Internet’s handprint

Author(s): Anders S.G. Andrae1
1Huawei Technologies Sweden AB, Kista, Sweden
Copyright © Anders S.G. Andrae. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

In this decade there will an unprecedented growth of generated data, computations, instructions, and operations. This growth may not compromise clean air, clean water and a sustainable energy and material usage, but rather facilitate these prerequisites for flora and fauna. There are many indications (expected trends and estimates) showing that the Internet Sector will be able to provide solutions to other Sectors such as Buildings, Transportation and Industry which will help reduce the total global consumption of energy and materials. For instance, products are replaced by virtual services e.g. by using e-readers instead of paperbacks, and transportation is avoided by online shopping or Internet meetings. This is more resource and energy efficient than before and entire sectors, like transport, industry, and agriculture can be optimized. Internet may foster new sustainable lifestyles which can lower the affluence despite certain rebound effects. The underlying idea is that e.g. human-related global greenhouse gas (GHG) supply can be significantly halted if existing and developing ICT Solutions are used in other sectors (and in the Internet infrastructure itself) to cause a handprint. Such solutions include products-sold-as-services, smart Grid and smart metering. Compared to earlier approaches, the 2020 transformative effects on smart work, land use and smart circularity are included in the discussion, as well as consequential LCA modelling. Internet’s handprint will be 4-7 times its footprint in 2030. The handprint is highly dependent e.g. on how large share of the buildings can adopt smart metering and the product to service rate. Internet will in itself use intelligent ICT solutions as well as neuromorphic, reversible and superconducting computing as well as nanophotonics to mitigate its own material and energy use. However, more importantly the intelligent ICT solutions should be used in the rest of the society to reach efficiency goals. Power saving is a highly efficient strategy for cost reduction in the Internet Sector itself and beyond.

Keywords: Agriculture; Ammonia; Buildings; Grid; Circularity; Communication; Consequential LCA; Consequential handprint; Computing; Data center; Data traffic; Deflation; Devices; Electricity use; Forest; Footprint; Forecast; Functionalities; Handprint; Hydrogen; Information; Internet; Iand use; Marginal variable change vectors; Operations; Transport; Travel; Waste.

1. Introduction

In the present decade there will be an unprecedented growth of generated data, computations, instructions and operations. This growth may not compromise clean air, clean water and a sustainable energy and material usage, but rather facilitate these prerequisites for flora and fauna. Overall, global primary energy consumption rises due to the Internet [1] and Internet’s own electrical energy consumption is also rising [2,3,4]. Plausibly the global primary energy and electricity consumption would rise even faster without the handprint of certain ICT solutions. The Internet Sector is one of few which might off-set its own electrical energy consumption and GHG supply, i.e., its handprint [5] is larger than its footprint. There are many indications (expected trends and estimates) showing that the Internet infrastructure will be able to provide solutions – within main Sectors such as Buildings, Transportation and Industry – which will help reduce (halt the increase of) the total global consumption of energy and materials [6]. Information and communications technologies (ICTs) can potentially contribute to reduce resource consumption through increased productivity in many Sectors by enabling total optimization and dematerialization, occasionally using artificial intelligence (AI) [7]. Internet’s deflationary characteristics suggest that it has a handprint. AI and machine learning (ML) are cornerstones of intelligent ICT Solutions which make them unique compared to incremental improvements. For instance, products are replaced by virtual services, e.g., by using e-readers instead of paperbacks [8], transportation is avoided by online shopping or online chatting. This is more resource and energy efficient than before and entire sectors, like transport, industry, and agriculture can be optimized. Internet may foster new sustainable lifestyles which can lower the affluence despite certain rebound effects. E.g. e-reader adopters are yet to fully abandon paper books for e-books suggesting a total net increase [8]. The underlying idea is that e.g. total anthropogenic global GHG supply (TAGGHGS) can be significantly halted if existing and developing ICT Solutions are used in other sectors (and Internet itself [9]) to their “full potential” in a smart manner. Such solutions include Products-sold-as-Services, Smart Grid and Smart Metering. The avoidance potential is highly dependent e.g. on how large share of the building GHG supply can be reduced by Smart Metering [10,11].

Internet will use smart ICT solutions to keep its own material and electrical energy use under control. The smart ICT solutions could also be used in the rest of the society to reach environmental goals. Still, the Internet Sector itself has a huge responsibility to try to reach high annual electrical energy efficiency gains of \(\approx20\)% in data centers and networks. This seems to have been the case in the last decade. New technologies such as neuromorphic, reversible and superconducting computing as well as nanophotonics may help in this decade [12,13]. Several attributional life cycle assessments have shown that Internet’s share of TAGGHGS may have been stable 2015-2020 [13]. However, although recent literature is divided[14], the trends of rampant instructions/second and slowing improvements of switching energy are very clear [12,14]. Related cryptocurrency mining electrical energy demand is on the rise but not necessarily the related GHG supply [15]. Therefore power saving is a highly efficient strategy for GHG supply reduction in the Internet itself and beyond. In this work, the potential TAGGHGS avoidance of using ICT Solutions for energy saving, compared to low adoption of ICT Solutions, is explored. An algorithm for the estimation is established.

1.1. Objectives

The objective of this prediction study is to estimate the changes (GHG is proxy) to occur between 2019 and 2030 if traditional technologies are replaced with Information and Communication Technology (ICT) technologies. Internet’s scope according to [16,17] consists of the use stage of end-user consumer devices, network infrastructure and data centers as well as the production of hardware for all. The attributional LCA approach [16,17] may not be able to capture the actual GHG avoidance derived from the use of ICT solutions, as many of them have the ability to decrease the energy and material losses. Consequently, less energy and materials need to be produced and purchased by a final customer in order to consume the same quantity of product. A consequential LCA (CLCA) with a planetary system boundary is attempted for ICT solutions handprint.

1.2. Hypotheses

The hypothesis is that Internet’s GHG supply will increase according to the expected scenario as outlined by Andrae [16]. Moreover, Internet’s GHG supply is off-set already in 2020 by ICT Solutions and the handprint will be 6 times the footprint by 2030.

2. Materials and methods

The approach for estimating Internet’s direct GHG supply is established while the handprint potential of ICT solutions for TAGGHGS is less clear. Here, for the sake of modelling, the World is divided into seven sectors – Industry, Buildings, Transport, Travel, Agriculture, Waste and Land use. Then several ICT Solutions ability to reduce TAGGHGS in each sector is estimated. The approach is very much simplistic as there are highly granular Input-Output models [9,18] which describe the economic flows of different sectors in the society. Therefore, the coupling of IO and LCA can be applied to model indirect impacts of changes in product inputs and outputs in several economic sectors [19]. The coupling of IO and LCA can cover all economic sectors in a large geographical boundary. All assumptions made are available in the Supplementary Information.

2.1. Description of method for estimating Internet GHG supply

The approach for Internet direct GHG supply follows the one outlined in [16] expected scenario. Table 1 shows some global trends assumptions derived from [13,16]. Trends for TAGGHGS are followed closely [20].

Table 1. Global Electricity demand and average GHG intensity 2019 to 2030.
Year Total global Total global internet TWh renewable electricity GHG intensity
electricity demand (TWh) electricity demand (TWh) including Hydro (TWh) in Gt CO2e/TWh
2019 27050 1950 7042 0.000545
2020 27188 1988 7265 0.000543
2021 27826 1986 7494 0.000542
2022 28467 1987 7731 0.000540
2023 29117 1997 7975 0.000538
2024 29775 2015 8227 0.000536
2025 30446 2046 8487 0.000535
2026 31179 2139 8755 0.000533
2027 31968 2288 9032 0.000533
2028 32813 2493 9318 0.000532
2029 33751 2791 9612 0.000532
2030 34718 3218 9916 0.000533

2.2. Handprint – description of method for estimating GHG supply reductions and power savings by ICT Solutions

The overall methodological approach for estimating electricity demand and GHG supply handprint by the Internet in other Sub-Sectors (Industry, Transportation, Buildings, Agriculture, Land use and Waste) is described below. Land use leads to increased GHG supply if new plants (e.g. trees) are not planted which can absorb \(CO_2\). Waste (management) is a relevant Sub-Sector of its own, e.g. landfill, recycling, incineration etc.
2.2.1. Consequential handprint LCA

The functional unit of the CLCA is: global demand of electricity and TAGGHGS. Figure 1 shows the principle of provided functions replacing more inefficient ways.

ICT Solutions are replacing traditional solutions in the CLCA. Increased digitalization leads to increased production of ICT Solutions which substitute products, energy, materials and land use. When less travel and transport are used, also less fuel is produced. To compensate for “missing” fuel, more electricity will be produced. These effects contribute to the view of Internet driving deflation.

2.3. Estimation of total anthropogenic global GHG supply

The GHG supply from the Sub-Sector Agriculture in 2030 is \(\approx8.4\) Gt as shown in Table 2 below. Table 2 shows that Internet’s share of TAGGHGS without Internet handprint will be low \((\approx2\%)\). Moreover, without active Internet handprint, Industry’s GHG supply will increase almost 20% between 2020 and 2030. Land use and waste environmental impacts are more challenging to reduce with ICT Solutions, but they still contribute to TAGGHGS which could rise between 2020 and 2030 [13].

Despite economic growth and rebound effects, TAGGHGS could likely be significantly halted if existing and future ICT Solutions are used in other sectors (and Internet itself). Table 2 shows the present estimations by Sector for approximate TAGGHGS.

Table 2. Estimation of total anthropogenic global GHG supply (Gigatonnes) by Sector 2019-2030.
GHG Supply  from Global Sectors and ICT 2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
GHG\(_{i=\text{Industry}}\) 18.5 17.6 17.9 18.2 18.5 18.8 19.1 19.4 19.7 20.0 20.4 20.7
GHG\(_{i=\text{Building}}\) 13.7 13.4 13.6 13.9 14.2 14.5 14.7 15.0 15.3 15.6 15.9 16.2
GHG\(_{i=\text{Travel}}\) 4.2 3.0 3.2 3.3 3.5 3.7 3.8 4.0 4.1 4.3 4.4 4.6
GHG\(_{i=\text{Transport}}\) 6.2 4.4 4.6 4.9 5.1 5.3 5.6 5.8 6.0 6.3 6.5 6.7
GHG\(_{i=\text{Agriculture}}\) 6.7 6.8 7.0 7.1 7.3 7.4 7.6 7.7 7.9 8.1 8.3 8.4
GHG\(_{i=\text{Land use}}\) 5.4 5.4 5.4 5.5 5.5 5.6 5.6 5.6 5.7 5.7 5.8 5.5
GHG\(_{i=\text{Waste}}\) 1.7 1.7 1.8 1.8 1.8 1.9 1.9 1.9 2.0 2.0 2.1 2.1
GHG\(_{i=\text{Internet}}\) 1.06 1.08 1.08 1.07 1.07 1.08 1.09 1.14 1.22 1.33 1.48 1.71
GHG\(_{i=\text{Electricity}}\) Part of (embedded) all sectors
Total GHG  Supply \((\text{TAGGHGS}_{t})\) without  GHG\(_{i-\text{internet}}\) and internet handprint (Gt) 56.4 52.4 53.5 54.7 55.9 57.1 58.3 59.5 60.8 62.0 63.3 64.6

Equation (1) below shows TAGGHGS in year t:

\begin{equation} \label{e1} \text{TAGGHGS}_{t}=\sum_{i}\text{GHG}_{i,t}. \end{equation}
(1)
Equation (2) below shows the total global handprint of ICT Solution j in year t:
\begin{equation} \label{e2} \text{ICT}_{hp,t}=\sum_{j,i}\text{MVCV}_{j,i,t}\times F_{j,i,t} \times \text{GHG}_{i,t}. \end{equation}
(2)
where, \( \text{TAGGHGS}_{t}=\) Total anthropogenic GHG supply in year \(t\); GHG\(_{i,t}=\) Anthropogenic GHG supply from Sector type \(i\) in year \(t\); ICT\(_{hp,t} =\) ICT Solutions total global GHG handprint in year \(t\); \(j=\) ICT Solution type; \(i =\) Sector type; \(t=\) year; MVCV\(_{j,i,t}=\) Marginal Variable Change Vector of ICT Solution \(j\) in Sector \(i\) in year \(t\); F\(_{j,i,t}=\) Fraction of Sector \(i\) which is applicable to ICT Solution \(j\) in year \(t.\)

Here follows two examples which explain somewhat (2);

  • In 2030, F is \(0.1\) for Travel Sector for “Video/telemeeting, air” as it is assumed that \(10\)% of the Travel sector GHG supply are air travel GHG supply which can be reduced (50%, \(\text{MVCV}=0.5\)) via “Video/telemeeting, air” ICT solutions. The minimum values for this case are \(\text{F}=0.01\) and \(\text{MVCV}=0.05\).
  • In 2030, F is \(0.5\) for Building Sector for “Smart metering in Buildings” as it is assumed that \(50\)% of the Building sector GHG supply are electricity related GHG supply which can be reduced (10%, \(MVCV=0.1\)) via “Smart metering in Buildings” ICT solutions. The minimum values for this case are \(F=0.05\) and \(\text{MVCV}=0.01\). \(\text{MVCV}_{\text{Smart metering, Buildings,} 2020 =0.03}\) is reported in literature [21].

2.4. Division of GHG supply between electricity and other sources for Industry, Buildings, Travel and Transports

Table 2 shows that the GHG supply from Industry is \(\approx18\) Gt in 2020 with around 6 Gt related to electricity demand.

Table 3. Division of GHG supply between electricity and other sources between 2020 and 2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Industry  Electricity  GHG, Gt  CO2e 6.2 6.2 6.2 6.3 6.3 6.3 6.4 6.4 6.4 6.5 6.5 6.5
Industry  Electricity  Use, TWh 12000 11400 11500 11600 11700 11800 1190 12000 12100 12200 12300 12400
Industry  Others,  Gt CO2e 12.0 11.4 11.7 11.9 12.2 12.5 12.8 13.0 13.3 13.6 13.8 14.1
Buildings  Electricity  GHG, Gt  CO2e 6.7 7.1 7.2 7.4 7.6 7.8 7.9 8.1 8.3 8.5 8.7 8.3
Buildings  Electricity  Use, TWh 12300 13000 13370 13740 14110 14480 14850 15220 15590 15960 16330 16700
Buildings  Others,  Gt CO2e 7.0 6.3 6.4 6.5 6.6 6.7 6.8 6.9 7.0 7.1 7.2 7.3
Travel  Electricity  GHG, Gt  CO2e 0.2 0.2 0.3 0.3 0.4 0.5 0.5 0.6 0.6 0.7 0.7 0.8
Travel  Electricity Use, TWh 400 400 510 620 730 840 950 1060 1170 1280 1390 1500
Travel  Others,  Gt  CO2e 4.0 2.8 2.9 3.0 3.1 3.2 3.3 3.4 3.5 3.6 3.7 3.8
Transports  Electricity,  GHG, Gt,  CO2e 0.2 0.2 0.2 0.3 0.3 0.3 0.4 0.4 0.4 0.5 0.5 0.5
Transports  Power,  TWh 400 400 460 520 580 640 700 760 820 880 940 1000
Transports  Others, Gt CO2e 6.0 4.2 4.4 4.6 4.8 5 5.2 5.4 5.6 5.8 6 6.2
Internet  Electricity  GHG, Gt  CO2e 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.2 1.3 1.5 1.7
Internet  Electricity  Use, TWh 1950 1988 1986 1987 1997 2015 2046 2139 2288 2493 2791 3218
TOTAL  GLOBAL  CO2e from  human  energy  conversion  activities, Gt CO2e 43.7 39.5 40.4 41.4 42.4 43.3 44.3 45.4 46.4 47.5 48.7 49.9

Transport Electricity GHG and Travel Electricity GHG are both \(\approx6\)% of respective Sectors total GHG, while Land use Electricity GHG is excluded as it is assumed close to zero. However, with the anticipated electrification of vehicles, both Transport and Travel Electricity GHG will increase [17].

Moreover, hydrogen production for fuel cell vehicles – and indirectly ammonia production for internal combustion engines – will add to the electricity demand of the Transport and Travel Sectors [13]. Hydrogen production will also add electricity demand in the Industry sector (e.g. Steel supply chain), but at the same time the net GHG supply may be reduced in e.g. Steel production [13].

Ammonia has potential for Travel and Transport as a more or less non-ICT based GHG Supply reducer as ammonia can be used in converted internal combustion engines [22]. It is especially useful to know Industry Electricity Use and Building Electricity Use to understand the effectiveness of different electrical energy efficiency strategies such as Smart Metering. Internet also has some GHG supply from other sources than electricity, such as from diesel generators [23] but they have been excluded. Table 3 shows the split between electricity GHG and other sources for each Sector.

Table 3 may help understand where electrification, hydrogen and ammonia solutions make the most sense in energy related activities.

2.5. Estimation of ICT Solutions handprints

They key question addressed here is: How much GHG supply can smart ICT Solutions help avoid, \(ICT_{hp,t}\), in other sectors of society each year between \(t=2019\) and \(t=2030?\) Despite large uncertainties, quite likely more GHG supply can be avoided than the Internet emits itself i.e., ICT\(_{hp,t} > \text{GHG}_{i=\text{Internet,}t}\), perhaps already for \(t=2022\). Table 4 shows the addressed Fraction (F) of each Sector (i) and how much the ICT technology (j) can reduce (MVCV).

Table 5 roughly outlines how ICT\(_{hp,t}\) could increase year by year from 2019 to 2030 as estimated in the present study to reach (at the most) \(\approx11\text{Gt}\) in 2030. However, likely some reduction of TAGGHGS has already occurred historically due to ICT solutions and sensitivity checks are performed in Section 4. Table 5 shows mainly future potential to 2030. In Sections 2.5.1 to 2.5.9 the numbers in Table 5 are explained.

Table 6 outlines roughly how electricity handprints (TWh) could increase linearly year by year from 2020 to 2030 as estimated in the present study to reach \(\approx 8497\) TWh in 2030. As soon as 2022 more TWh can be cut by the Internet than its own usage.

2.5.1. Smart Grid
Table 7 shows three examples of where Smart Grid can achieve transformation. Smart Grid savings are firstly that 50% of all Buildings GHG supply are applicable for 10% reduction each using Smart Metering. This means that \(0.1\times 0.5\times 16.2\) Gt\( = 0.81\) Gt can be avoided in 2030. Smart Metering makes the users aware of the power consumption [21]. Smart Grid savings can also be obtained from “Power grid optimization” which may reduce 50% (power load balancing) of power use in each case it is introduced, but perhaps only 10% of global electricity GHG supply is applicable for optimization in 2030, i.e., \(0.5\times0.1\times34718\) TWh\(\times0.000533 \text{Gt}/\text{TWh} = 0.92\) Gt.

Further Smart Grid related savings by fewer losses than traditional grids [26] are possible from facilitation of renewable energy sources. This is assumed to reduce 10% of the power used in each applicable case which may be 20% of all globally used electricity, \(0.1\times 0.2\times 34718 \text{TWh} \times 0.000533 \text{Gt}/\text{TWh} = 0.37 \text{Gt}\). AI-driven battery management (including self-repair) is part of the renewable energy story for ICT handprint. All in all in 2030, \(0.81+0.92+0.37 = 2.1 \)Gt savings in 2030 from Smart Grid.

2.5.2. Smart Agriculture

Table 8 shows an example in which Smart Agriculture can achieve transformation. Smart Agriculture can be used to reduce TAGGHGS by e.g. more surveillance and less manual inspection. It is estimated that 10% of GHG supply of the entire Agriculture sector can be reduced, \(0.10\times8.43 \text{Gt} = 0.84 \text{Gt}\). AI is especially useful in Agriculture [28]. Autonomous variable herbicide spraying can save \(>50\%\) of liquid applied per hectare [29].

Table 4. Evolution matrix for F and MVCV for \(t=2019\) to 2030 for chosen \(i\) and \(j.\).
\# \(j\) 2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030 MVC \(v,j\)
1 0.005 0.05 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 10%
2 0.0001 0.001 0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 0.18 0.2 10%
3 0.00005 0.0005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 20%
4 0.00025 0.0025 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 10%
5 0.005 0.05 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 10%
6 0.005 0.05 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 10%
7 0.0005 0.005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 10%
8 0.0005 0.005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0. 1 20%
9 0.0025 0.025 0.05 0.1 0.15 0.20 0.25 0.3 0.35 0.4 0.45 0.5 20%
10 0.01 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 50%
11 0.01 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 50%
12 0.005 0.05 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 20%
13 0.001 0.01 0.02 0.04 0.06 0.08 0.10 0.12 0.14 0.16 0.18 0.2 50%
14 0.00005 0.0005 0.001 0.002 0.003 0.004 0.005 0.006 0.007 0.008 0.009 0.01 10%
15 0.0015 0.015 0.03 0.06 0.09 0.12 0.15 0.18 0.21 0.24 0.27 0.3 50%
16 0.0005 0.005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 20%
17 0.0025 0.025 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 20%
18 0.0005 0.005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 50%
19 0.005 0.05 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 10%
20 0.0005 0.005 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.1 10%
Autonomous intelligent tractors help avoid manual checks of the fields of cultivation 1
   Facilitating renewable energy sources 2
   Power grid optimization 3
   Smart metering in Buildings 4
   Car pools, leasing services, mobility-as-a-service 5
   Selling products as services, servitization 6
  Public travel suggestions 7
   Fleet car management 8
Route optimization in Leisure                9
Video/telemeetings, car 10
Video/telemeetings, air                     11
Office space                  12
    Teleworking, car                    13
  Hotels                   14
Office energy use                   15
Food store cooling energy                    16
Route optimization in Logistics                   17
Facilitate choosing train instead of car                    18
AI enabled optical sorting                   19
Forest monitoring with drones and sensors 20
Table 5. Estimation of GHG supply (Gigatonnes) reductions enabled by ICT Solutions 2019-2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Intelligent Grid  Handprint, Gt 0.00 0.01 0.17 0.35 0.54 0.74 0.94 1.15 1.37 1.60 1.85 2.11
Intelligent  Agriculture Handprint, Gt 0.00 0.03 0.07 0.14 0.22 0.30 0.38 0.46 0.55 0.65 0.74 0.84
Intelligent Service Handprint, Gt 0.01 0.10 0.21 0.43 0.66 0.90 1.15 1.40 1.67 1.95 2.23 2.53
Intelligent Travel  Handprint, Gt 0.00 0.02 0.04 0.09 0.14 0.19 0.25 0.31 0.38 0.45 0.52 0.60
Intelligent Work  Handprint, Gt 0.05 0.33 0.38 0.46 0.54 0.63 0.73 0.82 0.93 1.03 1.14 1.26
Intelligent  Buildings Handprint, Gt 0.01 0.11 0.23 0.47 0.72 0.98 1.25 1.53 1.82 2.12 2.43 2.75
Intelligent Transport Handprint, Gt 0.00 0.03 0.07 0.15 0.23 0.32 0.42 0.52 0.63 0.75 0.88 1.01
Intelligent Circularity Handprint, Gt 0.00 0.01 0.02 0.04 0.05 0.07 0.10 0.12 0.14 0.16 0.19 0.21
Intelligent Land  Use Handprint, Gt 0.00 0.00 0.01 0.01 0.02 0.02 0.03 0.03 0.04 0.05 0.06 0.5
TOTAL SMART  savings per year\(ICT_{hp}\) 0.08 0.65 1.20 2.14 3.12 4.16 5.23 6.35 7.53 8.75 10.03 11.37
Table 6. Estimation of electricity handprint (TWh) enabled by ICT Solutions 2019-2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Industry 1201 1150 1345 1559 1781 2014 2256 2510 2776 3058 3356 3376
Buildings 12 127 322 662 1020 1396 1789 2201 2630 3077 3542 4025
Travel 4.7 47 68 103 145 195 252 316 387 466 552 645
Transports 0.3 3.0 6.9 16 26 38 53 68 86 106 127 150
TOTAL savings TWh 1218 1327 1742 2339 2973 3643 4349 5095 5880 6706 7577 8497
Table 7. Smart Grid saving ICT Technologies.
t=2030 i Buildings Global electricity supply
Facilitating renewable energy sources 10% [24] 20% [24]
Power grid optimization 50% [24] 10% [24]
Smart metering in Buildings 10% [25] 50% [25]
Table 8. Smart Agriculture saving ICT technologies.
\(t=2030\) \(i\) Agriculture
\(j\) MVCV F
Autonomous intelligent tractors help avoid manual checks of the fields of cultivation 10% [27] 100%[27]
2.5.3. Smart Services

Smart Services is a rather wide concept for Smart ICT but mainly it is about virtualization and dematerialization. The link to servitization is very strong [29,30]. Table 9 shows two examples in which Smart Services can achieve transformation.

Table 9. Smart Services saving ICT Technologies.
\(t=2030\) \(i\) Travel Industry
\(j\) MVCV F F
Car pools, leasing services, mobility-as-a-service 10% [30] 100%[30]
Selling products as services, servitization 10% [31] 100% [31]

E-readers and audio books are examples of book-as-a-service (potentially) replacing physical books [8]. Global Change Mix Factors [32] may reveal to which degree this will materialize and then cause a rebound effect on F. Regarding financial products, digital solutions on blockchain may change the electricity demand of the financial systems [33]. Another example of smart service is e-commerce [34]. With the current rate of digitalization it seems likely that 100% of all Industry products could be sold as services in 2030. It is assumed that 10% of all travel transport and 10% of all Industry GHG supply can be avoided by selling products as services. All in all, \(0.1\times1\times4.6 \text{Gt} + 0.1\times1\times20.7 \text{Gt} = 2.5 \text{Gt}\).

2.5.4. Smart Travel

Smart Travel is about optimizing travel routes and vehicle sharing. It is assumed that three main mechanisms lead to savings; smart public travel, fleet car management and route optimization. Table 10 shows two examples in which Smart Travel solutions can achieve transformation.

Table 10. Smart Travel saving ICT Technologies.
\(t=2030\) \(i\) Travel
\(j\) MVCV F
Public travel suggestions 10% [35] 10% [35]
Fleet car management 20% [36] 10% [36]
Route optimization in Leisure 20% [37] 50% [37]

AI Taxi is an example of fleet car management [7]. The eighth and ninth handprints may be overestimated. Map route travel service handprints are already achieved. All in all, Smart Travel may reduce GHG supply by \((0.1\times0.1 + 0.2\times0.1 + 0.2\times0.5)\times4.6 \text{Gt} = 0.6 \text{Gt}.\)

2.5.5. Smart Work

Smart Work is about reducing business travel and commuting and the need for less hotel rooms and offices. In 2020 the airline passenger traffic shrunk 67% compared to 2019 and was reduced to 1999 levels [38]. No matter the reason, this suggests that digitalization tools could reach a very high implementation (high F) for video/telemeetings already in 2020 (Table 4). Table 11 shows five examples in which Smart Work solutions can achieve transformation.

Table 11. Smart Services saving ICT Technologies.
\( t=2030\) \(i\) Travel Buildings
\(j\) MVCV F F
Video/telemeetings, air 50% [39] 10% [39]
Video/telemeetings, car 50% [40] 10% [40]
Teleworking, car 50% [41] 20% [41]
Office space 20% [42] 100% [30]
Hotels 10% [43] 1% [43]

The tenth and eleventh services could be similar and double counted. A sensitivity analysis will include such issues. All in all, Smart Work may reduce GHG supply by \((0.5\times0.1 + 0.5\times0.1 + 0.5\times0.2)\times4.6 \text{Gt} + (0.2\times0.1 + 0.1\times0.01)\times16.2 \text{Gt} = 1.26 \text{Gt}\).

2.5.6. Smart Buildings

Smart ICT is facilitating automated heating, ventilation and air conditioning (HVAC) systems as well as light control. Via deep learning and cloud-based computing, ICT solutions autonomously optimizes existing HVAC control systems for lowest possible energy consumption. Table 12 shows two examples in which Smart Building solutions can achieve transformation.

Table 12. Smart Building saving ICT solutions.
\( t=2030\) \(i\) Buildings
\(j\) MVCV F
Office energy use 50% [39] 30% [44]
Food storage cooling energy 20% [40] 10% [45]

Office energy use here, and Smart metering in Section 2.5.1, may address somewhat similar flows. HVAC savings are however also related to thermal energy and not only electricity. All in all, Smart Building solutions may reduce GHG supply by \((0.5\times0.3 + 0.2\times0.1)\times16.2 \text{Gt} = 2.75 \text{Gt}.\)

2.5.7. Smart transports

Smart Transports is mainly about optimization of truck logistics and shifting transport from e.g. car to train [46]. Table 13 shows two examples in which Smart Transport solutions can achieve transformation.

Table 13. Smart Transport saving solutions.
\(t=2030\) \(i\) Transport
\(j\) MVCV F
Route optimization in Logistics 20% [47] 50% [47]
Facilitate choosing train instead of truck 50% [48] 10% [48]

All in all Smart Transport solutions may reduce GHG supply by \((0.2\times0.5 + 0.5\times0.1)\times4.5 \text{Gt} = 0.68 \text{Gt}\). Arguably F for ICT solution (Table 13, last row) may be lower than 10%. Another example of a Smart Transport solution is wireless vehicle-vehicle communication with Cooperative Adaptive Cruise Control which saves truck fuel [49].

2.5.8. Smart Circularity
Around 99% of everything that we buy becomes waste after 6 months. Some 2 billion tonnes of waste (garbage) is generated annually of which \(\approx2.5%\) is e-waste. Total Material Consumption per capita is also increasing. The effective material flow is much higher than the conventional weight flow. The so called Total Material Requirements per kg metal is increasing, i.e., the ore grades are diminishing. Ore grades (e.g. copper) is gradually decreasing 2.5% per annum, while production and energy consumption (and GHG supply) from mining is increasing [50]. Using AI software for optimization is likely a more fruitful route than new waste management technologies. In product design, AI may predict product design variables for GHG supply reduction and customer relevance. AI can help the Waste sector by Smart logistics (improvements in route planning), mobile collection of e-waste on demand [51], and via intelligent optical sorting machines.

Here the example of intelligent Optical sorting machines is used to exemplify how much the GHG supply from the Waste Management Sector can be reduced. AI helps capturing data from optical sorters from which machinery can learn and “make” decisions that optimize sorting [52]. AI-Powered Robot Picking is another example of Intelligent Circularity. Smart Circularity can be used in Waste Management to avoid GHG supply. Waste can be identified for its proper handling. It is assumed that in each case Smart Circularity is used 10% of the GHG supply can be avoided and that all waste related GHG supply can be addressed by intelligent sorting in 2030, i.e., \(0.1\times1\times2.1 \text{Gt} = 0.21 \text{Gt}\). One could argue that selling services instead of products is also smart circularity [31]. Nevertheless, Industry related material savings (servitization) is addressed by Smart Services in Section 2.5.3.

Route planning of garbage trucks is addressed by Smart Transport in Section 2.5.7. Table 14 shows an example in which a Smart waste management solution can achieve transformation.

Table 14. Smart Waste management solutions.
\( t=2030\) \(i\) Transport
\(j\) MVCV F
AI enabled optical sorting 10% [52] 100% [52]

All in all Smart Circularity solutions may reduce GHG supply by \(0.1\times1\times2.1\text{ Gt} = 0.21 \text{Gt}\).

2.5.9. Smart land use

AI can be used for managing sustainable land use [53]. Smart Forestry (IoT monitoring) can be used to reduce GHG supply caused by illegal tree cutting [54,55]. Table 15 shows an example in which a Smart land use solution can achieve transformation.

Table 15. Smart Land use solutions.
\(t=2030\) \(i\) Transport
\(j\) MVCV F
Forest monitoring with drones and sensors 10% [56] 10% [56]

All in all Smart Land use solutions may reduce GHG supply by \(0.1\times0.1\times5.8 \text{Gt} = 0.058 \text{Gt}\).

2.6. Total Internet GHG supply handprint

All in all, Internet’s handprint will be 11.37 Gt in 2030 using assumed (very high) values for MVCV and F. However, when introducing smaller minimum values for MVCV and F, the handprint will be much smaller, but still safely higher than Internet’s footprint.

2.7. Estimation of global GHG supply with and without ICT handprint and Share of electric power GHG of total global GHG

It is relevant to estimate to which degree the savings from ICT Solutions of Table 5 can reduce TAGGHGS (Table 2). In Table 16 is shown how TAGGHGS is slowed down. In 2020 the TAGGHGS is 0.2% (57.4 instead of 57.5) less thanks to ICT. In 2030 TAGGHGS could be around 17% (54.9 instead of 66.3) lower than business as usual. Table 16 shows the estimation of global GHG supply with and without ICT handprint and share of electric power GHG supply.

2.8. Handprint in each Sector

In this section the savings made possible by Smart Grid, Smart Travel, Smart Buildings etc. are allocated to each societal sector (Table 17). For example the savings by Smart Work are allocated to Travel if the Smart Work savings are travel related, and savings by Smart Grid are allocated to Buildings if the Smart Grid savings are Buildings related.

2.9. Share of each sectors GHG supply that can be cut by ICT Solutions

This section discusses the share of each sectors’ GHG supply which could be cut year by year from 2019 to 2030. The shares are obtained by dividing the Handprint in the Sector (Table 17) with the Sector (Table 2). Table 18 the shares of each sectors GHG supply that can be cut over time are shown.

Table 16. Estimation of global GHG supply (Gigatonnes) with and without ICT handprint and Share of electric power GHG, 2019-2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
TAGGHGS (Gt)  without  ICT  enabling 57.5 53.4 54.6 55.8 57.0 58.2 59.4 60.7 62.0 63.3 64.8 66.3
TAGGHGS (Gt)  thanks  to   ICT  enabling 57.4 52.8 53.4 53.7 53.9 54.1 54.2 54.3 54.5 54.6 54.7 54.9
Global electric  power related  GHG supply 14.7 14.8 15.1 15.4 15.7 16.0 16.3 16.6 17.0 17.5 18.0 18.5
Table 17. Estimation of global GHG supply (Gigatonnes) with and without ICT handprint and Share of electric power GHG, 2019-2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Handprint  in Industry 0.01 0.09 0.28 0.58 0.88 1.20 1.53 1.86 2.22 2.58 2.96 3.37
Handprint  in Buildings 0.01 0.13 0.33 0.67 1.03 1.39 1.78 2.17 2.58 3.01 3.45 3.90
Handprint  in Travel 0.05 0.35 0.42 0.55 0.70 0.85 1.01 1.18 1.36 1.56 1.76 1.98
Handprint  in Transports 0.00 0.03 0.07 0.15 0.23 0.32 0.42 0.52 0.63 0.75 0.88 1.01
Handprint  in Agriculture 0.00 0.03 0.07 0.14 0.22 0.30 0.38 0.46 0.55 0.65 0.74 0.84
Handprint  in Waste 0.00 0.01 0.02 0.04 0.05 0.07 0.10 0.12 0.14 0.16 0.19 0.21
Handprint  in Land use 0.00 0.00 0.01 0.01 0.02 0.02 0.03 0.03 0.04 0.05 0.05 0.06
TOTAL Internet  handprint per year 0.08 0.65 1.20 2.14 3.12 4.16 5.23 6.35 7.53 8.75 10.03 11.37
Table 18. Shares of each sectors GHG supply that can be cut by ICT Solutions between 2019 and 2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Industry 0% 1% 2% 3% 5% 7% 9% 10% 12% 14% 16% 17%
Buildings 0% 1% 2% 5% 7% 10% 12% 14% 17% 19% 22% 24%
Travel 1% 12% 13% 17% 20% 23% 27% 30% 33% 36% 40% 43%
Transports 0% 1% 2% 3% 5% 6% 8% 9% 11% 12% 14% 15%
Agriculture 0% 1% 1% 2% 3% 4% 5% 6% 7% 8% 9% 10%
Land use 0% 0% 0% 0% 0% 0% 1% 1% 1% 1% 1% 1%
Waste 0% 1% 1% 2% 3% 4% 5% 6% 7% 8% 9% 10%

2.10. Effect of Internet handprint on global GHG supply

In Table 19 the handprint of ICT solutions on TAGGHGS is summarized. In 2030 at the most \(\approx17\)% of TAGGHGS (11.37 Gt of 66.3 Gt) can be reduced. In Section 4 it is elaborated with sensitivity analysis what speaks for 11.37 Gt and what speaks against.

\begin{table}[H] \begin{center}
Table 19. Effect of Internet handprint on global GHG supply from 2019 to 2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Internet  infrastructure GHG Supply 1.06 1.08 1.08 1.07 1.07 1.08 1.09 1.14 1.22 1.33 1.48 1.71
Internet’s handprint 0.08 0.65 1.20 2.14 3.12 4.16 5.23 6.35 7.53 8.75 10.03 11.37
Total global GHG supply without  Internet’s handprint 57.5 53.4 54.6 55.8 57.0 58.2 59.4 60.7 62.0 63.3 61.8 66.3
Total global GHG supply with  Internet’s handprint 57.4 52.8 53.7 53.9 54.1 54.2 54.3 54.5 54.6 54.6 54.7 57.9
Table 20. Specific ICT Solutions shares of total handprint in 2030.
Effect pathway Gt CO2e Share of handprint  in 2030
SMART GRID
Smart metering in Buildings less energy use 0.81 7.1%
Facilitating renewable energy sources less energy use 0.37 3.3%
Power grid optimization less energy use 0.93 8.2%
SMART AGRICULTURE
Autonomous intelligent tractors help avoid manual checks of the fields of cultivation. less material use and land use 0.84 7.4%
SMART SERVICES
Car pools, leasing services, mobility-as-a-service Fuel saving 0.46 4.0%
Products sold as Services Material efficiency 2.07 18.2%
SMART TRAVEL
Public travel suggestions Information availability 0.05 0.4%
Fleet car management Fuel saving 0.05 0.4%
Route optimization in Leisure Fuel saving 0.8%
SMART WORK
Video/telemeetings, air Marginal effect on aviation 0.23 2.0%
Video/telemeetings, car Fuel saving 0.23 2.0%
Teleworking, car Fuel saving 0.46 4.0%
Office space Energy saving 0.32 2.8%
Hotels Energy saving 0.02 0.1%
SMART BUILDINGS
Office energy use Thermal energy saving 2.43 21.4%
Food storage cooling energy Electric power saving 0.32 2.8%
SMART TRANSPORT
Route optimization in Logistics Fuel saving 0.67 5.9%
Facilitate choosing train instead of car Information availability 0.34 3.0%
SMART CIRCULARITY
AI enabled optical sorting Material recycling 0.21 1.8%
SMART LAND USE
Forest monitoring with drones and sensors Forestation 0.06 0.05%
TOTAL 11.37 100%
\caption{Specific ICT Solutions shares of total handprint in 2030.}\label{t20} \end{center} \end{table}

2.11. Specific ICT Solution share of total handprint in 2030

Here specific ICT Solutions are listed in Table 20 and their share of total handprint. The largest reduction amount, 2.43 Gt and 21%, can be achieved from “Office energy use” and “Selling products as services, servitization” 2.07 Gt and 18%.

2.12. Individual products handprint

In the present decade there will be an unprecedented growth of generated data shown in Table 21 [16]. This can be used to estimate Internet’s handprint per Byte. Individual product’s services handprints can then be estimated if their bandwidths are known. Evidently, applicable handprint services need to have specific pathways for creating handprints.

Table 21. Effect of Internet handprint on global GHG supply from 2019 to 2030.
2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030
Mobile  data  traffic  (EB/year) 354 549 829 1228 1825 2718 4057 6175 9290 13904 20767 31008
Fixed  data  traffic  (EB/year) 1964 2444 3054 3829 4817 6079 7693 9763 12420 15836 20234 25901
Within  and  between  Data  centers, (EB/year) 13004 16926 22011 28606 37120 48094 62208 80207 103278 132745 170229 217689
Global  Data  Center  IP Traffic, (EB/year) 15322 19919 25895 33663 43762 46890 73957 96145 124988 162484 211230 274599

3. Results

The order of magnitude of the GHG Supply handprint is reasonable. Figure 2 is a graphical representation of the present article. It seems plausible that Internet’s handprint will be higher than its footprint. However, 11.37 Gt may be heavily overestimated.

4. Discussion

What would overthrow the results in the present research? Are there any new developments since 2015 which would falsify magnificent Internet handprints? What is only theory and what are the facts? Is here Internet’s handprint massively exaggerated several times? One obvious issue is to which extent the digitalization has already been achieved, meaning that F’s max value for t=2030 is already achieved. 2020 meant a huge leap forward in this respect for some ICT Solutions such as “Video/telemeetings, air” and “Video/telemeetings, car”. Anyway the reduction of GHG supply observed in 2020 is not really caused by certain ICT solutions. However, they made e.g. working from home possible. Here the view is taken that ICT solutions number 10 and 11 in Table 4 are tested big-scale making the assumed 50% (F=0.5) cut of applicable Transport and Travel GHG Supply between 2019 and 2020 possible.

On the other hand it is not argued that Internet’s handprint will lead to absolute smaller TAGGHGS, but rather a slow-down of the increase of TAGGHGS. 2020 will show this fact e.g. with fewer travels and more virtual meetings.

2020 showed that digital ICT technologies can be widely adopted very quickly. Smart Buildings is a very important area for ICT solution offsetting of TAGGHGS as Buildings use much energy. However, it may be argued that “Smart Metering in Buildings” and “Smart Buildings office energy use reduction” is equal. Also, old buildings may not be able to reduce energy use as much as newly constructed ones. These limitations are considered to be included in the sensitivity analysis in which F and MVCV are reduced 10 times. \(\text{MVCV}_{\text{Smart metering, Buildings,}2020}=0.\)03 [20] measurement is a good indication for the reasonableness of \(\text{MVCV}_{\text{Smart metering,Buildings,}2030}=0.1\).

Likewise, certain Smart Travel ICT Solutions may be similar to Smart Services for Travel. Regarding Smart Work ICT Solutions, “telemeeting” and “teleworking” seem identical with regards to Travel handprint.

If the biggest one – teleworking – is churned the total ICT potential is reduced by 0.48 Gt in 2030. Anyway, for Smart Work the anticipated 2030 savings may already have happened in 2020 due to the global macro changes in 2020. Temporary or permanent decline to a new baseline of airline and automotive travel and transport are the most obvious observations in 2020.

The effectiveness of AI to achieve savings depends greatly on sufficient data and the data scientists and engineers developing the AI software. AI has successfully been employed for forecasting the volume of waste which will be generated. This facilitate proper planning of landfill sites, recycling units, development as well as operation of garbage collection infrastructure. AI can cope especially well with historical data which are of nonlinear nature. Still several indications of savings exist.

ICT Product handprints

What is the link to ICT product related handprints? Dividing the total handprint in Table 5 (11.37 Gt) with the Global Data Center IP Traffic in Table 21 (268 ZettaByte) gives e.g. 0.039 kg CO2e/GigaByte for 2030. However, this intensity is quite rough but may be tested together with specific GigaByte/s bandwidth data.

The right performance for the right application

What performance is good enough for a certain application? Such questions are valid e.g. for Travel Electricity Use (Table 3) where Na-ion batteries (90-115 Wh/kg) could be enough for certain electric vehicles instead of Li-ion (100-265 Wh/kg) [57,58].

The global material efficiency/waste problem seems not to be solved effectively by improved local waste management (e.g. collection). Perhaps an AI optimization of total global supply chains – which targets waste minimization in production and Total Material Consumption/capita is more effective. Optimizing and predicting the whole nonlinear global societal system with Internet as a driver – markets, Input-Output, GHG supply, resources, costs, jobs, waste – is a daunting task which theoretically could better be managed with AI and humans instead of humans alone.

Sensitivity analyses

Without sensitivity checks by 2030 the handprint/footprint ratio will be around 7 (11.37/1.71). Using Monte Carlo simulation and maximum and minimum values of F, MVCV etc. gives an uncertainty spread such that GHGi=Internet,t=2020 = 1.17 Gt (Min 1.07 Gt Max 1.29 Gt) and ICThp,2020 = 0.35 Gt (Min 0.23 Gt Max 0.48 Gt). All assumptions are found in the Supplementary Information. Videomeetings represent almos t 50% of Internet’s handprint in 2020 but just 4% in 2030 where instead Office energy use and Servitization of products dominate.

Using maximum and minimum values of F, MVCV etc. (see Supplementary Information) gives an uncertainty spread such that GHG\(_{i=\text{Internet,}t=2030} = 1.53\) Gt (Min 1.28 Gt Max 1.8 Gt) and ICT\(_{hp,2030} = 6.32\) Gt (Min 4.41 Gt Max 8.52 Gt). Compared to the original mean value (11.37 Gt), including the spread of input values reduces the mean value of ICT\(_hp,2030\) substantially due to ten times lower minimum values of F and MVCV. In 2020 the GHG supply by the Internet is some 70% higher than Internet’s handprint. Hence, the GHG supply by the Internet is not off-set already in 2020 by ICT Solutions. Nevertheless, the handprint/footprint ratio will be around 4 (6.32/1.53) by 2030. Thus the handprint hypotheses in Section 1.2 are falsified.

5. Next steps

The present research confirms that the largest handprints from the Internet in 2030 will be in Buildings and Industry. Still, individual nations and service providers would like to estimate better specific handprints. Moreover, the measurable entities in the system should be identified more carefully for individual ICT Solutions such those related to 5G [59]. Additionally, the standardization of the handprint calculation for electronic products should be attempted.

Conflicts of Interest

The author declares no conflict of interest.

References:

  • Lange, S., Pohl, J., & Santarius, T. (2020). Digitalization and energy consumption. Does ICT reduce energy demand?. Ecological Economics, 176, 106760. [Google Scholor]
  • Mir, U. (2020). Bitcoin and Its Energy Usage: Existing Approaches, Important Opinions, Current Trends, and Future Challenges. KSII Transactions on Internet and Information Systems (TIIS), 14(8), 3243-3256. [Google Scholor]
  • Liu, Y., Wei, X., Xiao, J., Liu, Z., Xu, Y., & Tian, Y. (2020). Energy consumption and emission mitigation prediction based on data center traffic and PUE for global data centers. Global Energy Interconnection, 3(3), 272-282. [Google Scholor]
  • Stobbe, L., Nissen, N. F., Druschke, J., Zedel, H., Richter, N., & Lang, K. D. (2019). Methodology for Modeling the Energy and Material Footprint of Future Telecommunication Networks. In EcoDesign and Sustainability II (pp. 223-238). Springer, Singapore. [Google Scholor]
  • Grönman, K., Pajula, T., Sillman, J., Leino, M., Vatanen, S., Kasurinen, H., & Soukka, R. (2019). Carbon handprint–An approach to assess the positive climate impacts of products demonstrated via renewable diesel case. Journal of Cleaner Production, 206, 1059-1072. [Google Scholor]
  • Ulucak, R., & Khan, S. U. D. (2020). Does information and communication technology affect CO2 mitigation under the pathway of sustainable development during the mode of globalization?. Sustainable Development, 28(4), 857-867. [Google Scholor]
  • Zhang, X., Shinozuka, M., Tanaka, Y., Kanamori, Y., & Masui, T. (2021). Forecast of Future Impacts of Using ICT Services on GHG Emissions Reduction and GDP Growth in Japan. In EcoDesign and Sustainability II(pp. 207-222). Springer, Singapore. [Google Scholor]
  • Amasawa, E., Ihara, T., & Hanaki, K. (2018). Role of e-reader adoption in life cycle greenhouse gas emissions of book reading activities. The International Journal of Life Cycle Assessment, 23(9), 1874-1887. [Google Scholor]
  • Zhou, X., Zhou, D., Wang, Q., & Su, B. (2019). How information and communication technology drives carbon emissions: a sector-level analysis for China. Energy Economics, 81, 380-392. [Google Scholor]
  • Bieser, J. C., & Hilty, L. M. (2018). Assessing indirect environmental effects of information and communication technology (ICT): A systematic literature review. Sustainability, 10(8), 2662. [Google Scholor]
  • Bieser, J., & Hilty, L. (2018). Indirect Effects of the Digital Transformation on Environmental Sustainability: Methodological Challenges in Assessing the Greenhouse Gas Abatement Potential of ICT. EPiC Series in Computing, (52), 68-81. [Google Scholor]
  • Andrae, A. S. G. (2019). Prediction Studies of Electricity Use of Global Computing in 2030. International Journal of Science and Engineering Investigations, 8, 27-33. [Google Scholor]
  • Andrae, A. S. G. (2020). Hypotheses for Primary Energy Use, Electricity Use and CO2 Emissions of Global Computing and Its Shares of the Total Between 2020 and 2030. WSEAS Transactions of Power Systems; 15: 50-59. [Google Scholor]
  • Delbeke, J., Haesler, S., & Prodanov, D. (2020). Failure Modes of Implanted Neural Interfaces. In Neural Interface Engineering (pp. 123-172). Springer, Cham. [Google Scholor]
  • Coindesk. (2020). [cited 25 January 2021].

    Available from: https://www.coindesk.com/the-last-word-on-bitcoins-energy-consumption.

  • Andrae, A .S. G. (2020) New perspectives on internet electricity use in 2030. Engineering and Applied Science Letter, 3(2), 19-31. [Google Scholor]
  • Andrae, A. S., & Edler, T. (2015). On global electricity usage of communication technology: trends to 2030. Challenges, 6(1), 117-157. [Google Scholor]
  • Sandberg, I. W. (1973). A nonlinear input-output model of a multisectored economy. Econometrica: Journal of the Econometric Society, 1167-1182. [Google Scholor]
  • Le Luu, Q., Longo, S., Cellura, M., Riva Sanseverino, E., Cusenza, M. A., Franzitta, V. (2020). A Conceptual Review on Using Consequential Life Cycle Assessment Methodology for the Energy Sector. Energies, 13(12), 3076. [Google Scholor]
  • Netherlands Environmental Assessment Agency (2020). [cited 25 January 2021] Available from:

    http://www.pbl.nl/en/publications/trends-in-global-co2-and-total-greenhouse-gas-emissions-2019-report

  • Behavioural Insights Team (2020) [cited 17 March 2021] Available from:

    https://www.bi.team/wp-content/uploads/2020/12/Guidance-on-conducting-energy-consumption-analysis.pdf

  • Kobayashi, H., Hayakawa, A., Somarathne, K. K. A., & Okafor, E. C. (2019). Science and technology of ammonia combustion. Proceedings of the Combustion Institute, 37(1), 109-133. [Google Scholor]
  • Andrae, A. S. G. (2015). Comparative screening life cycle impact assessment of renewable and fossil power supply for a radio base station site. International Journal of Green Technology, 1, 21-34. [Google Scholor]
  • Feinberg, E. (2012). Smart grid optimization. Energy, 2012. [cited 25 January 2021] Available from:

    https://www.iaria.org/conferences2012/filesICNS12/SmartGridOptimization-Rev1.pdf

  • Fischer, C. (2008). Feedback on household electricity consumption: a tool for saving energy?. Energy efficiency, 1(1), 79-104. [Google Scholor]
  • Bose, B. K. (2017). Artificial intelligence techniques in smart grid and renewable energy systems-Some example applications. Proceedings of the IEEE, 105(11), 2262-2273. [Google Scholor]
  • Berenstein, R., Shahar, O. B., Shapiro, A., & Edan, Y. (2010). Grape clusters and foliage detection algorithms for autonomous selective vineyard sprayer. Intelligent Service Robotics, 3(4), 233-243. [Google Scholor]
  • Magomadov, V. S. (2019, December). Deep learning and its role in smart agriculture. In Journal of Physics: Conference Series (Vol. 1399, No. 4, p. 044109). IOP Publishing. [Google Scholor]
  • Pérez-Ruiz, M., Gonzalez-de-Santos, P., Ribeiro, A., Fernández-Quintanilla, C., Peruzzi, A., Vieri, M., & Agüera, J. (2015). Highlights and preliminary results for autonomous crop protection. Computers and Electronics in Agriculture, 110, 150-161. [Google Scholor]
  • Fernando, C., Soo, V. K., & Doolan, M. (2020). Life Cycle Assessment for Servitization: A Case Study on Current Mobility Services. Procedia Manufacturing, 43, 72-79. [Google Scholor]
  • ITU-T (2021). L.1024 (01/21) The potential impact of selling services instead of equipment on waste creation and the environment – Effects on global information and communication technology [cited 17 March 2021] Available from:

    https://www.itu.int/rec/T-REC-L.1024-202101-I

  • Andrae, A. S. (2015). Method based on market changes for improvement of comparative attributional life cycle assessments. The International Journal of Life Cycle Assessment, 20(2), 263-275. [Google Scholor]
  • Krause, M. J., Tolaymat, T. (2018). Quantification of energy and carbon costs for mining cryptocurrencies. Nature Sustainability, 1(11), 711-718. [Google Scholor]
  • Hischier, R. (2018). Car vs. Packaging-A First, Simple (Environmental) Sustainability Assessment of Our Changing Shopping Behaviour. Sustainability, 10(9), 3061. [Google Scholor]
  • Ivanov, S. H., & Webster, C. (2017). Adoption of robots, artificial intelligence and service automation by travel, tourism and hospitality companies–a cost-benefit analysis. Artificial Intelligence and Service Automation by Travel, Tourism and Hospitality Companies–A Cost-Benefit Analysis. [Google Scholor]
  • Hu, J., Morais, H., Sousa, T., & Lind, M. (2016). Electric vehicle fleet management in smart grids: A review of services, optimization and control aspects. Renewable and Sustainable Energy Reviews, 56, 1207-1226. [Google Scholor]
  • James, J. Q., Yu, W., & Gu, J. (2019). Online vehicle routing with neural combinatorial optimization and deep reinforcement learning. IEEE Transactions on Intelligent Transportation Systems, 20(10), 3806-3817. [Google Scholor]
  • Businesswire. (2020). [cited 25 January 2021].

    Available from: https://www.businesswire.com/news/home/20201228005254/en/

  • Andrae, A. S., & Edler, T. (2015). On global electricity usage of communication technology: trends to 2030. Challenges, 6(1), 117-157. [Google Scholor]
  • Masino, C., Rubinstein, E., Lem, L., Purdy, B., & Rossos, P. G. (2010). The impact of telemedicine on greenhouse gas emissions at an academic health science center in Canada. Telemedicine and e-Health, 16(9), 973-976. [Google Scholor]
  • O’Keefe, P., Caulfield, B., Brazil, W., White, P. (2016). The impacts of telecommuting in Dublin. Research in Transportation Economics, 57, 13-20. [Google Scholor]
  • Lupton, P., & Haynes, B. (2000). Teleworking-the perception-reality gap. Facilities. [Google Scholor]
  • Messenger, J. C. (Ed.). (2019). Telework in the 21st century: An evolutionary perspective. Edward Elgar Publishing. [Google Scholor]
  • Serra, J., Pubill, D., Antonopoulos, A., & Verikoukis, C. (2014). Smart HVAC control in IoT: Energy consumption minimization with user comfort constraints. The Scientific World Journal, 2014. [Google Scholor]
  • Nugroho, A., Setiadi, R. N., & Umar, L. (2020, October). Smart Box Development for Food Storage with PCI-Based Temperature PID Control. In Journal of Physics: Conference Series (Vol. 1655, No. 1, p. 012017). IOP Publishing. [Google Scholor]
  • Abduljabbar, R., Dia, H., Liyanage, S., & Bagloee, S. A. (2019). Applications of artificial intelligence in transport: An overview. Sustainability, 11(1), 189. [Google Scholor]
  • Ebendt, R., Sohr, A., Touko Tcheumadjeu, L. C., & Wagner, P. (2010). Utilizing historical and current travel times based on floating car data for management of an express truck fleet. http://hdl.handle.net/10195/37753 [Google Scholor]
  • Gössling, S. (2018). ICT and transport behavior: A conceptual review. International journal of sustainable transportation, 12(3), 153-164. [Google Scholor]
  • McAuliffe, B., Lammert, M., Lu, X. Y., Shladover, S., Surcel, M. D., & Kailas, A. (2018). Influences on energy savings of heavy trucks using cooperative adaptive cruise control(No. 2018-01-1181). SAE Technical Paper. [Google Scholor]
  • Calvo, G., Mudd, G., Valero, A., & Valero, A. (2016). Decreasing ore grades in global metallic mining: a theoretical issue or a global reality?. Resources, 5(4), 36. [Google Scholor]
  • Nowakowski, P., Szwarc, K., & Boryczka, U. (2018). Vehicle route planning in e-waste mobile collection on demand supported by artificial intelligence algorithms. Transportation Research Part D: Transport and Environment, 63, 1-22. [Google Scholor]
  • Harvard Business School. (2020). [cited 25 January 2021] Available from:

    https://digital.hbs.edu/platform-digit/submission/tomra-potatoes-to-the-right-rocks-to-the-left/

  • Liu, Y., Tang, W., He, J., Liu, Y., Ai, T., & Liu, D. (2015). A land-use spatial optimization model based on genetic optimization and game theory. Computers, Environment and Urban Systems, 49, 1-14. [Google Scholor]
  • Zou, W., Jing, W., Chen, G., Lu, Y., & Song, H. (2019). A survey of big data analytics for smart forestry. IEEE Access, 7, 46621-46636. [Google Scholor]
  • Lakhwani, K., Gianey, H., Agarwal, N., & Gupta, S. (2019). Development of IoT for smart agriculture a review. In Emerging trends in expert applications and security (pp. 425-432). Springer, Singapore. [Google Scholor]
  • Basse, R. M., Charif, O., & Bodis, K. (2016). Spatial and temporal dimensions of land use change in cross border region of Luxembourg. Development of a hybrid approach integrating GIS, cellular automata and decision learning tree models. Applied Geography, 67, 94-108. [Google Scholor]
  • Palomares, V., Serras, P., Villaluenga, I., Hueso, K. B., Carretero-González, J., & Rojo, T. (2012). Na-ion batteries, recent advances and present challenges to become low cost energy storage systems. Energy & Environmental Science, 5(3), 5884-5901. [Google Scholor]
  • Mogensen, R., Brandell, D., & Younesi, R. (2016). Solubility of the solid electrolyte interphase (SEI) in sodium ion batteries. ACS Energy Letters, 1(6), 1173-1178. [Google Scholor]
  • Huawei (2020). Green 5G: Building a sustainable world. [cited 25 January 2021] Available from: https://www- file.huawei.com/ /media/corp2020/pdf/public-policy/green 5g building a sustainable world v1.pdf?la=en [Google Scholor]