is to the total monetary cost of the j-th good output yj. Given the interrelationship of industries we may derive a Leontief matrix of these technological coefficients A = {aij}i,j = 1, ..., N. The matrix L = (I – A)–1 is referred to as the Leontief inverse matrix.
Let F = {F1, …, FN}′ be a vector of end consumption by producers, and apostrophe denotes the transpose operation. Hence the total production cost can be derived as follows:
y = (I – A)–1F, (1)
where y = {y1, …, yN}′ is a vector of total output.
To apply the input-output cost computation methodology to climate risk we introduce the full risk R = {R1, …, RN}′. The underlying logic fully replicates the Leontief technological cost approach. If the industry consumes some factors including from itself, and the marginal (own) climate risk assessment of each industry is r. Then the total climate risk per industry has to trace back the entire production chain, by weighting the inputs proportionate to their technological contribution A. Thus, the full climate risk is obtained as follows:
R = L′ r. (2)
Finally we aggregate the full climate risk estimates at the level of industries and countries separately to benchmark those against the credit risk aggregates per countries and industries. We present the charts, as well as baseline linear regressions with the mean of PD logarithms by country or by industry being the dependent variable and the full climate risk as the independent one.
For the robustness check we recall the stylized fact about our dataset. The marginal climate risk estimates are available only for half of the observations; see panel D at Fig.
The country and industry data is presented in Appendices A and B. It can be considered as the country and industry relative ranking between themselves on the ground of the full climate risk data. For comparison, the mean values of the marginal climate risk were added to provide a reader with the feeling of scale as to how much the full climate risk changed when transiting from the marginal one, but expressed in the same units of measurement as the marginal one.
The marginal climate risk data for Greece and Hungary were unavailable, although there are five companies from these countries with PD available. Nevertheless, the full climate risk is available for for the countries mentioned above as they form part of the global division of labor and have non-zero technological coefficients in WIOD set. Hence, the countries were included in our main findings, but they were excluded from the robustness check. As a result, the number of country observations changes from 35 in Table
Variable | M_cty | M_ind | F_cty | F_ind |
---|---|---|---|---|
Environm | –0.048*** | 0.002 | ||
IOfull | –0.032** | 0.015* | ||
_cons | –5.082*** | –5.300*** | –5.058*** | –5.511*** |
R 2 | 10.40 | 0.00 | 6.40 | 4.00 |
Adjusted R2 | 7.50 | –2.40 | 3.50 | 1.60 |
N | 33 | 43 | 35 | 43 |
Robustness check: Regression for data with non-empty climate risk scores.
Variable | M_cty | M_ind | F_cty | F_ind |
---|---|---|---|---|
Environm | –0.013 | 0.002 | ||
IOfull | 0.005 | 0.015* | ||
_cons | –5.930*** | –5.300*** | –6.096*** | –5.511*** |
R 2 | 1.70 | 0.00 | 0.40 | 4.00 |
Adjusted R2 | –1.50 | –2.40 | –2.90 | 1.60 |
N | 33 | 43 | 33 | 43 |
Our research objective was to trace the relationship between the credit risk and the full climate risk. The findings are presented in four charts in Fig.
Credit-climate risk relationship at the country and industry levels.
Source: Compiled by the authors.
Table
Transiting to the full climate risk makes to meaningful difference at the country level, compare panel B to A in Fig.
Past credit data was used, which do not consider the green transition. Therefor if a simulation scenario analysis was performed when consumers shift to greener energy and to more climate-friendly goods and services, which might have resulted in a positive relationship between credit and climate risks.
At the industry level we notice a shift from the horizontal trend in panel C of Fig.
To sum up, we find that industry-wide there is a positive relationship of credit risk and the full climate one, despite the fact that past historical data was analyzed.
The previous section dealt with the credit risk estimated across the entire set of companies within a country or an industry. However, there is a downward bias in the mean PD values for companies that were assigned with the marginal climate risk by Sustainalytics, recall panel D at Fig.
To ensure confidence level of the findings herein, we limit the PD estimates to the companies with the non-empty marginal climate risk data only. The robustness check results are available in Fig.
Robustness check: Climate-credit risk relationship for data with non-empty climate (E) risk scores.
Source: Compiled by the authors.
Then an angle change was observed — though statistically insignificant — at the country level also, compare panel B to A at Fig.
Thus, it must be noted that despite the use of past performance data that does not account for the prospect of the green transition, a positive credit-climate risk relationship at the industry level was revealed. The use of input-output tables and the study of full climate risk measure help arrive at this conclusion.
Previous studies argued for the positive climate-credit relationship presence (see
Previous studies used the marginal climate risk data which as far as this paper is concerned does not help to arrive at reliable conclusions. It is an obvious fact that can quickly be found the research studies. However, the marginal climate risk may produce a biased perception of an industry. To achieve reliable result, the Basel Committee recommended using IOTs. However, the input-output tables approach is applied to carbon emissions in most studies but its use is neglected in the marginal climate ratings.
Despite the use of past data for this study, it was revealed that a positive relationship exists between credit risks and the full climate risks at the industry level.
The authors are grateful to V. Azarina, S. Dzuba, and S. Shibitov for assistance in data collection. The authors acknowledge K. Yudaeva, N. Turdyeva, D. Musaelyan, V. Loginova, D. Nguyen, and T. Walther for discussing the topic and raising valuable proposals. The authors also thank the anonymous reviewer whose comments helped to improve the research.
# | Industry | Freq_PD | PD_all, % | PD_E, % | Freq_E | E_mean | E_IO_full |
---|---|---|---|---|---|---|---|
1 | Advertising | 7 | 0.23 | 0.23 | 5 | 0.06 | 4.49 |
2 | Aerospace & defense | 37 | 0.85 | 0.29 | 17 | 6.69 | 11.86 |
3 | Air courier | 25 | 0.74 | 0.12 | 10 | 6.22 | 11.51 |
4 | Airlines | 27 | 1.21 | 1.13 | 8 | 9.84 | 22.82 |
5 | Aluminium | 19 | 0.50 | 0.40 | 10 | 6.96 | 25.18 |
6 | Apparel/accessories | 39 | 0.30 | 0.23 | 26 | 1.59 | 14.67 |
7 | Auto & truck manufactures | 34 | 0.55 | 0.34 | 24 | 7.22 | 21.83 |
8 | Auto & truck parts | 43 | 0.69 | 0.27 | 20 | 5.40 | 17.77 |
9 | Beverages | 120 | 0.60 | 0.28 | 51 | 3.63 | 15.30 |
10 | Biotechs | 32 | 0.23 | 0.16 | 16 | 6.79 | 14.82 |
11 | Broadcasting & cable | 74 | 0.50 | 0.30 | 43 | 8.18 | 13.51 |
12 | Business & personal services | 31 | 0.85 | 0.65 | 13 | 1.92 | 6.69 |
13 | Business products & supplies | 61 | 0.57 | 0.42 | 36 | 1.99 | 6.39 |
14 | Casinos & gaming | 123 | 1.03 | 0.62 | 59 | 3.78 | 9.21 |
15 | Computer & electronics retail | 180 | 0.69 | 0.21 | 88 | 4.36 | 20.15 |
16 | Conglomerates | 6 | 0.55 | 0.35 | 3 | 2.18 | 14.30 |
17 | Construction materials | 74 | 0.46 | 0.22 | 36 | 9.67 | 22.45 |
18 | Containers & packaging | 14 | 0.91 | 0.28 | 9 | 3.70 | 16.47 |
19 | Department stores | 128 | 0.54 | 0.28 | 70 | 6.97 | 10.41 |
20 | Diversified chemicals | 12 | 0.30 | 0.15 | 7 | 3.52 | 16.92 |
21 | Diversified metals & mining | 42 | 0.38 | 0.20 | 23 | 12.90 | 23.68 |
22 | Diversified utilities | 66 | 0.71 | 0.36 | 20 | 16.20 | 22.66 |
23 | Drug retail | 140 | 0.64 | 0.28 | 63 | 5.63 | 10.10 |
24 | Electric utilities | 6 | 0.93 | 0.21 | 2 | 1.08 | 13.73 |
25 | Electrical equipment | 138 | 0.45 | 0.29 | 67 | 13.58 | 32.38 |
26 | Environmental & waste | 41 | 0.30 | 0.22 | 24 | 5.39 | 11.69 |
27 | Furniture & fixtures | 42 | 0.65 | 0.20 | 16 | 6.08 | 17.11 |
28 | Heavy equipment | 49 | 1.11 | 0.78 | 18 | 7.05 | 21.07 |
29 | Home improvement retail | 35 | 0.70 | 0.21 | 16 | 7.52 | 11.18 |
30 | Hotels & motels | 14 | 0.25 | 0.17 | 11 | 3.88 | 10.52 |
31 | Internet & catalog retail | 37 | 0.42 | 0.28 | 25 | 7.51 | 12.84 |
32 | Natural gas utilities | 166 | 0.56 | 0.23 | 83 | 13.15 | 31.07 |
33 | Other transportation | 31 | 0.34 | 0.18 | 20 | 6.25 | 15.05 |
34 | Paper & paper products | 32 | 0.60 | 0.33 | 16 | 3.58 | 14.85 |
35 | Pharmaceuticals | 11 | 0.39 | 0.35 | 6 | 11.40 | 23.46 |
36 | Printing & publishing | 3 | 0.20 | 0.14 | 2 | 1.50 | 5.11 |
37 | Railroads | 16 | 0.69 | 0.26 | 8 | 0.46 | 8.91 |
38 | Real estate | 18 | 0.27 | 0.29 | 15 | 7.89 | 9.81 |
39 | Recreational products auto | 4 | 0.42 | 0.15 | 1 | 0.07 | 5.79 |
40 | Software & programming | 37 | 0.23 | 0.19 | 21 | 7.99 | 12.73 |
41 | Specialized chemicals | 35 | 0.76 | 0.38 | 13 | 2.41 | 17.00 |
42 | Trading companies | 10 | 0.19 | 0.12 | 6 | 7.10 | 9.99 |
43 | Financial | 7 | 0.74 | 0.13 | 3 | 4.17 | 8.54 |
# | Country | Freq_PD | PD_all, % | PD_E, % | Freq_E | E_mean | E_IO_full |
---|---|---|---|---|---|---|---|
1 | Australia | 36 | 0.20 | 0.18 | 23 | 7.93 | 13.41 |
2 | Austria | 5 | 0.17 | 0.16 | 4 | 8.90 | 11.18 |
3 | Belgium | 8 | 0.25 | 0.11 | 4 | 4.20 | 9.20 |
4 | Brazil | 30 | 0.90 | 0.58 | 12 | 11.75 | 16.84 |
5 | Canada | 61 | 0.62 | 0.28 | 33 | 8.25 | 13.34 |
6 | China | 291 | 1.03 | 0.67 | 66 | 9.21 | 23.83 |
7 | Czech Republic | 1 | 0.11 | 0.11 | 1 | 18.32 | 17.35 |
8 | Denmark | 13 | 0.36 | 0.16 | 10 | 3.32 | 7.70 |
9 | Finland | 10 | 0.32 | 0.17 | 4 | 6.95 | 10.03 |
10 | France | 71 | 0.34 | 0.18 | 36 | 3.83 | 7.30 |
11 | Germany | 63 | 0.42 | 0.35 | 43 | 6.62 | 10.80 |
12 | Greece | 4 | 0.54 | n/a | n/a | 10.86 | |
13 | Hungary | 1 | 0.30 | n/a | n/a | 13.41 | |
14 | India | 43 | 0.64 | 0.40 | 24 | 10.83 | 16.45 |
15 | Indonesia | 5 | 0.20 | 0.15 | 3 | 11.61 | 29.78 |
16 | Ireland | 15 | 0.88 | 0.23 | 7 | 4.51 | 9.37 |
17 | Italy | 19 | 0.60 | 0.32 | 7 | 4.90 | 7.75 |
18 | Japan | 200 | 0.41 | 0.24 | 137 | 6.85 | 12.93 |
19 | Luxembourg | 9 | 0.25 | 0.35 | 2 | 3.93 | 15.77 |
20 | Mexico | 18 | 0.25 | 0.18 | 9 | 13.20 | 13.74 |
21 | Netherlands | 24 | 0.29 | 0.17 | 9 | 6.95 | 10.59 |
22 | Norway | 9 | 0.16 | 0.15 | 6 | 9.95 | 14.18 |
23 | Poland | 6 | 0.24 | 0.24 | 4 | 22.22 | 19.24 |
24 | Portugal | 5 | 1.42 | 0.24 | 1 | 8.02 | 7.63 |
25 | Russia | 56 | 0.66 | 0.24 | 8 | 16.16 | 18.16 |
26 | South Korea | 60 | 0.59 | 0.24 | 28 | 8.86 | 17.35 |
27 | Spain | 24 | 0.77 | 0.31 | 9 | 3.48 | 6.38 |
28 | Sweden | 24 | 0.16 | 0.16 | 18 | 5.25 | 9.55 |
29 | Switzerland | 42 | 0.58 | 0.63 | 23 | 5.20 | 9.82 |
30 | Taiwan | 39 | 0.34 | 0.20 | 15 | 7.98 | 17.34 |
31 | Turkey | 9 | 1.49 | 0.30 | 1 | 2.39 | 4.90 |
32 | United Kingdom | 99 | 0.64 | 0.25 | 32 | 4.22 | 8.99 |
33 | USA | 662 | 0.59 | 0.29 | 418 | 6.40 | 10.21 |
34 | Rest of the world | 104 | 0.54 | 0.24 | 33 | 7.51 | 15.68 |