Skip to main content
ACS AuthorChoice logoLink to ACS AuthorChoice
. 2024 Jan 2;58(2):971–990. doi: 10.1021/acs.est.3c03088

Mass-Balance-Consistent Geological Stock Accounting: A New Approach toward Sustainable Management of Mineral Resources

Mark U Simoni †,‡,*, Johannes A Drielsma §, Magnus Ericsson , Andrew G Gunn , Sigurd Heiberg #, Tom A Heldal , Nedal T Nassar , Evi Petavratzi , Daniel B Müller
PMCID: PMC10795188  PMID: 38166114

Abstract

graphic file with name es3c03088_0006.jpg

Global resource extraction raises concerns about environmental pressures and the security of mineral supply. Strategies to address these concerns depend on robust information on natural resource endowments, and on suitable methods to monitor and model their changes over time. However, current mineral resources and reserves reporting and accounting workflows are poorly suited for addressing mineral depletion or answering questions about the long-term sustainable supply. Our integrative review finds that the lack of a robust theoretical concept and framework for mass-balance (MB)-consistent geological stock accounting hinders systematic industry-government data integration, resource governance, and strategy development. We evaluate the existing literature on geological stock accounting, identify shortcomings of current monitoring of mine production, and outline a conceptual framework for MB-consistent system integration based on material flow analysis (MFA). Our synthesis shows that recent developments in Earth observation, geoinformation management, and sustainability reporting act as catalysts that make MB-consistent geological stock accounting increasingly feasible. We propose first steps for its implementation and anticipate that our perspective as “resource realists” will facilitate the integration of geological and anthropogenic material systems, help secure future mineral supply, and support the global sustainability transition.

Keywords: mineral depletion, mineral resources, material flow analysis (MFA), sustainability reporting, United Nations Framework Classification for Resources (UNFC), digital economy, geoinformation management

1. Introduction

Are we running out of mineral resources? Resource optimists embrace the economic perspective of Smith,1 and others25 in arguing that markets are self-regulating, and that global mineral depletion is a nonissue6,7 for society. Indeed, while mineral extraction accelerated over the last century,8 there is little historical indication that physical depletion of individual deposits has impacted the global availability of minerals: inflation-corrected commodity prices remained stable over the past century,4,911 and commodity time-price trends indicate that mineral products became more affordable.12

Resource pessimists follow Malthus,13 Jevons,14 and Hubbert,15 in arguing that unconstrained mining will deplete Earth’s finite nonrenewable mineral stocks to the point of constraining future growth. The Club of Rome’s report “Limits to Growth”16 intensified the discussion about finite stocks.1719 While its predictions of physical scarcity have not materialized,20 the depletion of deposits indeed accelerated together with extraction rates,21,22 ore grades in production declined,23,24 and environmental impacts and resource conflicts multiplied and intensified.22,2529 Global trends continue to raise broad concerns about future raw material availability and sustainability.21,3033

The mineral depletion and sustainability debate continues unabated, and while neither the optimistic nor the pessimistic perspective is inherently contradictory or incorrect, neither has offered a unifying solution to reconcile the positions.4,3439 Notably, both resource optimists and resource pessimists base their claims on the same national and global mineral production statistics and estimates for mineral resources and reserves.4042 Whether these data are at all suitable for quantifying long-term mineral depletion is questioned by recent studies.11,4346 Various authors highlight significant uncertainties regarding conceptual methods for estimation, classification, and spatial aggregation of mineral resources and reserves across all data sources, particularly for critical raw materials.4751 Moreover, the general lack of systematic and standardized granular mine-site-level “bottom-up” information is a key concern for comparing, aggregating, and monitoring mineral resources and mineral reserves.42,51,52 Poor data availability also hampers environmental, social, and governance (ESG) risk assessments,53,54 sustainability analysis,55,56 and raw materials scenario modeling.47,53,54 Notwithstanding, there are few recommendations on how mineral-related data collection may be streamlined and industry-government integration facilitated to address data gaps and fragmentation. Here, we use material flow analysis (MFA) and mass-balance (MB) principles to review current mineral reserve accounting, mine production monitoring, and industry-government data integration. We use this background to define a MB-consistent geological stock accounting approach and broader framework that can help to establish a coherent language across the relevant research fields. We will illustrate how our approach may be used to address the identified data gaps and data fragmentation, and review its context within recent trends in Earth Systems modeling and policymaking to propose next steps toward physical accounting and material systems integration.

2. A Brief Review of Mass-Balance-Consistent Accounting

Monitoring dynamic changes of physical stocks and flows of materials and energy in the socioeconomic metabolism(57) or physical economy(58) reveals how we as producers and consumers of goods and services depend on, and shape, the anthropogenic and natural environment. The birth of industrial dynamics(59) in the late 1950s, industrial metabolism(60,61) in the 1980s, and industrial ecology(62,63) in the 1990s, have laid the groundwork for using integrated system approaches as tools for natural resource management, circular economy efforts, and sustainable development.6466 Since the first formal “materials balance approach” of the U.S. economy was published in 1969,67 MFA has become a well-established method for modeling anthropogenic and natural physical systems at multiple scales, from single-unit processes at the facility level, to complex global material and energy systems.68,69 MFA builds on the basic principle of conservation of mass, derived from the First Law of Thermodynamics.70,71 Throughout history, conservation of mass (MB-consistency) has been recognized as fundamental in chemistry,72,73 forestry,7476 glaciology,7779 hydrology,8082 climatology,83,84 as well as in geology,8587 petroleum reservoir modeling,88,89 mineral processing,90,91 and urban metabolism studies.92,93 MFA formalizes MB-consistency for physical accounting (materials accounting) by requiring that (i) the system boundary be explicitly defined in space and time, (ii) stocks and flows be expressed in consistent physical (nonmonetary) units, and (iii) mass and energy be in balance across transformation, distribution, and storage processes in the system.68,69 Materials occupy space and can only be accounted for if the system boundary and the processes are clearly defined in space (3D) and time,70 e.g., to quantify natural groundwater flows in the Earth’s subsurface, or to model the material stock in houses in the built environment. 2D geospatial data are insufficient, as they can only indicate where materials are on a map but cannot capture their physical characteristics (e.g., 3D shape and extent, mineral distribution, overburden thickness) or their material balance volumes.

For analyzing physical systems, a MB-consistent MFA approach brings diverse benefits:70,71,94

  • The system structure of connected flows carries additional information about the origin and destination of the flows.

  • Mass balance equations make the system structure explicit and can close data gaps without requiring additional data collection.

  • The explicit system definition allows for balancing each process for total mass and all chemical elements, and facilitates data harmonization and integration (e.g., to avoid double-counting).

  • The MB principle is useful for sensitivity analysis and data reconciliation. It enables robust accounting and scenario models for physical matter in the “real world”.

Altogether, MFA provides a robust and transparent reference framework to understand, visualize, and transform material and energy systems and their associated value, information, and emission layers toward sustainability.9496 Recent applications include a plant-level study for Europe’s biggest aluminum smelter outside of Russia,97 the International Aluminium Institute’s “Global Aluminium Cycle”,98 the European Union’s “Material System Analysis” studies,99 and U.S. Geological Survey publications on tantalum, niobium, and rare earth elements (REEs).100102 While there are many examples to demonstrate MFA’s utility, there has not been much discussion about MFA in mineral resource geology, mineral depletion studies, and sustainable mining (cf. Supporting Information, S1.3), partly because of data gaps and a lack of transparency in current industry minerals reporting. Data fragmentation and poor international harmonization8,41,42,51 impede MB-consistent physical accounting. Here, we address this gap and use MFA principles to discuss three key issues related to (1) geological stock accounting (section 3), (2) monitoring of mine production flows (section 4), and (3) systems integration (sections 5 and 6), as illustrated in Figure 1.

Figure 1.

Figure 1

Simplified material flow analysis (MFA) system of the global mineral material cycle. Material flows (arrows) connect material transformation, transport, market, and storage processes (blue boxes) with or without material stocks (white boxes). Highlights in red identify three key issues that require mass-balance-consistent mineral information: geological stock accounting (section 3), monitoring of mine production (section 4), and physical systems integration (sections 5 and 6).

3. The Concept of Geological Stocks

Mineral deposits are nonrenewable in human time scales, and geological exploration and mine project development need to compensate for deposits being depleted. This is increasingly challenging, as global demand for minerals continues to grow,22 while the probability of exploration projects reaching the mining stage remains notoriously low.20 Moreover, lead times from prospecting to production often reach 8–11 years for exploration and additional 9–12 years for mine development.103 Government-industry information flows are crucial in this context. Definitions, methods, and standards for government and industry data collection, sharing, and integration, however, have diverse historical backgrounds and have been developed by different organizations to serve distinct information needs: Government agencies, for instance, collect basic geoscientific and industry data to inform long-term resource management, promote sustainable development, and secure an affordable supply of raw materials at national, regional, and local levels. National- and regional-scale geospatial data sets and mineral resource estimates by government agencies often cover both known and undiscovered mineral deposits, and aim to inform a wide range of users including policy makers, exploration companies, and investors.42,104107 These data sets and resource estimates, however, have diverse underlying assumptions, varying uncertainty, and significant data gaps,41,50,108,109 which make them difficult to compare and integrate. Exploration and mining companies, on the other hand, collect detailed site-scale information for project-specific appraisal (valuation) and operations planning, with the goal of generating revenue though successful mining and refining ventures (Figure 1). As early stage industry exploration projects advance to drilling, permitting, and construction, their costs rapidly grow,20 and companies may use public disclosure to report promising exploration results and attract capital for project development. The 1997 Bre-X mining fraud, which cost investors US$6 billion,110 led regulators and professional associations to increasingly require that such industry disclosures follow “resource classification standards”108,111 (cf. S2) overseen by a certified professional, known as competent person (CP)112 or qualified expert (QE).108,111,113 While the definitions of the terms resources and reserves vary across extractive industries (e.g., industrial minerals, metals, oil and gas) and between jurisdictions (e.g., Australia, Canada, China, United States),108,111,114 they are commonly understood along following lines:104,115reserves are the amount of discovered in-ground commodities that are considered to be economically recoverable and marketable at the time of determination through projects that are committed to be realized, while resources comprise both discovered and undiscovered quantities that are not yet economically recoverable at present in this sense, but may, eventually, be extracted. Both definitions presume some degree of recoverability and human intent, which indicates that resources and reserves are a function of exploration efforts, market demand, regulations, and other environmental, socioeconomic and technical variables (collectively often called “modifying factors”50,112). Reserves are by definition better constrained than resources, yet both are somewhat uncertain, and inherently dynamic.108,109 Remembering this commonality, we here simply use “reserves” to refer to reported quantities estimated through national and international (e.g., CRIRSCO-aligned)112 resource classification standards or through the more generic United Nations Framework Classification for Resources UNFC.116 In contrast to project- and commodity-specific classification of reserves (i.e., reporting only the amount of commodity x we can mine and sell for profit or by applying subsidies), the scope for MB-consistent geological stock accounting is broader in that it aims to facilitate spatiotemporally explicit and MB-consistent data integration and physical accounting for the entire geological “subsurface”117 of a geographical region. Using the terms stock,70,118intrinsic physical properties,119,120spatial compartment,68,70 and mutually exclusive and collectively exhaustive (MECE),119 we suggest the following new definitions: the geological stock is the physical content of a natural material compartment that is delimited by a spatiotemporally explicit, georeferenced, and time-invariant 3D system boundary. Geological stock quantification maps the material content in the defined compartment in a mutually exclusive and collectively exhaustive manner at a specified reference point in time, based on purely intrinsic (e.g., physical, chemical, and mechanical) material properties. Intrinsic properties include, for instance, the total mass, elemental composition, mineralogy, and strength. A physical material flow out of the defined compartment occurs when natural material leaves the system boundary during the period of consideration between two reference points in time, independent of whether the material has an economic value, and regardless of whether the flow results from human activity or natural processes. Geological stock accounting tracks physical material stocks and flows and their changes over time based on their purely physical attributes, which makes it conceptually suitable for MB-consistent raw material system modeling and scenario development. To illustrate conceptual differences between mineral resource classification and MB-consistent physical accounting, we use four MFA system definitions (Figure 2), and individually discuss them below.

Figure 2.

Figure 2

Different approaches for geological stock accounting: (a) reserves included as fixed stocks within the system boundary; (b) exploration interpreted as a (in)flow of material; (c) geosphere excluded from the system boundary; (d) multidimensional and mass-balance (MB)-consistent geological stock model. Approaches (a) and (b) violate material flow analysis (MFA) principles, (c) is permissible but uninformative, and (d) is the spatiotemporally explicit conceptual approach.

3.1. Using Reserves to Calculate Depletion (Figure 2a)

National and global resources and reserves numbers are often combined with production statistics to calculate mineral depletion rates.16,35,36,38,39,121 This incorrectly assumes, without explicitly stating so, that reserves are fixed physical quantities, i.e., “all there is”.111 Accelerating global resource extraction would thus progressively deplete them, aligning with the “fixed-stock paradigm”4 and pessimistic predictions of impending global exhaustion. However, Zimmermann122 pointedly stated in 1951: “resources are not, they become; they are not static, but expand and contract in response to human wants and human actions”. Indeed, reported global resources and reserves of many commodities continue to grow, despite accelerating extraction rates.107,123,124 That reserves are inherently dynamic125 is illustrated by two examples: first, mine life cycle disruptions such as bankruptcy can unexpectedly and instantaneously “erase” a company’s reserves, reducing national (and global) reserve totals; and second, more efficient technology can turn previously subeconomic parts of a deposit into economic reserves, thus increasing reserve totals. Notably, long-term commodity prices have remained relatively stable4,9,11 despite declining ore grades in production.23,24 This was predominantly driven by exploration successes, technological innovation, and economies of scale, which lowered the threshold for economic mining and increased global reserves.23,126,127 On a project level, reserve calculations commonly use a cutoff grade to estimate recoverable in-ground quantities, defined by a set of assumed operating conditions with variable uncertainty, including technical feasibility, labor and fuel costs, taxes, and projected commodity prices. Changes to any of these may call for adjusting the cutoff grade. Higher market prices, for instance, make it feasible to profitably mine lower-grade and deeper ores. Interestingly, empirical data suggest that there is no specific geological or thermodynamic grade-threshold that may limit this trend. While geologists previously postulated a “mineralogical barrier” for the copper concentration (copper ore grade) in the crust,128,129 randomly sampled data across all rock types indicate a unimodal continuum.130 The absence of a clearly identifiable intrinsic(119) ore grade threshold emphasizes that the definition of “ore deposits” (i.e., naturally occurring mineral material “known to be producible to yield a profit)131 is arbitrary from a physical accounting perspective. Reserve numbers of individual industry projects can thus be understood as a snapshot of a “working inventory”132 that dynamically evolves in function of socioeconomic (and thus extrinsic(119)) factors. In addition, project owners may choose or be required to selectively disclose only some of their reserves, to the extent that fits their commercial interest and applicable regulations. Arguably, project owners theoretically have the information to “account” for the entire 3D geological stock volume in their concession area in a MB-consistent manner (e.g., by using 3D block models and data reconciliation).133,134 However, their published reserve numbers only represent those selected individual 3D “blocks”20,135 that fulfill the reserve classification criteria (i.e., a dynamically evolving subsample of the total geological stock). All 3D information is lost after reporting, which implies that published reserves become decoupled in space and time and do not allow for MB-consistent data integration, reconciliation, and material stock and flow accounting. Government mineral inventories and national reserve totals compiled from these selectively reported industry reserve quantities (plus possibly additional government estimates) are hence poorly suited for MB-consistent physical stock accounting. Altogether, while previous authors have already pointed out that reported reserve numbers should not be misinterpreted as fixed stocks,7,11,111,122 we here show that doing so violates MFA principles, and that these estimates cannot be used for MB-consistent physical accounting because reserves data (i) lack explicit georeferencing and a time-invariant 3D system boundary (cf. spatial compartment); (ii) are inherently dynamic and co-defined by extrinsic socioeconomic factors (which continuously changes the MFA balance volume); (iii) and are selectively sampled and neither mutually exclusive nor collectively exhaustive across time and space.

3.2. Modeling Exploration as an Inflow (Figure 2b)

To account for the dynamic nature of reserves, it has been suggested to introduce exploration as an imaginary inflow(136) (“exploration” arrow) representing “flows from unknown resources into a reserve inventory”.7 Geologists commonly categorize exploration projects into greenfields and brownfields exploration, and aim to provide information that helps to “convert”137 or “upgrade”125 mineral discoveries into mineable reserves. Conceptually, greenfield exploration expands the system boundary of reserves though new discoveries and classification outside of previously known geological districts or terrains. This changes the balance volume during the accounting period, which makes it impossible to uphold the MB-principle because the 3D system boundary (spatial compartment) is not time-invariant.70 Brownfields exploration, in contrast, increases the knowledge within previously known terrains that have existing data, often in the vicinity of abandoned or operating mines. New measurements and subsequent (re)classification20 update the geological knowledge of individual blocks inside the imagined 3D system boundary around the entire brownfields volume, and may increase or decrease reported reserves. Regardless, exploration is no measurable physical flow, and this approach cannot solve the MB-consistency issues inherent to reserves accounting.

3.3. MB-Consistency without Geological Stocks (Figure 2c)

The resource optimist’s view can be framed as geological stocks being so vast and markets and human ingenuity so successful in developing new solutions, that accurate quantification of geological stocks is simply irrelevant.25,138 In other words: “Whatever is left in the ground is unknown, probably unknowable, but surely unimportant; a geological fact of no economic interest”.7 Indeed, geologists point out that the mineral content of the Earth’s crust is orders of magnitude bigger than reported industry reserves.111,130 Economists may argue that functioning markets automatically balance production and consumption, and that focusing on production costs and prices, and addressing market failures, is more important than quantifying physical availability.4,139 Translated to MFA, this approach draws the system boundary such that the geological subsystem (geosphere) is excluded from consideration. While this is indeed a MB-consistent system definition, it does not contribute to tracking how Earth’s natural resources are depleted. Importantly, it does not contribute to data collection and knowledge integration for “physically consistent”140 modeling and Earth System Science,141 which we need to evaluate prospective mining localities, develop supply scenarios, and address the ESG issues that are likely to limit mineral production well before any global physical depletion.132,142,143

3.4. MB-Consistent Geological Stock Accounting (Figure 2d)

MB-consistent geological stock accounting requires a spatiotemporally explicit system definition to describe and monitor changes in the geological stock volume in the geosphere. Here, we propose to model the geological stock using a full-coverage 3D digital geomodel (cf. section 5) with a georeferenced time-invariant (fixed) spatial system boundary that establishes the model’s initial physical reference state(27) at an initial reference point in time. By recording the intrinsic physical material properties of stocks and separating them from socioeconomic (and thus extrinsic)119 factors, we can use MFA to track the actual physical changes over time. Combining spatial resolution and MB-equations facilitates both site-specific and regional-scale geological stock quantification and MFA data integration (MFA subsystem modeling approach).144Section 5 elaborates how changes in geological stocks due to mining and better knowledge about intrinsic material properties of specific blocks can be represented. Moreover, this method considers the entire 3D distribution of geological materials in the Earth’s crust and its uncertainty, not just the continuously changing reserves in known mineral deposits. Notably, this scope definition also satisfies the stated objective of the UN System of Environmental-Economic Accounting (SEEA)145 “to include all of the resources that may provide benefits to humanity” (i.e., the entire 3D geological stock), while it also “allows for a full analysis of changes”.145 Altogether, our geological stock accounting approach aims to facilitate data integration to represent the physical reality as accurately as possible with a continuously increasing resolution.

4. Physical Monitoring of Mine Production

It is widely accepted that granular disclosure of relevant data is a key driver for responsible mining and achieving the Sustainable Development Goals (SDGs), for example decent work and economic growth (SDG 8), and responsible consumption and production (SDG 12).146,147 However, systematic site-scale information is still “conspicuously missing”148 from corporate sustainability reporting of mining companies, while corresponding government data sets are often incomplete, fragmented across different agencies, and difficult to integrate, as we show in Figure 3 and the following sections.

Figure 3.

Figure 3

Physical monitoring of mine production. (a) Mine planning: The natural characteristics of mineral deposits such as depth and ore grade, combined with mine design and operating efficiency, determine the expected (ex-ante) material flows. Figure not to scale, modified after ref (163). (b) Material flows and sustainability: Material flows of mining are interlinked with environmental, social, and governance (ESG) issues and tracking them is thus crucial for the Social License to Operate (SLO) and Sustainable Development License to Operate (SDLO). (c) Reference system for physical monitoring: A standardized material flow analysis (MFA) system definition with explicit reference points and a mutually agreed-upon terminology facilitates systematic reporting and enables mass-balance-consistent monitoring of mine production flows.

4.1. Industry Reporting of Mine Production Flows

Mining companies routinely collect material flow data at different stages of their mine life cycles to manage their economic efficiency149 and ESG risks.150,151 However, public disclosure of data on observed past (ex-post) or expected future (ex-ante) material flows is rare and typically neither systematic nor MB-consistent. The amount and quality of in-house information increases as projects advance along the project-production cycle:152 during the prefeasibility and feasibility stages, expected sales production and waste flows can be estimated by combining geological information with mine design and scheduling.153 This makes it necessary to characterize in-ground materials and to calculate total extraction (excavation) volumes and associated flows of topsoil, overburden, below cutoff grade waste rock, and pay-grade ore for further processing (Figure 3a). Besides being essential for mine life cycle costing and environmental optimization at a corporate management level,154,155 this ex-ante information is also of interest for national mineral resource governance and local stakeholders: Specifically, it could be used to demonstrate compliance with legal, regulatory, contractual, fiscal, and infrastructural requirements, and could facilitate stakeholder negotiations to define the terms of the “Social License to Operate” (SLO) and “Sustainable Development License to Operate” (SDLO).53,148,156 Ex-ante data could also help exploit synergies71 between different projects at an early planning stage where design decisions can still be influenced. Yet, these data are rarely systematically reported or updated to reflect changes in planning. During the actual production phase(s), companies routinely monitor material flows along the processing chain to manage operations and ESG risks (Figure 3b).91,133,134 Many jurisdictions mandate annual reporting of “mine production” or “sold production” quantities to mining authorities. However, reported data (information flows) are typically not defined with MB-consistent reference systems (e.g., Figure 3c). This results in misunderstandings regarding what reported production data refer to (e.g., the total mass with average ore grade, or the total pure metal content of sold products) and allows for “hidden” inconsistencies. Moreover, published industry data generally only cover some selected materials and flows (e.g., omit to report removed waste rock),40 exclude relevant details (e.g., whole-rock composition including companion or critical metals and deleterious elements; mineralogy; pH; physical product qualities),50,157 and may be preaggregated across projects to company-levels (i.e., not granular, site-scale). Moreover, depending on the jurisdiction, they may remain entirely undisclosed for entities that are not listed on stock exchanges, or that have revenues below a given threshold.158,159 Similarly, government communication is a problem.160 Reporting may for instance be fragmented across agencies: mining directorates, tax authorities, national environmental protection agencies, or local municipal planning offices collect (but not necessarily share) ex-ante or ex-post information on mining-related material flows for environmental impact assessments, license extensions, taxation, and closure procedures. Similarly, information on planned or completed excavation for urban and infrastructure development projects are often poorly integrated with information on mining projects,161 despite being relevant for construction aggregates (“development minerals”) management and circular economy strategies.162 Altogether, current production reporting does not provide complete material flow data coverage and lacks a material systems context.

4.2. Government Aggregation of Production Data

Reported mine production data are commonly ingested by geological survey organizations (GSOs), mining directorates, and industry associations. Due to confidentiality concerns, these organizations usually only publish them as aggregated mineral production statistics.4042,158 National mine production totals and global production estimates are used by a wide range of stakeholders, e.g., to evaluate markets for project development, assess raw material criticality,164168 investigate the long-run availability of metals,43,105 and develop raw material policies and science-based resource efficiency targets.169 However, the published production statistics are often misinterpreted by data users that do not know their context. Back-calculations using published production statistics, for instance, systematically underestimate total extraction46 because the quantities, types, and composition of nonsales material flows are not correctly reported. Historically, the flows of topsoil, over- and interburden, and below-cutoff waste rock, collectively referred to as hidden or indirect flows,170unused extraction,171 or natural resource residuals,145 were not considered as tradeable commodities with economic value46,67,172,173 and are thus not reported. Indeed, national accounting systems including Eurostat (cf. “Waste disposal to the environment”)171 and the UN System of Environmental-Economic Accounting (SEEA)145 still consider them to be “outside” of the system boundary, assuming they are immediately returned to and part of “the environment”. This scope partly explains why quantitative data on unused extraction are absent from national statistics.46,174 Yet, this does not lessen their relevance for sustainability-related discussions. Hidden flows exert various pressures on the environment and can contain both potentially harmful and useful material.175 For open pit mines, hidden flows are commonly two, and occasionally 30 times bigger than the ore retained (used extraction),176 and orders of magnitude bigger than final sales quantities.40,177 Globally, the mining industry is the largest “waste” producer,156 and in 2016 alone the flow of unreported waste rock was estimated to be 72 billion tonnes (Gt).178 Altogether, the historical flow of nonsales quantities (hidden flows, reported tailings, and other residues) is estimated to have accumulated a total of several hundred Gt of mine wastes.179 While nonsales quantities raise various ESG issues, they can also offer opportunities for remining of tailings, ecosystem restoration, and higher-value land use (Figure 3b). All countries with important mining histories have legacy mine waste stocks. In the United States alone, there are estimated 550 000 abandoned mines, 4–13% of which may pose a risk to human health and the environment.180182 The estimated remediation costs of the 64 priority sites are US$7.8 billion, of which $2.4 billion would come from taxpayers.183 Notably, many risk-prone historical practices have been superseded,184 and historical extraction rates used to be much lower than today. The accelerating mineral extraction rates21,22 and increasing waste-to-ore ratios,51 on the other hand, spotlight the need to better understand and address future waste flows, including though transparent reporting of tailings storage178,185 and monitoring of unused extraction (e.g., topsoil, over- and interburden, waste rock; Figure 3b). This emphasizes concepts such as circular economy,186zero waste,187comprehensive extraction/comprehensive resource recovery,188,189 in addition to remining, reprocessing, and rehabilitation.184,190 All require site-scale and MB-consistent data on material flows and stocks to identify ESG risks,191 facilitate sustainable sourcing, evaluate residual resources and market potentials,192 and to allow for robust data integration. Still, data gaps on mine waste types, volumes, mineralogy, and composition continue to impede resource recovery from growing waste streams (“miningof flows) and historical waste deposits193 (remining of legacy stocks). Similarly, Economy-Wide Material Flow Accounts194 and indicators for Material Footprints,195 Total Material Requirements,172,173 Rock-to-Metal Ratios,40 and project-specific resource efficiency54,196 are all hindered by the poor availability or lack of relevant, robust, and accessible site-scale material stock and flow data.

4.3. Reference Systems for Consistent Reporting

MB-consistent material systems are useful for defining terms (e.g., stocks, flows), relationships, and indicators (e.g., circularity, efficiency, recovery rate). Mining has a long and diverse history across the world, and conflicting definitions abound. The term ore, for instance, can refer to either crude ore or usable ore. Crude ore is often used for run-of-mine or pithead output material that needs further processing to become a saleable product; useable ore may refer to either high-grade direct-shipping ore, or to finished (beneficiated) ore that has undergone further processing to turn it into a saleable product, such as concentrate or pellets. Without a MB-consistent system definition, there is a risk for calculation errors with potentially far-reaching consequences: the U.S. World iron ore production statistics between 2000 and 2014, for instance, overestimated the global production of useable ore by 10 to 32%197 because Chinese production numbers were interpreted as useable ore, although they actually reported crude ore.

Such misunderstandings can be avoided by publishing material system diagrams or material flowcharts that define key terms and use explicit reference points to place reported mine production data into a systems context (Figure 3c). Indeed, the Norwegian Directorate of Mining (DMF) recommends material flowsheets as part of permitting procedures for mining activities.198 Similarly, the Canadian Institute of Mining (CIM) notes that material flow diagrams are of “great assistance” for reconciling long-term models with plant production data,199 and that mass balances of the major flows should be included for internal as well as public reporting of minerals projects.199,200 These guidelines are a first step toward, but not sufficient for, systematic physical monitoring and accounting. They acknowledge that material system diagrams are helpful but do not make their use mandatory, and do not discuss how explicit system boundaries, reference points, and MB principles can facilitate transparent regular (e.g., annual) reporting and monitoring of mine production flows.

5. Geomodeling of Material Stocks and Flows

5.1. Geomodels for Stock Accounting and Resource Classification

Geomodels are digital representations of the Earth’s subsurface201 that are essential for addressing a wide range of societal issues.202 They can be expressed though gridded volume elements (voxels) and attributes that characterize and quantify continuous physical phenomena such as geological formations, groundwater flows, and other subsurface features.203 Geomodels have been extensively used in petroleum reservoir engineering since computers became available in the late 1960s.88 Given our previous definition, geological stocks can be modeled with voxels and analyzed either as a whole or in parts to quantify the total material content together with its average composition and/or that of selected individual voxels, elements, or substances, for any specific point of time, with a certain level of confidence. This may, for instance, be used to calculate the elementary stock of pure copper in tonnes based on the copper grade distribution within a defined volume, or to quantify the total stock of sand and gravel in a region as the sum of sand-containing voxels, for a specific reference point of time. An unlimited number of voxel attributes can be defined to describe stock characteristics. Here, we illustrate geological stock accounting in Figure 4a, using only ore grade and uncertainty. The total extraction flow during the time interval from the initial reference state at t0 to a specified reference state at t1 corresponds to an observed stock reduction. Using prospective geomodeling, further stock reduction may be simulated for a future state t2, subject to probabilistic geomodeling, mine design, and operational planning.204,205 The extracted material leaves the geological stock subsystem (geosphere) and enters the economy. Notably, natural processes such as erosion move material only within the geological subsystem and do not register as a transfer of material from the geosphere. We deliberately separate the geological stock accounting step (a) from the resource classification (b). Geological stock accounting is necessary to build a robust and MB-consistent full-coverage digital model of the physical reality. Resource classification is conceptualized as an optional and independent additional step that acts as a “filter” to selectively appraise specific stock segments that are thought to be of particular interest for further mineral project development. While we postulate that a MB-consistent geological stock model can always serve as a robust information source for subsequent resource classification and aggregation, earlier sections have outlined that the inverse is impossible: reserve numbers cannot be converted to geospatial models and thus have limited utility for mineral depletion, environmental, and sustainability monitoring and assessments.

Figure 4.

Figure 4

Multidimensional geological stock accounting illustrated as a cube with 27 voxels at three reference points (t0, t1, t2). (a) Geological stock accounting monitors changes of the physical domain over time and shows historical extraction as a measured reduction of the total stock S by 0.5 voxels from 27 → 26.5 during t0 → t1 and anticipated further reduction 26.5 → 26 during t1 → t2, assuming stock scenario S1. Exploration activity changes only the attributes (e.g., ore grade) and associated uncertainty of the geological stock characterization (2 voxels from 0% → 25–50% confidence during t0 → t1, and from 25 to 50% →>75% during t1 → t2, assuming stock scenario S1). (b) Resource classification acts as a filter domain that selectively appraises parts of the geological stock to report reserves and resources, while omitting the rest of the geological stock including known but low grade (barren) voxels; Individual geological stock voxels may remain physically unchanged but may nevertheless be reclassified as time passes (1 resources to 1 reserves during t0 → t1) or vice versa (1 reserves to 1 resources during t1 → t2 assuming resource classification scenario S1,ii(t2)). (c) Uncertainty attribution is considered as two separate steps: step c[a] addresses solely the uncertainty of the physical attributes for stock quantification; step c[b] incorporates the additional uncertainty of socioeconomic assumptions of resource classification. Color hue (red, green, blue) represents three ore grade classes relative to average crustal abundance (depleted, average to low grade, enriched); color saturation (0–25, 25–50, 50–75, 75–100) shows the confidence in the results (unknown to complete knowledge). MB, mass-balance.

5.2. Model Uncertainty

Uncertainty is pertinent to the quantification, and visualization of 3D geodata.206208 Epistemic uncertainty arises from incomplete knowledge and can be reduced though new exploration, geological mapping, drilling, and sample analysis.209,210 MB-consistent geological stock accounting presumes that the model’s system boundary (i.e., envelope of all 27 voxels in Figure 4) remains fixed though time. This enables spatially explicit uncertainty attribution for every voxel to capture the evolution of knowledge over time (confidence intervals in Figure 4c). Exploration activity is not considered to be a physical material flow and does not affect the system boundary or the total geological stock volume. Rather, new observations reduce the uncertainty of the attributed physical characteristics of voxels (i.e., increase the confidence in the stock characterization). Conversely, measurements during production can provide a “closed-loop”133 feedback to validate or reconcile the model and increase the confidence for the remaining in situ material. Both integration of (ex-ante) exploration data and closed-loop (ex-post) analysis and feedback thus make the geological stock model for the remaining stock more accurate, useful, and valuable over time. Reported mineral reserve numbers, in contrast, are valid only at a specific point of time; they have additional uncertainty due to extrinsic socioeconomic assumptions that are difficult to constrain and predict.211,212 This shortcoming underscores the strategic benefit of allocating research and funding for MB-consistent geological stock accounting and material flow monitoring: information on material systems describes observable real-world phenomena, helps understand physical changes such as resource depletion, and can contribute to building a continuously growing, versatile, robust, and increasingly accurate global geoscientific knowledge base.

6. Framework for Systems Integration

While the credo of the extractive industry has long been “if we can’t grow it, we have to mine it”,213,214 one may add ‘but we need robust material stock and flow models to know when, where and how to best get it’. The clean energy transition, for instance, requires batteries, solar cells, and wind turbines, but national policies seldom quantify how much lithium, indium and dysprosium will be needed to produce them, and where and how to sustainably source the required minerals, components, or products.215 Answering these questions is challenging without reliable geospatial information and robust scenario models, which again require systematic mine-site-scale material stock (key issue one) and material flow data (issue two). We argue that a more physical-accounting-centric approach to industry-government data integration is necessary and mutually beneficial.

6.1. The Current Situation: Data Fragmentation and Limited Coordination (Figure 5a)

Figure 5.

Figure 5

(a) Today’s information flows on nonrenewable mineral resources result in incomplete, fragmented, and inconsistent knowledge that is unsuitable for addressing systemic issues related to sustainable resource management. (b) The proposed monitoring of physical systems is based on an Open Government Data (OGD) framework that supports multidimensional geodata integration, mass-balance (MB) consistent geological stock accounting, and spatiotemporally explicit material systems governance. PPP: Public-Private Partnership; SLO: Social License to Operate; SDLO: Sustainable Development License to Operate; GSO: Geological Survey Organization; EO: Earth Observation; IoT: Internet of Things; BIM/CIM: Building/City Information Modeling; ML: Machine Learning; AI Artificial Intelligence; AR/VR: Augmented/Virtual Reality; G2B, G2G, B2B, B2G: Government-to-Business data sharing, etc.

The mining industry collects detailed 3D geological as well as material flow data for site-specific project planning and operational management. However, these data sets are typically stored in proprietary company data “silos”,216 and generally not part of public disclosure or formal government reporting (5a, information flow ‘A’). Often, only stock-market-listed mining and exploration companies have public disclosure routines in place. Even in these cases, published data are incompletely georeferenced and lack comparability and consistency both between entities in the same industry and across jurisdictions.52,114 Moreover, details on intrinsic physical properties for systematic quantification and characterization of relevant material stocks and flows (e.g., mass and volume of waste rock, whole-rock composition, mineralogy, pH of tailings) are commonly missing. Notwithstanding, data providers such as S&P Global or Wood Mackenzie compile comprehensive datasets from the available company data; governments, on the other hand, rarely systematically harvest these data to supplement or validate their own information.

Governments collect data by different means and manage enormous amounts of multiscale geospatial information. Data provided by geological survey organisations (GSOs), for instance, are sought-after for mineral exploration and project planning (“information flow” arrow ‘B’), and are key drivers for economic development.217220 In Western Australia, for instance, GSO data delivered an estimated 31-fold total return on investment.219 However, the minerals and mining-related datasets are still mostly 2D, have coarse resolution, and mainly cover areas where publicly funded exploration campaigns have been conducted (“mapped areas” labeled ‘B’). National mineral inventories and mineral statistics combine such government data with mandatory company reporting, and occasionally also voluntary public disclosures and information from industry associations and commercial data providers.41,221 Such data compilation and integration from sources that are poorly standardized, diverse, and can only be selectively sampled is time-consuming and costly.42 Moreover, nongeospatial “external” data cannot readily be integrated into existing geomodels, but rather only indirectly linked to administrative records (e.g., mapped concession areas ‘A’) or approximate locations of production sites (e.g., ‘ID1’). This entails that national mineral inventories have known and unknown (hidden) spatiotemporal data gaps (e.g., irregularly updated reserves information; areas without geodata ‘C’, NoData or data N/A), irreconcilable data overlaps (e.g., contradictory government-industry geodata), and thematic inconsistencies (e.g., different survey methods, reporting dates, or spatiotemporal resolution). Poor metadata and lack of documentation on data collection, cleaning, and aggregation workflows further increases uncertainty. Altogether, today’s government-industry data integration produces inconsistent 2D maps with hidden gaps and unnecessary overlaps. This results in national spatiotemporal data coverages that are neither mutually exclusive (A∩B∩C:= 0), nor collectively exhaustive (total geological stock:= ΣA + ΣB + ΣC).

6.2. Facilitating Integrated Monitoring of Physical Systems (Figure 5b)

Interdisciplinary, cross-scale, digital Earth science platforms and information infrastructures are needed for environmental monitoring, Big Data analytics and cross-disciplinary Earth science.222 Such platforms could form the basis for hybrid modeling approaches140 that obey physical laws, while leveraging data-driven machine learning to better understand the Human–Earth system.223 The OneGeology initiative, for instance, was established to harmonize global geoscience data,224 while the EarthServer community wishes to allow users to “ask any question, any time, on any volume”.225 MB-consistent geological stock accounting aligns with these visions, with Figure 5b showing its role as part of what we call the monitoring of physical systems. Advances in three key domains are particularly favorable for further developments:

  • (i)

    Earth Observation (EO) and Geomodeling. Earth observation (EO) continuously expands our knowledge of an urbanizing planet226228 with exponentially increasing amounts of global-scale, multidimensional time-series data. Data acquisition technologies such as satellites and drones that interact the Internet of Things (IoT) facilitate both global mapping of mining land use,229 and high-resolution mine-site-scale monitoring of production stockpiles and tailings storage facilities.230,231 Such remote and in situ measurements are key to the extractive industry’s Mining 4.0 vision of smart and connected digital transformation.232,233 It is estimated that 95% of EO data have never been accessed, partly due to challenges with managing its volume, variety, veracity, velocity, and the difficulty to extract value (the five Vs).222 This indicates that there is a huge potential for Big Earth Data fusion,222 geospatial artificial intelligence (GeoAI),234 and cloud-based computing, which together can help improve data accessibility and support investigative approaches also for users with limited knowledge.235,236 Simultaneously, free or relatively inexpensive access to open government servers223 or proprietary platforms such as Google’s Earth Engine237 and Microsoft’s Planetary Computer,238 coupled with geodata modeling environments including the Open Data Cube (ODC)236,239 and advances in data processing240 and visualization technologies,241243 facilitate large-area high-resolution geomodeling.244246 Digital twins247,248 may soon become standard tools for modeling the geological subsurface together with production facilities at mine-site (plant) scale, and may be part of larger models that integrate geological information with urban-scale building- and city information models (BIM/CIM) into regional GeoBIM systems.249,250 Indeed, two decades after the former Vice President of the USA Al Gore outlined his vision of a “Digital Earth”,251 the UN-led Coalition for Digital Environmental Sustainability252 has recently declared the development of a “Planetary Digital Twin” a strategic priority for the sustainability transformation. Given the accelerating rate of innovation, we can imagine multidimensional (e.g., 6D = x,y,z + time + scale/resolution + uncertainty)253,254 Digital Earth Science Platforms254256 that allow us to model historical, monitor ongoing, and simulate future geological and anthropogenic stock changes and material flows through space and time.

  • (ii)

    Multidimensional Geoinformation Management. The value of data is maximized by reuse.257 Standards and protocols such as the forthcoming ISO 19123-1 on multidimensional “coverages”256 and the “Spatial Data on the Web Best Practices”258 facilitate sharing and integration of georeferenced multidimensional data with their original granularity (triple-lined arrows). Standardization can be voluntary or mandatory: the European INSPIRE Directive on establishing an infrastructure for spatial information,259 for instance, defines legally binding goals for geodata harmonization across European countries, while the International Union of Geological Sciences follows a voluntary “Big Science Initiative” standardization approach.260,261 Development of a multidimensional “Open Government Data (OGD5.0) Framework for Physical Accounting” can draw on such efforts (cf. Figures 4, 5), while spatiotemporally explicit and MB-consistent reporting can support mutually exclusive and collectively exhaustive(119) data integration and the establishment of digital twins and “cyber-physical systems”.262 Multistakeholder involvement and Public-Private Partnerships (PPPs)263 can commit to “co-create”264 the OGD5.0 for secure, consistent, and integrated Government-to-Government (G2G) and Government-to-Business (G2B) information exchange.218,265 For governments, which serve as stewards for data and natural resources on behalf of society, a material systems approach can help close data gaps, reduce industry-government information asymmetries, and build public knowledge capital to support long-term sustainable development. The industry can benefit from access to previously unavailable information through the B2B data trade. This would allow partners to exploit the collective data volume though machine learning (ML), artificial intelligence (AI),234,266,267 and digital laboratories with augmented and virtual reality (AR/VR),268,269 and can inform mineral systems analysis270 and exploration,47,217 process innovation,266 and supply chain management.103 Similarly, transdisciplinary stakeholder collaborations271 can contribute to joint problem solving.

  • (iii)

    Policy Trends and Best Practice Examples. Knowledge sharing between government and industry, and across supply chains, is a key challenge for mineral resource governance.156,272 The FAIR273 and OGD274 principles, OECD Recommendations,275 and the Integrated Geospatial Information276 and Global Statistical Geospatial Frameworks277 provide high-level guidance for addressing “data and organizational silos”.278 However, additional efforts are needed to ensure more effective data collection (e.g., to avoid data duplication and target key gaps), facilitate better data integration (e.g., georeferencing, MFA system diagrams/flowsheets with explicit data reference points), and promote data reuse (e.g., FAIR principles, PPPs). Various studies have found that voluntary reporting commitments by mining companies emphasized documentation of compliance over actual data disclosure,159,279 failed to guarantee timely and granular project-by-project level reporting,280282 and had limited impact on mine-site level action.148,279 In response, governments are called upon to use their legislative, regulatory, and policy tools to implement new frameworks that support systematic ESG reporting (cf. S2)53,56,283 and granular data disclosure.194,283288 Governments could use a common physical systems approach to monitor and manage material systems, and to set predictable but yet flexible framework conditions263 that allow the extractive industries to compete with their best capabilities for securing future mineral supply. By inviting/requiring mining and exploration companies to submit collected geodata into secure public databases, long-term public knowledge and value creation can be maximized.160 MB-consistent monitoring can promote transparency (e.g., materials certification, traceability) that helps build public trust, contributes to fighting theft, corruption, and tax fraud (e.g., fraudulent transfer pricing) and can ensure that mining activities achieve their project-specific commercial interests, while fulfilling their broader societal obligations toward the SDGs.94,146,147

Altogether, we can maximize the robustness and value of reported material stock and flow data by ensuring that they are (a) georeferenced and MB-consistent over consecutive accounting steps, which enables geospatial analytics, bottom-up raw material analysis, and scenario development with MFA;289 (b) collectively exhaustive regarding spatial coverage and stakeholders including SMEs,283 which facilitates more representative aggregation across project, enterprise, and jurisdictional levels; and (c) open (FAIR), which supports SLO and SDLO negotiations and digital innovation. Reported site-scale data can be used in sustainability assessments55 to inform investors about project risks and opportunities,191,290,291 and to identify trade-offs and synergies across different projects. Overall, MB-consistent data on physical stocks and flows can help to understand decision path dependency292 (e.g., historical mine production data allow approximation of accumulated mine waste stocks), and help set science-based targets293 for mineral supply within the “sustainability solution space”294 or “safe operating space”.295 Future efforts toward integration can draw on experiences from following three initiatives:

  • (1)

    the European Open Data Directive, which requires from its member States that “public sector bodies and public undertakings shall make their documents available [...] in formats that are open, machine-readable, accessible, findable, and re-usable [...] at the best level of precision and granularity”.296 Six thematic categories of high-value data sets are highlighted: geospatial, Earth observation and environment, meteorological, statistical, company information and ownership, and mobility.297 Moreover, the European Commission announced in its European strategy for data(167) that it will explore a regulatory framework to govern the public sector’s reuse of privately held data of public interest, and will launch a strategic “Destination Earth” initiative to develop a very high precision digital model of the Earth.

  • (2)

    the Dutch law on subsurface information, which establishes the Dutch National Key Registry of the Subsurface (BRO) as a central data repository to collect, store, and manage all publicly funded subsurface data.298 A crucial aspect of the BRO is that it integrates confidential personal and industry information related to licensing and use, and that its stepwise implementation is intended to ultimately include data on all subsurface construction activities including measurements related to exploration, extraction, and storage of minerals and geothermal heat.

  • (3)

    the Norwegian National Data Repository for petroleum exploration and production data (Diskos), which is a public-private partnership established in 1992 as a joint venture between the Norwegian government and the oil companies on the Norwegian Continental Shelf.299 Diskos ensures secure, efficient, and standardized data management on behalf of its members, with shared overheads and added benefits. The system holds all the data of all licensees including detailed project metrics (i.e., all geological data, time-based forecasts, investment and operating cost schedules, production, emissions, cash flows etc.).300 This reduces individual data handling costs as company repositories are no longer required, allows business-to-business (B2B) trade of entitlements to confidential data, and facilitates business-to-government (B2G) reporting. Although company data remain confidential, they are accessible for authorized government processes. This decreases the reporting burden, expedites processing, and reduces administrative costs because the government already has access to the information it requires for taxation and resource governance. Diskos also incorporates the information that financial regulators typically require for stock market disclosure, which instills confidence, promotes transparency, and ensures consistency between industry reporting and government inventories. By leveraging the “digital economy”268 for exploration and minerals development,301 common repositories can stimulate data reuse, value maximation in mining, and more transparent taxation. Finally, Diskos contributes significantly to expanding Norway’s collective knowledge capital as new data on licensed and unlicensed areas are continuously integrated. This information will eventually be made public as the needs for confidentiality cease or when licenses expire or are relinquished.

All three initiatives make some level of stakeholder coordination and reporting mandatory. They maximize collective value generation from both a business and societal perspective, clarify roles and responsibilities, and advocate data sharing and reuse.

7. Implementing Physical Monitoring

Transdisciplinary271 research and coordinated efforts can help to ensure that (1) reported data on stocks and stock changes are explicitly georeferenced in space and time, and that documentation includes the original granular data on volume, mass, composition, and relevant intrinsic material properties; (2) reporting mandates cover all relevant stakeholders (including both the formal sector and estimates on artisanal mining) and all relevant material stocks and flows for calculating mass balances across processes; and that (3) reporting workflows use common data standards, MFA system diagrams with explicit reference points and terminology, and multidimensional geodata models that maintain MB-consistency across processing stages through space and time.

Given the increasing momentum toward sustainability reporting, the global appetite for transformative change, and the emergence of Big Earth Data technologies, MB-consistent physical accounting is becoming feasible. Better industry-government coordination and data integration are of mutual benefit, supporting the statement that “without a common framework to organize findings, isolated knowledge does not cumulate.”302 Governments and industry typically share the risks and rewards of mineral extraction in the monetary economy (e.g., operating surplus, taxes), physical economy (mining waste, material supply), and digital economy (data waste, data reuse). Our definitions and framework for MB-consistent geological stock accounting are designed to guide efforts toward an integration of terminology and data, and sustainable management of human-natural physical systems. For implementation, we suggest the following next steps:

  • (i)

    Review and Adapt Policy Frameworks and Legislation for Physical Accounting. Intergovernmental bodies and governments can review current mineral resource, mine production, and ESG reporting to identify their key gaps and limitations with focus on geodata integration and material stock and flow analysis. To clarify information under their stewardship, they may use their platforms to showcase typical applications and limitations of current data and outline key benefits of mass-balance-consistent accounting. Next steps may include defining roles and responsibilities across stakeholders to formalize data sharing and standardization; assigning explicit mandates to address data fragmentation and promote cross-institutional integration; enacting new policies for systematic monitoring of the physical human-natural system; and developing data-driven scenario models to inform decision-making. International partners may include the UN Statistics Division (UNSD), International Resource Panel (IRP), UNECE Expert Group on Resource Management (EGRM), UN Initiative on Global Geospatial Information Management (UN-GGIM), and UN-led Coalition for Digital Environmental Sustainability (CODES). On a country-level, relevant bodies include GSOs, mining directorates, mapping and planning authorities, environment agencies, and statistical offices, as well as professional associations, NGOs, academia, and industry.

  • (ii)

    Develop Infrastructures for Multidimensional Geoinformation. Through transdisciplinary government mandates and partnerships, appointed agencies and relevant stakeholders can review how technical data standards, reporting workflows and accounting systems (e.g., ISO,256 INSPIRE,259 UNFC,116 SEEA,145 UNEP194) may be adapted to facilitate systematic and granular disclosure in-line with OGD, FAIR, and SDLO principles, and how to automate consistent integration for multidimensional minerals-related material stock and flow information. A first step toward promoting research and development of technical infrastructures could make it mandatory for companies and data providers to map their current reporting of materials-related stock and flow data using MFA system diagrams (flowsheets), standard terminology, and explicit reference points. Funding bodies and relevant stakeholders may consider pilot projects to evaluate this idea, define and map relevant terms, and initiate the development of common data models for physical monitoring, multiscale modeling, and MB-consistent accounting.

8. Conclusions

Finding new ways to understand stock-service-benefit relations and make human interactions with the natural environment more sustainable is a key challenge for Earth System Science.140,141,303,304 The proposed definition and conceptual approach combines multidimensional geomodeling with MFA to facilitate mass-balance-consistent geological stock accounting as part of efforts to secure a sustainable mineral supply within biophysical planetary boundaries.66,169,305,306 It marks a paradigm shift for mineral resource governance by (1) enabling integrated monitoring of stock changes and impacts over time; (2) creating a robust basis for on-the-fly calculation of geological and waste stocks, mineral reserves, ESG risks, and asset portfolios; (3) pooling of government-industry information for mineral systems analysis, predictive mapping, and spatial planning to “safeguard” geological deposits for future mining; and by (4) using MFA to inform strategies for mineral supply, circular economy, and on how to balance sustainability trade-offs. While legal and proprietary issues, coordination, and the need to change legacy data systems pose a sizable challenge, investments into integrated physical monitoring and modeling are likely to yield substantial long-term benefits. Data fragmentation, ownership rights to commercial-in-confidence information, as well as diverse definitions, reporting schemes, and institutional responsibilities call for more research on how to standardize terminology, streamline reporting requirements, and collaborate to make mineral information more available and useful for resource management. We expect that industry and professional associations, regulators, and relevant government and international agencies can start with small first steps to promote standardized and granular reporting of site-scale geological stock and material flow data without imposing significant additional burdens on operators, as much of the relevant data are already routinely collected. Further research could help to better understand how the growing momentum of Earth systems monitoring, digital twins, and multistakeholder resource governance dialogue can be combined with FAIR data policies and sustainability efforts to accelerate the buildup of geoscientific knowledge of the “knowns” (showing, e.g., that Europe is not necessarily resource-poor), to better inform efforts on “what needs to be known” (e.g., where to target exploration and direct innovation) for the global public good.

Resource realists play a vital role in research on methods and models to monitor and anticipate physical human-nature interactions, can support initiatives that build the common global Earth System knowledge base, and can help communicate the interconnected challenges of mineral resource depletion and sustainable supply to explore new pathways for satisfying our societal needs within planetary boundaries.

Acknowledgments

We appreciate the insightful comments and valuable feedback provided by our three anonymous reviewers, which greatly contributed to refining this manuscript. We also acknowledge the diligent efforts of the editor, Matthew Eckelman, whose guidance supported the publishing process. M.U.S. thanks the Norwegian University of Science and Technology for funding this research. We gratefully acknowledge support for inputs though the MinFuture project under the European Horizon 2020 Grant Agreement No. 730330. Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. Government.

Supporting Information Available

The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acs.est.3c03088.

  • Materials and methods section describing literature selection and bibliometric analysis; timeline of historical events with reference list; notes on mass balance consistency in financial reporting and the UN System of Environmental-Economic Accounting (PDF)

Author Contributions

M.U.S. conceived, designed, and formalized the research and writing. D.B.M. supervised the work. All authors contributed to authoring the article and provided critical input that helped shape the research, analysis, and paper.

The authors declare no competing financial interest.

Supplementary Material

es3c03088_si_001.pdf (765.1KB, pdf)

References

  1. Smith A.The Wealth of Nations; J. M. Dent & Sons LTD: London, 1776; Vol. 1. [Google Scholar]
  2. Solow R. M. Is the End of the World at Hand?. Challenge 1973, 16 (1), 39–50. 10.1080/05775132.1973.11469961. [DOI] [Google Scholar]
  3. Stiglitz J. E. Growth with Exhaustible Natural Resources: Efficient and Optimal Growth Paths. Symposium on the economics of exhaustible resources 1974, 41, 123–137. 10.2307/2296377. [DOI] [Google Scholar]
  4. Tilton J. E.; Crowson P. C. F.; DeYoung J. H.; Eggert R. G.; Ericsson M.; Guzmán J. I.; Humphreys D.; Lagos G.; Maxwell P.; Radetzki M.; Singer D. A.; Wellmer F.-W. Public policy and future mineral supplies. Resour. Policy 2018, 57, 55–60. 10.1016/j.resourpol.2018.01.006. [DOI] [Google Scholar]
  5. Castillo E.; Eggert R. Reconciling Diverging Views on Mineral Depletion: A Modified Cumulative Availability Curve Applied to Copper Resources. Resour. Conserv. Recycl. 2020, 161, 104896. 10.1016/j.resconrec.2020.104896. [DOI] [Google Scholar]
  6. Beckerman W. Economists, Scientists, and Environmental Catastrophe. Oxford Econ. Pap. 1972, 24 (3), 327–44. 10.1093/oxfordjournals.oep.a041225. [DOI] [Google Scholar]
  7. Adelman M. A. Mineral Depletion, with Special Reference to Petroleum. Rev. Econ. Statist. 1990, 72 (1), 1–10. 10.2307/2109733. [DOI] [Google Scholar]
  8. Krausmann F.; Lauk C.; Haas W.; Wiedenhofer D. From resource extraction to outflows of wastes and emissions: The socioeconomic metabolism of the global economy, 1900–2015. Global Environ. Change 2018, 52, 131–140. 10.1016/j.gloenvcha.2018.07.003. [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Stuermer M. 150 years of boom and bust: what drives mineral commodity prices?. Macroecon. Dynam. 2018, 22 (03), 702–717. 10.1017/S136510051600050X. [DOI] [Google Scholar]
  10. Stuermer M. Non-renewable resource extraction over the long term: empirical evidence from global copper production. Miner. Econ. 2022, 35 (3), 617–625. 10.1007/s13563-022-00352-0. [DOI] [Google Scholar]
  11. Wellmer F.-W. What we have learned from the past and how we should look forward. Miner. Econ. 2022, 35 (3), 765–795. 10.1007/s13563-021-00296-x. [DOI] [Google Scholar]
  12. Pooley G.; Tupy M.. Simon Abundance Index: A New Way to Measure Availability of Resources; Policy Analysis Number 857; Cato Institute, 2018.
  13. Malthus T. R.An Essay on the Principle of Population, As It Affects the Future Improvement of Society; J. Johnson in St Paul’s Church-yard: London, 1798; Vol. 1. [Google Scholar]
  14. Jevons W. S.The Coal Question: An Inquiry Concerning the Progress of the Nation and the Probable Exhaustion of Our Coal-Mines; Macmillan and Co.: London, 1865. [Google Scholar]
  15. Hubbert M. K.Nuclear energy and the fossil fuels. In Drilling and Production Practice; American Petroleum Institute: San Antonio, TX, 1956; p 40. [Google Scholar]
  16. Meadows D. H.; Meadows D. L.; Randers J.; Behrens I. I. I.; W W.. The Limits to Growth: A Report for the Club of Rome’s Project on the Predicament of Mankind; Universe Books: New York, 1972. [Google Scholar]
  17. Georgescu-Roegen N. Energy and economic myths. Southern Econ. J. 1975, 41, 347–381. 10.2307/1056148. [DOI] [Google Scholar]
  18. Daly H. E. Reply to Solow/Stiglitz. Ecological Economics 1997, 22 (3), 271–273. 10.1016/S0921-8009(97)00086-4. [DOI] [Google Scholar]
  19. Lawn P. On the Ehrlich-Simon bet: Both were unskilled and Simon was lucky. Ecological Economics 2010, 69 (11), 2045–2046. 10.1016/j.ecolecon.2010.07.009. [DOI] [Google Scholar]
  20. Wellmer F.-W. Geology and Mining: A Symbiotic Cooperation?!. Mining 2022, 2 (2), 402–424. 10.3390/mining2020021. [DOI] [Google Scholar]
  21. Global Material Resources Outlook to 2060 - Economic Drivers and Environmental Consequences In Organisation for Economic Co-operation and Development Paris; OECD, 2019; p 212.
  22. Global Resources Outlook 2019: Natural Resources for the Future We Want; United Nations Environment Programme, International Resource Panel: Paris, 2019; DTI/2226/NA. [Google Scholar]
  23. Northey S.; Mohr S.; Mudd G. M.; Weng Z.; Giurco D. Modelling future copper ore grade decline based on a detailed assessment of copper resources and mining. Resour. Conserv. Recycl. 2014, 83, 190–201. 10.1016/j.resconrec.2013.10.005. [DOI] [Google Scholar]
  24. Calvo G.; Mudd G.; Valero A.; Valero A. Decreasing Ore Grades in Global Metallic Mining: A Theoretical Issue or a Global Reality?. Resources 2016, 5 (4), 36. 10.3390/resources5040036. [DOI] [Google Scholar]
  25. Conde M. Resistance to Mining. A Review. Ecological Economics 2017, 132, 80–90. 10.1016/j.ecolecon.2016.08.025. [DOI] [Google Scholar]
  26. Andrews T.; Gamu J.; Billon P. L.; Oh C. H.; Reyes D.; Shin J.. Role of Host Governments in Enabling or Preventing Conflict Associated with Mining, Full-length version; United Nations Development Programme: New York, 2018. [Google Scholar]
  27. The IPBES Assessment Report on Land Degradation and Restoration; Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES): Bonn, Germany, 2018. 10.5281/zenodo.3237392. [DOI]
  28. Rötzer N.; Schmidt M. Historical, Current, and Future Energy Demand from Global Copper Production and Its Impact on Climate Change. Resources 2020, 9 (4), 44. 10.3390/resources9040044. [DOI] [Google Scholar]
  29. Luckeneder S.; Giljum S.; Schaffartzik A.; Maus V.; Tost M. Surge in global metal mining threatens vulnerable ecosystems. Global Environ. Change 2021, 69, 102303. 10.1016/j.gloenvcha.2021.102303. [DOI] [Google Scholar]
  30. Turner G.Is Global Collapse Imminent? An Updated Comparison of the Limits to Growth with Historical Data; Melbourne Sustainable Society Institute, The University of Melbourne: 2014. [Google Scholar]
  31. Steffen W.; Broadgate W.; Deutsch L.; Gaffney O.; Ludwig C. The trajectory of the Anthropocene: The Great Acceleration. Anthropocene Review 2015, 2 (1), 81–98. 10.1177/2053019614564785. [DOI] [Google Scholar]
  32. Northey S. A.; Mudd G. M.; Werner T. T.; Jowitt S. M.; Haque N.; Yellishetty M.; Weng Z. The exposure of global base metal resources to water criticality, scarcity and climate change. Global Environ. Change 2017, 44, 109–124. 10.1016/j.gloenvcha.2017.04.004. [DOI] [Google Scholar]
  33. Savinova E.; Evans C.; Lebre E.; Stringer M.; Azadi M.; Valenta R.K. Will global cobalt supply meet demand? The geological, mineral processing, production and geographic risk profile of cobalt. Resour. Conserv. Recycl. 2023, 190, 106855. 10.1016/j.resconrec.2022.106855. [DOI] [Google Scholar]
  34. Lusty P. A. J.; Gunn A. G. Challenges to global mineral resource security and options for future supply. Geological Society, London, Special Publications 2015, 393 (1), 265–276. 10.1144/SP393.13. [DOI] [Google Scholar]
  35. Calvo G.; Valero A.; Valero A. Assessing maximum production peak and resource availability of non-fuel mineral resources: Analyzing the influence of extractable global resources. Resour. Conserv. Recycl. 2017, 125, 208–217. 10.1016/j.resconrec.2017.06.009. [DOI] [Google Scholar]
  36. Turcheniuk K.; Bondarev D.; Singhal V.; Yushin G. Ten years left to redesign lithium-ion batteries. Nature 2018, 559 (7715), 467–470. 10.1038/d41586-018-05752-3. [DOI] [PubMed] [Google Scholar]
  37. Schmidt M. Scarcity and Environmental Impact of Mineral Resources—An Old and Never-Ending Discussion. Resources 2019, 8 (1), 2. 10.3390/resources8010002. [DOI] [Google Scholar]
  38. Henckens T. Scarce mineral resources: Extraction, consumption and limits of sustainability. Resour. Conserv. Recycl. 2021, 169, 105511. 10.1016/j.resconrec.2021.105511. [DOI] [Google Scholar]
  39. Sverdrup H. U.; Olafsdottir A. H.; Ragnarsdottir K. V.. Development of a Biophysical Economics Module for the Global Integrated Assessment Model WORLD7. In Feedback Economics: Economic Modeling with System Dynamics; Cavana R. Y., Dangerfield B. C., Pavlov O. V., Radzicki M. J., Wheat I. D., Eds.; Springer International Publishing: Cham, 2021; pp 247–283. [Google Scholar]
  40. Nassar N. T.; Lederer G. W.; Brainard J. L.; Padilla A. J.; Lessard J. D. Rock-to-Metal Ratio: A Foundational Metric for Understanding Mine Wastes. Environ. Sci. Technol. 2022, 56 (10), 6710–6721. 10.1021/acs.est.1c07875. [DOI] [PMC free article] [PubMed] [Google Scholar]
  41. Bide T.; Brown T. J.; Gunn A. G.; Deady E. Development of decision-making tools to create a harmonised UK national mineral resource inventory using the United Nations Framework Classification. Resources Polym. 2022, 76, 102558. 10.1016/j.resourpol.2022.102558. [DOI] [Google Scholar]
  42. Jorgensen L. F.; Wittenberg A.; Deady E.; Kumelj Š.; Tulstrup J. European mineral intelligence - collecting, harmonizing and sharing data on European raw materials. Geological Society, London, Special Publications 2023, 526 (1), 51–67. 10.1144/SP526-2022-179. [DOI] [Google Scholar]
  43. Graedel T. E.; Barr R.; Cordier D.; Enriquez M.; Hagelüken C.; Hammond N. Q.; Kesler S.; Mudd G.; Nassar N.; Peacey J.; Reck B. K.; Robb L.; Skinner B. J.; Turnbull I.; Santos R. V.; Wall F.; Wittmer D.. Estimating Long-Run Geological Stocks of Metals; Working Group on Geological Stocks of Metals, UNEP International Panel on Sustainable Resource Management: Paris, 2011. [Google Scholar]
  44. Wellmer F. W.; Scholz R. W. Peak minerals: What can we learn from the history of mineral economics and the cases of gold and phosphorus?. Miner. Econ. 2017, 30 (2), 73–93. 10.1007/s13563-016-0094-3. [DOI] [Google Scholar]
  45. Weber L.; Reichl C. Mineral statistics—useful tool or needless exercise?. Mineral economics: raw materials report 2022, 35 (3–4), 569–586. 10.1007/s13563-022-00314-6. [DOI] [Google Scholar]
  46. West J.; Lieber M.; Lutter S.; Schandl H. Proposal for a new compilation system for metal ores in economy wide material flow accounting. J. Ind. Ecol. 2020, 24 (6), 1220–1233. 10.1111/jiec.13015. [DOI] [Google Scholar]
  47. Northey S. A.; Klose S.; Pauliuk S.; Yellishetty M.; Giurco D. Primary Exploration, Mining and Metal Supply Scenario (PEMMSS) model: Towards a stochastic understanding of the mineral discovery, mine development and co-product recovery requirements to meet demand in a low-carbon future. Resources, Conservation & Recycling Advances 2023, 17, 200137. 10.1016/j.rcradv.2023.200137. [DOI] [Google Scholar]
  48. Singer D. A. Comparison of expert estimates of number of undiscovered mineral deposits with mineral deposit densities. Ore Geol. Rev. 2018, 99, 235–243. 10.1016/j.oregeorev.2018.06.019. [DOI] [Google Scholar]
  49. Mudd G. M.; Jowitt S. M. The New Century for Nickel Resources, Reserves, and Mining: Reassessing the Sustainability of the Devil’s Metal. Econ. Geol. 2022, 117 (8), 1961–1983. 10.5382/econgeo.4950. [DOI] [Google Scholar]
  50. Mudd G. M.; Jowitt S. M.; Werner T. T. The world’s by-product and critical metal resources part I: Uncertainties, current reporting practices, implications and grounds for optimizm. Ore Geol. Rev. 2017, 86, 924–938. 10.1016/j.oregeorev.2016.05.001. [DOI] [Google Scholar]
  51. Northey S. A.; Mudd G. M.; Werner T. T. Unresolved Complexity in Assessments of Mineral Resource Depletion and Availability. Nat. Resour. Res. 2018, 27 (2), 241–255. 10.1007/s11053-017-9352-5. [DOI] [Google Scholar]
  52. Simoni M. U.; Aslaksen Aasly K.; Eilu P.; Schjødt F.. Mintell4 EU Deliverable D4.1. Case Study Review with Guidance and Examples for Applying the UNFC to European Mineral Resources; Geological Survey of Norway (NGU): Trondheim, Norway, 2021. [Google Scholar]
  53. Sustainability Reporting in the Mining Sector - Current Status and Future Trends; United Nations Environment Programme (UNEP): Nairobi, Kenya, 2020. [Google Scholar]
  54. Lebre E.; Owen J. R.; Kemp D.; Valenta R. K. Complex orebodies and future global metal supply: An introduction. Resour. Policy 2022, 77, 102696. 10.1016/j.resourpol.2022.102696. [DOI] [Google Scholar]
  55. Sala S.; Ciuffo B.; Nijkamp P. A systemic framework for sustainability assessment. Ecological Economics 2015, 119, 314–325. 10.1016/j.ecolecon.2015.09.015. [DOI] [Google Scholar]
  56. Gorman M. R.; Dzombak D. A. A review of sustainable mining and resource management: Transitioning from the life cycle of the mine to the life cycle of the mineral. Resour. Conserv. Recycl. 2018, 137, 281–291. 10.1016/j.resconrec.2018.06.001. [DOI] [Google Scholar]
  57. Schandl H.; Müller D. B.; Moriguchi Y. Socioeconomic Metabolism Takes the Stage in the International Environmental Policy Debate: A Special Issue to Review Research Progress and Policy Impacts. J. Ind. Ecol. 2015, 19 (5), 689–694. 10.1111/jiec.12357. [DOI] [Google Scholar]
  58. Turner G. M.; Poldy F.. Let’s Get Physical: Creating a Stocks and Flows View of the Australian Economy. In MODSIM 2001, Canberra, Australia, 2001; pp 1637–1642. [Google Scholar]
  59. Forrester J. W. Industrial Dynamics. A major breakthrough for decision makers. Harvard Bus. Rev. 1958, 36 (4), 37–66. [Google Scholar]
  60. Fischer-Kowalski M. Society’s Metabolism - The Intellectual History of Materials Flow Analysis, Part I, 1860–1970. J. Ind. Ecol. 1998, 2 (1), 61–78. 10.1162/jiec.1998.2.1.61. [DOI] [Google Scholar]
  61. Ayres R. U.Industrial metabolism. In Technology and Environment, Ausubel J. H., Sladovich H. E., Eds. The National Academies Press: Washington, D..C., 1989; Vol. 1989, pp 23–49. [Google Scholar]
  62. Frosch R. A.; Gallopoulos N. E. Strategies for manufacturing. Sci. Am. 1989, 261 (3), 144–152. 10.1038/scientificamerican0989-144. [DOI] [Google Scholar]
  63. Graedel T. E.; Allenby B. R.; Telephone A.; Company T.. Industrial Ecology; Prentice Hall, 1995. [Google Scholar]
  64. Sterman J. D.Business Dynamics; McGraw-Hill, 2000. [Google Scholar]
  65. Ghisellini P.; Cialani C.; Ulgiati S. A review on circular economy: the expected transition to a balanced interplay of environmental and economic systems. J. Clean. Prod. 2016, 114, 11–32. 10.1016/j.jclepro.2015.09.007. [DOI] [Google Scholar]
  66. Haberl H.; Wiedenhofer D.; Pauliuk S.; Krausmann F.; Müller D. B.; Fischer-Kowalski M. Contributions of sociometabolic research to sustainability science. Nat. Sustainability 2019, 2 (3), 173–184. 10.1038/s41893-019-0225-2. [DOI] [Google Scholar]
  67. Ayres R. U.; Kneese A. V. Production, consumption, and externalities. Am. Econ. Rev. 1969, 59 (3), 282–297. [Google Scholar]
  68. Baccini P.; Brunner P. H.. Metabolism of the Anthroposphere; Springer: Berlin; New York, 1991. [Google Scholar]
  69. Brunner P. H.; Rechberger H.. Practical Handbook of Material Flow Analysis; CRC Press/LewisPublishers: Boca Raton, FL, 2004. [Google Scholar]
  70. Brunner P. H.; Rechberger H.. Practical Handbook of Material Flow Analysis: For Environmental, Resource, and Waste Engineers, 2nd ed.; CRC Press: Boca Raton, 2017. [Google Scholar]
  71. Cullen J. M.; Cooper D. R. Material Flows and Efficiency. Annu. Rev. Mater. Res. 2022, 52 (1), 525–559. 10.1146/annurev-matsci-070218-125903. [DOI] [Google Scholar]
  72. de Lavoisier A.-L.Traité Élémentaire de Chimie; Chez Cuchet, libraire: Paris, 1789; Vol. 1. [Google Scholar]
  73. Martins R.A priori components of science: Lavoisier and the law of conservation of mass in chemical reactions. In Studies in History and Philosophy of Science II; Quamcumque Editum, 2021; pp 5–71. [Google Scholar]
  74. Hartig G. L.Anweisung zur Taxation der Forste, oder zur Bestimmung des Holzertrags der Wälder; Heyer: Giessen, 1795. [Google Scholar]
  75. Kurth H.; Gerold D.; Ulbricht R.. Forsteinrichtung: Nachhaltige Regelung des Waldes. DLV-Verlag: Berlin, 1994. [Google Scholar]
  76. Müller D. B.; Bader H.-P.; Baccini P. Long-term Coordination of Timber Production and Consumption Using a Dynamic Material and Energy Flow Analysis. J. Ind. Ecol. 2004, 8 (3), 65–88. 10.1162/1088198042442342. [DOI] [Google Scholar]
  77. Anonymous . Mass-Balance Terms. J. Glaciol. 1969, 8 ( (52), ), 3–7. 10.3189/S0022143000020736 [DOI] [Google Scholar]
  78. Cogley J. G. Mass-balance terms revisited. J. Glaciol. 2010, 56 (200), 997–1001. 10.3189/002214311796406040. [DOI] [Google Scholar]
  79. Mellor M. Mass balance studies in Antarctica. J. Glaciol. 1959, 3 (26), 522–533. 10.3189/S0022143000017275. [DOI] [Google Scholar]
  80. Korzoun V. I.World Water Balance and Water Resources of the Earth; USSR Committee for the International Hydrological Decade: Paris, 1978. [Google Scholar]
  81. Aeschbach-Hertig W.; Gleeson T. Regional strategies for the accelerating global problem of groundwater depletion. Nat. Geosci. 2012, 5 (12), 853–861. 10.1038/ngeo1617. [DOI] [Google Scholar]
  82. Peters-Lidard C. D.; Hossain F.; Leung L. R.; McDowell N.; Rodell M.; Tapiador F. J.; Turk F. J.; Wood A. 100 Years of Progress in Hydrology. Meteorological Monographs 2018, 59, 25.1–25.51. 10.1175/AMSMONOGRAPHS-D-18-0019.1. [DOI] [Google Scholar]
  83. Le Quéré C.; Andrew R. M.; Canadell J. G.; Sitch S.; Korsbakken J. I.; Peters G. P.; Manning A. C.; Boden T. A.; Tans P. P.; Houghton R. A.; Keeling R. F.; Alin S.; Andrews O. D.; Anthoni P.; Barbero L.; Bopp L.; Chevallier F.; Chini L. P.; Ciais P.; Currie K.; Delire C.; Doney S. C.; Friedlingstein P.; Gkritzalis T.; Harris I.; Hauck J.; Haverd V.; Hoppema M.; Klein Goldewijk K.; Jain A. K.; Kato E.; Körtzinger A.; Landschützer P.; Lefèvre N.; Lenton A.; Lienert S.; Lombardozzi D.; Melton J. R.; Metzl N.; Millero F.; Monteiro P. M. S.; Munro D. R.; Nabel J. E. M. S.; Nakaoka S.; O’Brien K.; Olsen A.; Omar A. M.; Ono T.; Pierrot D.; Poulter B.; Rödenbeck C.; Salisbury J.; Schuster U.; Schwinger J.; Séférian R.; Skjelvan I.; Stocker B. D.; Sutton A. J.; Takahashi T.; Tian H.; Tilbrook B.; van der Laan-Luijkx I. T.; van der Werf G. R.; Viovy N.; Walker A. P.; Wiltshire A. J.; Zaehle S. Global Carbon Budget 2016. Earth Syst. Sci. Data 2016, 8 (2), 605–649. 10.5194/essd-8-605-2016. [DOI] [Google Scholar]
  84. Wiese D. N.; Bienstock B.; Blackwood C.; Chrone J.; Loomis B. D.; Sauber J.; Rodell M.; Baize R.; Bearden D.; Case K.; Horner S.; Luthcke S.; Reager J. T.; Srinivasan M.; Tsaoussi L.; Webb F.; Whitehurst A.; Zlotnicki V. The Mass Change Designated Observable Study: Overview and Results. Earth Space Sci. 2022, 9 (8), e2022EA002311 10.1029/2022EA002311. [DOI] [Google Scholar]
  85. Lyell C.Principles of Geology: Being an Inquiry how Far the Former Changes of the Earth’s Surface are Referable to Causes Now in Operation; John Murray: London, 1830; Vol. 1. [Google Scholar]
  86. Rudwick M. J. S. The Strategy of Lyell’s Principles of Geology. Isis 1970, 61 (1), 5–33. 10.1086/350576. [DOI] [Google Scholar]
  87. Syvitski J.; Ángel J. R.; Saito Y.; Overeem I.; Vörösmarty C. J.; Wang H.; Olago D. Earth’s sediment cycle during the Anthropocene. Nat. Rev. Earth Environ. 2022, 3 (3), 179–196. 10.1038/s43017-021-00253-w. [DOI] [Google Scholar]
  88. Odeh A. S. Reservoir Simulation···What Is It. J. Pet. Technol. 1969, 21 (11), 1383–1388. 10.2118/2790-PA. [DOI] [Google Scholar]
  89. Magoon L. B.; Dow W. G. The Petroleum System—From Source to Trap. AAPG Memoir 1994, 60, 3–24. 10.1306/M60585C1. [DOI] [Google Scholar]
  90. Wiegel R. L. Advances in mineral processing material balances. Can. Metall. Q. 1972, 11 (2), 413–424. 10.1179/cmq.1972.11.2.413. [DOI] [Google Scholar]
  91. Hodouin D. Methods for automatic control, observation, and optimization in mineral processing plants. Journal of Process Control 2011, 21 (2), 211–225. 10.1016/j.jprocont.2010.10.016. [DOI] [Google Scholar]
  92. Wolman A. The Metabolism of Cities. Sci. Am. 1965, 213 (3), 178–193. 10.1038/scientificamerican0965-178. [DOI] [PubMed] [Google Scholar]
  93. Kennedy C.; Pincetl S.; Bunje P. The study of urban metabolism and its applications to urban planning and design. Environ. Pollut. 2011, 159 (8), 1965–1973. 10.1016/j.envpol.2010.10.022. [DOI] [PubMed] [Google Scholar]
  94. Müller D. B.; Billy R.; Simoni M. U.; Petavratzi E.; Liu G.; Rechberger H.; Lundhaug M. C.; Cullen J. M.. Maps of the physical economy to inform sustainability strategies. In Handbook of Recycling, 2nd ed.; Meskers C., Worrell E., Reuter M. A., Eds.; Elsevier: Waltham, USA, 2023; pp 1–18. [Google Scholar]
  95. Gonzalez Hernandez A.; Lupton R. C.; Williams C.; Cullen J. M. Control data, Sankey diagrams, and exergy: Assessing the resource efficiency of industrial plants. Appl. Energy 2018, 218, 232–245. 10.1016/j.apenergy.2018.02.181. [DOI] [Google Scholar]
  96. Lupton R. C.; Allwood J. M. Hybrid Sankey diagrams: Visual analysis of multidimensional data for understanding resource use. Resour. Conserv. Recycl. 2017, 124, 141–151. 10.1016/j.resconrec.2017.05.002. [DOI] [Google Scholar]
  97. Billy R. G.; Monnier L.; Nybakke E.; Isaksen M.; Müller D. B. Systemic Approaches for Emission Reduction in Industrial Plants Based on Physical Accounting: Example for an Aluminum Smelter. Environ. Sci. Technol. 2022, 56 (3), 1973–1982. 10.1021/acs.est.1c05681. [DOI] [PMC free article] [PubMed] [Google Scholar]
  98. IAI . The Global Aluminium Cycle - Aluminium Stocks and Flows Visualization, 2023. https://alucycle.international-aluminium.org/. (accessed 14.08.2023).
  99. Torres De Matos C.; Wittmer D.; Mathieux F.; Pennington D.. Revision of the Material System Analyses Specifications; JRC118827; European Commission: Luxembourg, 2020. 10.2760/374178. [DOI] [Google Scholar]
  100. Padilla A. J.; Nassar N. T. Dynamic material flow analysis of tantalum in the United States from 2002 to 2020. Resour. Conserv. Recycl. 2023, 190, 106783. 10.1016/j.resconrec.2022.106783. [DOI] [Google Scholar]
  101. McCaffrey D. M.; Nassar N. T.; Jowitt S. M.; Padilla A. J.; Bird L. R. Embedded critical material flow: The case of niobium, the United States, and China. Resour. Conserv. Recycl. 2023, 188, 106698. 10.1016/j.resconrec.2022.106698. [DOI] [Google Scholar]
  102. Alonso E.; Pineault D. G.; Gambogi J.; Nassar N. T. Mapping first to final uses for rare earth elements, globally and in the United States. J. Ind. Ecol. 2023, 27 (1), 312–322. 10.1111/jiec.13354. [DOI] [Google Scholar]
  103. Petavratzi E.; Gunn G.. Decarbonising the automotive sector: a primary raw material perspective on targets and timescales. Miner. Econ. 2023.36545. 10.1007/s13563-022-00334-2 [DOI] [Google Scholar]
  104. McKelvey V. E. Mineral Resource Estimates and Public Policy: Better methods for estimating the magnitude of potential mineral resources are needed to provide the knowledge that should guide the design of many key public policies. Am. Sci. 1972, 60 (1), 32–40. [Google Scholar]
  105. Skinner B. J. Earth resources. Proc. Nat. Acad. Sci. U.S.A. 1979, 76 (9), 4212–4217. 10.1073/pnas.76.9.4212. [DOI] [PMC free article] [PubMed] [Google Scholar]
  106. Kesler S. E.Geological Stocks and Prospects for Nonrenewable Resources. In Linkages of Sustainability; Graedel T. E.; van der Voet E., Eds. The MIT Press: Cambridge, Mass., 2009. [Google Scholar]
  107. NEA, IAEA . Uranium 2020: Resources, Production and Demand; NEA No. 7413; OECD Publishing: Paris, 2021. 10.1787/d82388ab-en. [DOI] [Google Scholar]
  108. Arndt N. T.; Fontboté L.; Hedenquist J. W.; Kesler S. E.; Thompson J. F. H.; Wood D. G. Metals and Minerals, Now and in The Future. Geochem. Perspect. 2017, 6 (1), 3–17. [Google Scholar]
  109. West J. Extractable global resources and the future availability of metal stocks: “Known Unknowns” for the foreseeable future. Resour. Policy 2020, 65, 101574. 10.1016/j.resourpol.2019.101574. [DOI] [Google Scholar]
  110. Andrews G. C.; Shaw P.; McPhee J.. Canadian Professional Engineering and Geoscience: Practice and Ethics, 6 ed.; Nelson: Toronto, 2019. [Google Scholar]
  111. Meinert L. D.; Robinson G. R. Jr; Nassar N. T. Mineral resources: Reserves, peak production and the future. Resources 2016, 5 (1), 14. 10.3390/resources5010014. [DOI] [Google Scholar]
  112. International Reporting Template for the Public Reporting of Exploration Results, Mineral Resources and Mineral Reserves; Committee for Mineral Reserves International Reporting Standards (CRIRSCO) and International Council on Mining & Metals (ICMM): London, 2013. [Google Scholar]
  113. Guidance Note on Competency Requirements for the Estimation, Classification and Management of Resources; ECE/ENERGY/GE.3/2022/4; United Nations Economic Commission for Europe, 2022. [Google Scholar]
  114. IFRS . Extractive Activities - Reserve and Resource Reporting; International Accounting Standards Board (IASB), 2020. [Google Scholar]
  115. Mineral Commodity Summaries 2019 - Appendix C - Reserves and Resources; U.S. Geological Survey: Reston, VA, 2023. 10.3133/mcs2023. [DOI] [Google Scholar]
  116. UNECE . United Nations Framework Classification for Resources Update 2019; ECE/ENERGY/125; United Nations Economic Commission for Europe: Geneva, Switzerland, 2019. [Google Scholar]
  117. Volchko Y.; Norrman J.; Ericsson L. O.; Nilsson K. L.; Markstedt A.; Öberg M.; Mossmark F.; Bobylev N.; Tengborg P. Subsurface planning: Towards a common understanding of the subsurface as a multifunctional resource. Land Use Policy 2020, 90, 104316. 10.1016/j.landusepol.2019.104316. [DOI] [Google Scholar]
  118. Faber M.; Frank K.; Klauer B.; Manstetten R.; Schiller J.; Wissel C. On the foundation of a general theory of stocks. Ecological Economics 2005, 55 (2), 155–172. 10.1016/j.ecolecon.2005.06.006. [DOI] [Google Scholar]
  119. Pauliuk S.; Majeau-Bettez G.; Müller D. B.; Hertwich E. G. Toward a Practical Ontology for Socioeconomic Metabolism. J. Ind. Ecol. 2016, 20 (6), 1260–1272. 10.1111/jiec.12386. [DOI] [Google Scholar]
  120. USGS . NADM Conceptual Model 1.0 - A Conceptual Model for Geologic Map Information; 2004–1334; U.S. Geological Survey: Reston, VA, 2004. 10.3133/ofr20041334. [DOI] [Google Scholar]
  121. Cohen D. Earth’s natural wealth: an audit. New Scientist 2007, 194, 34–41. 23 May 2007 10.1016/S0262-4079(07)61315-3. [DOI] [Google Scholar]
  122. Zimmermann E. W.World Resources and Industries: A Functional Appraisal of the Availability of Agricultural and Industrial Materials, revised ed.; Harper & Row: New York, 1951. [Google Scholar]
  123. Mudd G. M. Assessing the Availability of Global Metals and Minerals for the Sustainable Century: From Aluminium to Zirconium. Sustainability 2021, 13 (19), 10855. 10.3390/su131910855. [DOI] [Google Scholar]
  124. Zeng X. Win-Win: Anthropogenic circularity for metal criticality and carbon neutrality. Frontiers of Environmental Science & Engineering 2023, 17 (2), 23. 10.1007/s11783-023-1623-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
  125. Ray G. F. Mineral reserves: Projected lifetimes and security of supply. Resour. Policy 1984, 10 (2), 75–80. 10.1016/0301-4207(84)90016-3. [DOI] [Google Scholar]
  126. Mudd G. M.; Jowitt S. M. Growing Global Copper Resources, Reserves and Production: Discovery Is Not the Only Control on Supply. Econ. Geol. 2018, 113 (6), 1235–1267. 10.5382/econgeo.2018.4590. [DOI] [Google Scholar]
  127. Ericsson M.; Drielsma J.; Humphreys D.; Storm P.; Weihed P. Why current assessments of ‘future efforts’ are no basis for establishing policies on material use—a response to research on ore grades. Miner. Econ. 2019, 32 (1), 111–121. 10.1007/s13563-019-00175-6. [DOI] [Google Scholar]
  128. Skinner B. J.Exploring the resource base. In Resources for the Future (RFF) Workshop on “The Long-Run Availability of Minerals”; Resources for the Future (RFF) and the Mining, Minerals and Sustainable Development Project (MMSD): Washington, D.C., 2001; p 25. [Google Scholar]
  129. Skinner B. J. A Second Iron Age Ahead? The distribution of chemical elements in the earth’s crust sets natural limits to man’s supply of metals that are much more important to the future of society than limits on energy. Am. Sci. 1976, 64 (3), 258–269. [Google Scholar]
  130. Arndt N.; Fontboté L.; Hedenquist J.; Kesler S.; Thompson J.; Wood D. Future Global Mineral Resources. Geochem. Perspect. 2017, 6 (1), 1–171. 10.7185/geochempersp.6.1. [DOI] [Google Scholar]
  131. United States Bureau of Mines. Dictionary of Mining, Mineral, and Related Terms, 2nd ed.; American Geological Institute: Alexandria, VA, 1997. [Google Scholar]
  132. Jowitt S. M.; Mudd G. M.; Thompson J. F. H. Future availability of non-renewable metal resources and the influence of environmental, social, and governance conflicts on metal production. Commun. Earth Environ. 2020, 1 (1), 13. 10.1038/s43247-020-0011-0. [DOI] [Google Scholar]
  133. Benndorf J.A Closed-Loop Approach for Mineral Resource Extraction. In Closed Loop Management in Mineral Resource Extraction: Turning Online Geo-Data into Mining Intelligence; Springer International Publishing: Cham, 2020; pp 5–17. [Google Scholar]
  134. Ghorbani Y.; Nwaila G. T.; Chirisa M. Systematic Framework toward a Highly Reliable Approach in Metal Accounting. Miner. Process. Extr. Metall. Rev. 2022, 43 (5), 664–678. 10.1080/08827508.2020.1784164. [DOI] [Google Scholar]
  135. Emery X.; Ortiz J. M.; Rodríguez J. J. Quantifying Uncertainty in Mineral Resources by Use of Classification Schemes and Conditional Simulations. Math. Geol. 2006, 38 (4), 445–464. 10.1007/s11004-005-9021-9. [DOI] [Google Scholar]
  136. Sonderegger T.; Berger M.; Alvarenga R.; Bach V.; Cimprich A.; Dewulf J.; Frischknecht R.; Guinée J.; Helbig C.; Huppertz T.; Jolliet O.; Motoshita M.; Northey S.; Rugani B.; Schrijvers D.; Schulze R.; Sonnemann G.; Valero A.; Weidema B. P.; Young S. B. Mineral resources in life cycle impact assessment—part I: a critical review of existing methods. Int. J. Life Cycle Assess. 2020, 25 (4), 784–797. 10.1007/s11367-020-01736-6. [DOI] [Google Scholar]
  137. Whiting T. H.; Schodde R. C.. Why do brownfields exploration? In International Mine Management 2006; Australasian Institute of Mining and Metallurgy: Melbourne, 2006; pp 41–50. [Google Scholar]
  138. Solow R. M. Resources and Economic Growth. American Economist 1978, 22 (2), 5–11. 10.1177/056943457802200201. [DOI] [Google Scholar]
  139. Tilton J. E. The Hubbert peak model and assessing the threat of mineral depletion. Resour. Conserv. Recycl. 2018, 139, 280–286. 10.1016/j.resconrec.2018.08.026. [DOI] [Google Scholar]
  140. Reichstein M.; Camps-Valls G.; Stevens B.; Jung M.; Denzler J.; Carvalhais N.; Prabhat Deep learning and process understanding for data-driven Earth system science. Nature 2019, 566 (7743), 195–204. 10.1038/s41586-019-0912-1. [DOI] [PubMed] [Google Scholar]
  141. Steffen W.; Richardson K.; Rockström J.; Schellnhuber H. J.; Dube O. P.; Dutreuil S.; Lenton T. M.; Lubchenco J. The emergence and evolution of Earth System Science. Nat. Rev. Earth Environ. 2020, 1 (1), 54–63. 10.1038/s43017-019-0005-6. [DOI] [Google Scholar]
  142. Prior T.; Giurco D.; Mudd G.; Mason L.; Behrisch J. Resource depletion, peak minerals and the implications for sustainable resource management. Global Environ. Change 2012, 22 (3), 577–587. 10.1016/j.gloenvcha.2011.08.009. [DOI] [Google Scholar]
  143. Dewulf J.; Hellweg S.; Pfister S.; León M. F. G.; Sonderegger T.; de Matos C. T.; Blengini G. A.; Mathieux F. Towards sustainable resource management: identification and quantification of human actions that compromise the accessibility of metal resources. Resour. Conserv. Recycl. 2021, 167, 105403. 10.1016/j.resconrec.2021.105403. [DOI] [Google Scholar]
  144. Tanzer J.; Rechberger H. Setting the Common Ground: A Generic Framework for Material Flow Analysis of Complex Systems. Recycling 2019, 4 (2), 23. 10.3390/recycling4020023. [DOI] [Google Scholar]
  145. United Nations; European Commission; Food and Agricultural Organization of the United Nations; International Monetary Fund; Organization for Economic Co-operation and Development; World Bank . System of Environmental-Economic Accounting 2012: Central Framework; United Nations: Washington, 2014. 10.5089/9789211615630.069. [DOI] [Google Scholar]
  146. Sonesson C.; Davidson G.; Sachs L.. Mapping Mining to the Sustainable Development Goals: An Atlas; Geneva, Switzerland, 2016. [Google Scholar]
  147. Mining and the SDGs: A 2020 Status Update; RMF, CCS: Nyon, Switzerland, 2020. 10.2139/ssrn.3726386. [DOI] [Google Scholar]
  148. RMI Report 2022 - Summary; Responsible Mining Foundation (RMF): Ontwerp, NL, 2022. [Google Scholar]
  149. Steiner G.; Geissler B.; Watson I.; Mew M. C. Efficiency developments in phosphate rock mining over the last three decades. Resour. Conserv. Recycl. 2015, 105, 235–245. 10.1016/j.resconrec.2015.10.004. [DOI] [Google Scholar]
  150. Lèbre C.; Owen J. R.; Corder G. D.; Kemp D.; Stringer M.; Valenta R. K. Source Risks As Constraints to Future Metal Supply. Environ. Sci. Technol. 2019, 53 (18), 10571–10579. 10.1021/acs.est.9b02808. [DOI] [PMC free article] [PubMed] [Google Scholar]
  151. Mine-Site Study 2019: Mine-Site ESG Data Disclosure by Small and Mid-Tier Mining Companies; Responsible Mining Foundation (RMF): Antwerp, NL, 2019. [Google Scholar]
  152. McLellan B. C.; Corder G. D. Risk reduction through early assessment and integration of sustainability in design in the minerals industry. J. Clean. Prod. 2013, 53 (0), 37–46. 10.1016/j.jclepro.2012.02.014. [DOI] [Google Scholar]
  153. Noble A. C.Mineral resource estimation. In SME Mining Engineering Handbook, 3rd ed.; Darling P., Ed.; Society for Mining, Metallurgy, and Exploration: Englewood, CO, 2011; pp 203–217. [Google Scholar]
  154. Pell R.; Tijsseling L.; Palmer L. W.; Glass H. J.; Yan X.; Wall F.; Zeng X.; Li J. Environmental optimization of mine scheduling through life cycle assessment integration. Resour. Conserv. Recycl. 2019, 142, 267–276. 10.1016/j.resconrec.2018.11.022. [DOI] [Google Scholar]
  155. Hustrulid W. A.; Kuchta M.; Martin R. K.. Open Pit Mine Planning and Design. 3rd ed.; CRC Press: London, 2013. [Google Scholar]
  156. Mineral Resource Governance in the 21st Century: Gearing Extractive Industries Towards Sustainable Development; International Resource Panel, United Nations Environment Programme: Nairobi, Kenya, 2020. [Google Scholar]
  157. Dehaine Q.; Tijsseling L. T.; Glass H. J.; Törmänen T.; Butcher A. R. Geometallurgy of cobalt ores: A review. Miner. Eng. 2021, 160, 106656. 10.1016/j.mineng.2020.106656. [DOI] [Google Scholar]
  158. Bide T.; Horvath Z.; Brown T.; Idoine N.; Lauko A.; Sores L.; Petavratzi E.; McGrath E.; Bavec S.; Rokavec D.; Eloranta T.; Aasly K.. ORAMA Project Deliverable 1.2. Final Analysis and Recommendations for the Improvement of Statistical Data Collection Methods in Europe for Primary Raw Materials; Brussels, 2018. [Google Scholar]
  159. Current Non-Financial Reporting Formats and Practices; European Financial Reporting Advisory Group (EFRAG): Brussels, Belgium, 2021. [Google Scholar]
  160. Minerals and Economic Development. In Breaking New Ground: Mining, Minerals and Sustainable Development; Mining, Minerals and Sustainable Development; International Institute for Environment and Development (IIED): London, 2002; pp 172–196. [Google Scholar]
  161. Torres A.; Simoni M. U.; Keiding J. K.; Müller D. B.; zu Ermgassen S. O. S. E.; Liu J.; Jaeger J. A. G.; Winter M.; Lambin E. F. Sustainability of the global sand system in the Anthropocene. One Earth 2021, 4 (5), 639–650. 10.1016/j.oneear.2021.04.011. [DOI] [Google Scholar]
  162. Franks D. M.; Keenan J.; Hailu D. Mineral security essential to achieving the Sustainable Development Goals. Nat. Sustainability 2023, 6 (1), 21–27. 10.1038/s41893-022-00967-9. [DOI] [Google Scholar]
  163. European Commission . Reference Document on Best Available Techniques for Management of Tailings and Waste-Rock in Mining Activities; ST/EIPPCB/MTWR_BREF_FINAL; European Integrated Pollution Prevention and Control Bureau (EIPPCB): Seville, Spain, 2009. [Google Scholar]
  164. Graedel T. E.; Nassar N. T. The criticality of metals: a perspective for geologists. Geological Society, London, Special Publications 2015, 393 (1), 291–302. 10.1144/SP393.4. [DOI] [Google Scholar]
  165. Hayes S. M.; McCullough E. A. Critical minerals: A review of elemental trends in comprehensive criticality studies. Resour. Policy 2018, 59, 192–199. 10.1016/j.resourpol.2018.06.015. [DOI] [Google Scholar]
  166. Yan W.; Wang Z.; Cao H.; Zhang Y.; Sun Z. Criticality assessment of metal resources in China. iScience 2021, 24 (6), 102524. 10.1016/j.isci.2021.102524. [DOI] [PMC free article] [PubMed] [Google Scholar]
  167. McNulty B. A.; Jowitt S. M. Barriers to and uncertainties in understanding and quantifying global critical mineral and element supply. iScience 2021, 24 (7), 102809. 10.1016/j.isci.2021.102809. [DOI] [PMC free article] [PubMed] [Google Scholar]
  168. Schrijvers D.; Hool A.; Blengini G. A.; Chen W.-Q.; Dewulf J.; Eggert R.; van Ellen L.; Gauss R.; Goddin J.; Habib K.; Hagelüken C.; Hirohata A.; Hofmann-Amtenbrink M.; Kosmol J.; Le Gleuher M.; Grohol M.; Ku A.; Lee M.-H.; Liu G.; Nansai K.; Nuss P.; Peck D.; Reller A.; Sonnemann G.; Tercero L.; Thorenz A.; Wäger P. A. A review of methods and data to determine raw material criticality. Resour. Conserv. Recycl. 2020, 155, 104617. 10.1016/j.resconrec.2019.104617. [DOI] [Google Scholar]
  169. Bringezu S. Toward science-based and knowledge-based targets for global sustainable resource use. Resources 2019, 8 (3), 140. 10.3390/resources8030140. [DOI] [Google Scholar]
  170. United Nations; European Commission; International Monetary Fund; Organization for Economic Co-operation and Development; World Bank . Handbook of National Accounting: Integrated Environmental and Economic Accounting; United Nations: New York, 2003. [Google Scholar]
  171. EUROSTAT . Economy-wide Material Flow Accounts. Handbook 2018 ed.; Eurostat: Luxembourg, 2018. 10.2785/158567. [DOI] [Google Scholar]
  172. Adriaanse A.; Bringezu S.; Hammond A.; Moriguchi Y.; Rodenburg E.; Rogich D.; Schütz H.. Resource Flows: The Material Basis of Industrial Economies; World Resources Inst.: WA, 1997. [Google Scholar]
  173. Watari T.; McLellan B. C.; Giurco D.; Dominish E.; Yamasue E.; Nansai K. Total material requirement for the global energy transition to 2050: A focus on transport and electricity. Resour. Conserv. Recycl. 2019, 148, 91–103. 10.1016/j.resconrec.2019.05.015. [DOI] [Google Scholar]
  174. Global Economy Wide Material Flow Accounting Manual; UN Environment: Nairobi, 2019. [Google Scholar]
  175. Bringezu S. Possible Target Corridor for Sustainable Use of Global Material Resources. Resources 2015, 4 (1), 25–54. 10.3390/resources4010025. [DOI] [Google Scholar]
  176. Zamorano S.Surface ore movement, storage, and recovery systems. In SME Mining Engineering Handbook, 3rd ed.; Darling P., Ed.; Society for Mining, Metallurgy, and Exploration (SME), 2011; pp 977–985. [Google Scholar]
  177. European Commission . Best Available Techniques (BAT) Reference Document for the Management of Waste from Extractive Industries in Accordance with Directive 2006/21/EC; EU Publications Office: Luxembourg, 2018. 10.2760/35297. [DOI] [Google Scholar]
  178. Baker E.; Davies M.; Fourie A.; Mudd G.; Thygesen K.. Mine Tailings Facilities: Overview and Industry Trends. In Towards Zero Harm: A Compendium of Papers Prepared for the Global Tailings Review; Global Tailings Review: London, 2020; pp 14–23. [Google Scholar]
  179. Lottermoser B. G.Mine Wastes: Characterization, Treatment and Environmental Impacts, 3rd ed.; Springer Berlin Heidelberg: Berlin, 2010. [Google Scholar]
  180. Fields S. The earth’s open wounds: abandoned and orphaned mines. Environ. Health Perspect. 2003, 111 (3), A154–A161. 10.1289/ehp.111-a154. [DOI] [PMC free article] [PubMed] [Google Scholar]
  181. Seymour J. F. Hardrock Mining and the Environment: Issues of Federal Enforcement and Liability. Ecol. Law Q. 2004, 31 (4), 795–956. [Google Scholar]
  182. Hudson-Edwards K. A.; Jamieson H. E.; Lottermoser B. G. Mine Wastes: Past, Present, Future. Elements 2011, 7 (6), 375–380. 10.2113/gselements.7.6.375. [DOI] [Google Scholar]
  183. Mittal A. K.Abandoned Mines: Information on the Number of Hardrock Mines, Cost of Cleanup, and Value of Financial Assurances; Testimony Before the Subcommittee on Energy and Mineral Resources, Committee on Natural Resources, House of Representatives; US Government Accountability Office: Washington, D.C., 14.07.2011, 2011. [Google Scholar]
  184. Lottermoser B. G. Recycling, Reuse and Rehabilitation of Mine Wastes. Elements 2011, 7 (6), 405–410. 10.2113/gselements.7.6.405. [DOI] [Google Scholar]
  185. Franks D. M.; Stringer M.; Torres-Cruz L. A.; Baker E.; Valenta R.; Thygesen K.; Matthews A.; Howchin J.; Barrie S. Tailings facility disclosures reveal stability risks. Sci. Rep. 2021, 11 (1), 5353. 10.1038/s41598-021-84897-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  186. Kirchherr J.; Reike D.; Hekkert M. Conceptualizing the circular economy: An analysis of 114 definitions. Resour. Conserv. Recycl. 2017, 127, 221–232. 10.1016/j.resconrec.2017.09.005. [DOI] [Google Scholar]
  187. Song Q.; Li J.; Zeng X. Minimizing the increasing solid waste through zero waste strategy. J. Clean. Prod. 2015, 104, 199–210. 10.1016/j.jclepro.2014.08.027. [DOI] [Google Scholar]
  188. Hilton J.; Moussaid M.; Birky B. In Comprehensive Extraction: A Key Requirement for Social Licensing of NORM Industries?; Seventh International Symposium on Naturally Occurring Radioactive Material (NORM VII); International Atomic Energy Agency, 22-26.04.2013; Beijing, China, 2013; pp 129–141. [Google Scholar]
  189. MacDonald D.; Hilton J.; Elliott D.; Heiberg S.; Tulsidas H.; Griffiths C. In Transforming Natural Resource Management for a Sustainable Planet; SPE Annual Technical Conference and Exhibition 2018, ATCE 2018; Dallas, U.S.A., 2018; p 10. [Google Scholar]
  190. Blengini G.; Mathieux F.; Mancini L.; Nyberg M.; Viegas H.. Recovery of Critical and Other Raw Materials from Mining Waste and Landfills; Publications Office of the European Union: Luxembourg, 2019. 10.2760/600775. [DOI] [Google Scholar]
  191. Lebre E.; Stringer M.; Svobodova K.; Owen J. R.; Kemp D.; Cote C.; Arratia-Solar A.; Valenta R. K. The social and environmental complexities of extracting energy transition metals. Nat. Commun. 2020, 11 (1), 4823. 10.1038/s41467-020-18661-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
  192. Suppes R.; Heuss-Aßbichler S. Resource potential of mine wastes: A conventional and sustainable perspective on a case study tailings mining project. J. Clean. Prod. 2021, 297, 126446. 10.1016/j.jclepro.2021.126446. [DOI] [Google Scholar]
  193. Žibret G.; Lemiere B.; Mendez A.-M.; Cormio C.; Sinnett D.; Cleall P.; Szabó K.; Carvalho M. T. National Mineral Waste Databases as an Information Source for Assessing Material Recovery Potential from Mine Waste, Tailings and Metallurgical Waste. Minerals 2020, 10 (5), 446. 10.3390/min10050446. [DOI] [Google Scholar]
  194. The Use of Natural Resources in the Economy: A Global Manual on Economy Wide Material Flow Accounting; DEW/2356/NA; United Nations Environment Programme: Nairobi, Kenya, 2023. [Google Scholar]
  195. Lenzen M.; Geschke A.; West J.; Fry J.; Malik A.; Giljum S.; Milài Canals L.; Piñero P.; Lutter S.; Wiedmann T.; Li M.; Sevenster M.; Potočnik J.; Teixeira I.; Van Voore M.; Nansai K.; Schandl H. Implementing the material footprint to measure progress towards Sustainable Development Goals 8 and 12. Nat. Sustainability 2022, 5 (2), 157–166. 10.1038/s41893-021-00811-6. [DOI] [Google Scholar]
  196. Lebre E.; Corder G. D.; Golev A. Sustainable practices in the management of mining waste: A focus on the mineral resource. Miner. Eng. 2017, 107, 34–42. 10.1016/j.mineng.2016.12.004. [DOI] [Google Scholar]
  197. Tuck C. A.; Xun S.; Singerling S. A. Global Iron Ore Production Data; Clarification of Reporting from USGS. Mining Eng. 2017, 69 (2), 20–23. [Google Scholar]
  198. Driftsplanveileder Fast fjell; Direktoratet for mineralforvaltning med Bergmesteren for Svalbard: Trondheim, 2021. [Google Scholar]
  199. CIM Estimation of Mineral Resources and Mineral Reserves Best Practice Guidelines; CIM: Quebec, Canada, 2019. [Google Scholar]
  200. CIM Leading Practice Guidelines for Mineral Processing; CIM: Quebec, Canada, 2022. [Google Scholar]
  201. Apel M. From 3d geomodelling systems towards 3d geoscience information systems: Data model, query functionality, and data management. Comput. Geosci. 2006, 32 (2), 222–229. 10.1016/j.cageo.2005.06.016. [DOI] [Google Scholar]
  202. Berg R. C.; Kessler H.; MacCormack K. E.; Russell H. A.; Thorleifson L. H. Future of 3D Geological Mapping and Modelling at Geological Survey Organizations. 2019 Synopsis of Three-dimensional Geological Mapping and Modelling at Geological Survey Organizations 2019, 302–305. [Google Scholar]
  203. Stafleu J.; Maljers D.; Busschers F. S.; Schokker J.; Gunnink J. L.; Dambrink R. M. Models Created as 3-D Cellular Voxel Arrays. Applied Multidimensional Geological Modeling 2021, 247–271. 10.1002/9781119163091.ch11. [DOI] [Google Scholar]
  204. Dimitrakopoulos R. Stochastic optimization for strategic mine planning: A decade of developments. J. Min. Sci. 2011, 47 (2), 138–150. 10.1134/S1062739147020018. [DOI] [Google Scholar]
  205. Goodfellow R. C.; Dimitrakopoulos R. Global optimization of open pit mining complexes with uncertainty. Appl. Soft Comput. 2016, 40, 292–304. 10.1016/j.asoc.2015.11.038. [DOI] [Google Scholar]
  206. Lindsay M. D.; Aillères L.; Jessell M. W.; de Kemp E. A.; Betts P. G. Locating and quantifying geological uncertainty in three-dimensional models: Analysis of the Gippsland Basin, southeastern Australia. Tectonophysics 2012, 546–547, 10–27. 10.1016/j.tecto.2012.04.007. [DOI] [Google Scholar]
  207. Krajnovich A.; Zhou W.; Gutierrez M. Uncertainty assessment for 3D geologic modeling of fault zones based on geologic inputs and prior knowledge. Solid Earth 2020, 11 (4), 1457–1474. 10.5194/se-11-1457-2020. [DOI] [Google Scholar]
  208. Bianchi M.; Turner A. K.; Lark M.; Courrioux G.. Uncertainty in 3-D Geological Models. In Applied Multidimensional Geological Modeling; John Wiley & Sons Ltd: West Sussex, UK, 2021; pp 357–382. [Google Scholar]
  209. Dowd P.Quantifying the Impacts of Uncertainty. In Handbook of Mathematical Geosciences: Fifty Years of IAMG; Daya Sagar B. S., Cheng Q., Agterberg F., Eds.; Springer International Publishing: Cham, 2018; pp 349–373. [Google Scholar]
  210. Abdulai M.; Sharifzadeh M. Uncertainty and Reliability Analysis of Open Pit Rock Slopes: A Critical Review of Methods of Analysis. Geotech. Geol. Eng. 2019, 37 (3), 1223–1247. 10.1007/s10706-018-0680-y. [DOI] [Google Scholar]
  211. Speirs J.; McGlade C.; Slade R. Uncertainty in the availability of natural resources: Fossil fuels, critical metals and biomass. Energy Policy 2015, 87, 654–664. 10.1016/j.enpol.2015.02.031. [DOI] [Google Scholar]
  212. McManus S.; Rahman A.; Coombes J.; Horta A. Uncertainty assessment of spatial domain models in early stage mining projects - A review. Ore Geol. Rev. 2021, 133, 104098. 10.1016/j.oregeorev.2021.104098. [DOI] [Google Scholar]
  213. Bloodworth A. J.; Gunn A. G. The future of the global minerals and metals sector: issues and challenges out to 2050. Geosciences: BRGM’s Journal for a Sustainable Earth 2012, 15, 90–97. [Google Scholar]
  214. Cole L.How ending mining would change the world. 2022. https://www.bbc.com/future/article/20220413-how-ending-mining-would-change-the-world (accessed 18.04.2023).
  215. Liang Y.; Kleijn R.; Tukker A.; van der Voet E. Material requirements for low-carbon energy technologies: A quantitative review. Renew. Sust. Energy Rev. 2022, 161, 112334. 10.1016/j.rser.2022.112334. [DOI] [Google Scholar]
  216. More K. S.; Wolkersdorfer C.; Kang N.; Elmaghraby A. S. Automated measurement systems in mine water management and mine workings - A review of potential methods. Water Resour. Ind. 2020, 24, 100136. 10.1016/j.wri.2020.100136. [DOI] [Google Scholar]
  217. Yousefi M.; Carranza E. J. M.; Kreuzer O. P.; Nykänen V.; Hronsky J. M. A.; Mihalasky M. J. Data analysis methods for prospectivity modelling as applied to mineral exploration targeting: State-of-the-art and outlook. J. Geochem. Explor. 2021, 229, 106839. 10.1016/j.gexplo.2021.106839. [DOI] [Google Scholar]
  218. Nurmi P. A. The Geological Survey of Finland strengthening its role as a key player in mineral raw materials innovation ecosystems. Geological Society, London, Special Publications 2020, 499 (1), 149–163. 10.1144/SP499-2019-83. [DOI] [Google Scholar]
  219. Fogarty J. J.An Economic Assessment of the Exploration Incentive Scheme: 10 years from 2009 to 2020; Prepared for the Department of Mines, Industry Regulation and Safety: Geological Survey of Western Australia: Perth, Australia, 2021. [Google Scholar]
  220. Wittenberg A.; Oliveira D. d.; Jorgensen L. F.; Gonzalez F. J.; Heldal T.; Aasly K. A.; Deady E.; Kumelj Š.; Sievers H.; Horvath Z.; McGrath E.. GeoERA Raw Materials Monograph - The Past and the Future; Federal Institute for Geosciences and Natural Resources (BGR): Hannover, Germany, 2022. 10.25928/geoera_rawmat22_1. [DOI] [Google Scholar]
  221. Bide T.; Brown T. J.; Gunn A. G.; Mankelow J. M. Utilisation of multiple current and legacy datasets to create a national minerals inventory: A UK case study. Resour. Policy 2020, 66, 101654. 10.1016/j.resourpol.2020.101654. [DOI] [Google Scholar]
  222. van Genderen J.; Goodchild M. F.; Guo H.; Yang C.; Nativi S.; Wang L.; Wang C.. Digital Earth Challenges and Future Trends. In Manual of Digital Earth; Guo H., Goodchild M. F., Annoni A., Eds.; Springer: Singapore, 2020; pp 811–827. [Google Scholar]
  223. Sudmanns M.; Tiede D.; Lang S.; Bergstedt H.; Trost G.; Augustin H.; Baraldi A.; Blaschke T. Big Earth data: disruptive changes in Earth observation data management and analysis?. International Journal of Digital Earth 2020, 13 (7), 832–850. 10.1080/17538947.2019.1585976. [DOI] [PMC free article] [PubMed] [Google Scholar]
  224. OneGelogy Consortium . OneGelogy - Providing geoscience data globally 2022. https://onegeology.org/ (accessed 18.04.2023).
  225. Baumann P.; Rossi A. P.; Bell B.; Clements O.; Evans B.; Hoenig H.; Hogan P.; Kakaletris G.; Koltsida P.; Mantovani S.; Marco Figuera R.; Merticariu V.; Misev D.; Pham H. B.; Siemen S.; Wagemann J.. Fostering Cross-Disciplinary Earth Science Through Datacube Analytics. In Earth Observation Open Science and Innovation, Mathieu P.-P.; Aubrecht C., Eds.; Springer International Publishing: Cham, 2018; pp 91–119. [Google Scholar]
  226. O’Sullivan C.; Wise N.; Mathieu P.-P.. The Changing Landscape of Geospatial Information Markets. In Earth Observation Open Science and Innovation; Mathieu P.-P., Aubrecht C., Eds.; Springer International Publishing: Cham, 2018; pp 3–23. [Google Scholar]
  227. Zhu Z.; Zhou Y.; Seto K. C.; Stokes E. C.; Deng C.; Pickett S. T. A.; Taubenböck H. Understanding an urbanizing planet: Strategic directions for remote sensing. Remote Sens. Environ. 2019, 228, 164–182. 10.1016/j.rse.2019.04.020. [DOI] [Google Scholar]
  228. Prakash M.; Ramage S.; Kavvada A.; Goodman S. Open Earth Observations for Sustainable Urban Development. Remote Sens. 2020, 12 (10), 1646. 10.3390/rs12101646. [DOI] [Google Scholar]
  229. Maus V.; Giljum S.; da Silva D. M.; Gutschlhofer J.; da Rosa R. P.; Luckeneder S.; Gass S. L. B.; Lieber M.; McCallum I. An update on global mining land use. Sci. Data 2022, 9 (1), 433. 10.1038/s41597-022-01547-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
  230. Ren H.; Zhao Y.; Xiao W.; Hu Z. A review of UAV monitoring in mining areas: current status and future perspectives. Int. J. Coal Sci. 2019, 6 (3), 320–333. 10.1007/s40789-019-00264-5. [DOI] [Google Scholar]
  231. Tucci G.; Gebbia A.; Conti A.; Fiorini L.; Lubello C. Monitoring and Computation of the Volumes of Stockpiles of Bulk Material by Means of UAV Photogrammetric Surveying. Remote Sens. 2019, 11 (12), 1471. 10.3390/rs11121471. [DOI] [Google Scholar]
  232. New Tech, new deal - Technology Impacts Review; Intergovernmental Forum on Mining, Minerals, Metals and Sustainable Development (IGF). International Institute for Sustainable Development (IISD): Winnipeg, Canada, 2019. [Google Scholar]
  233. Jang H.; Topal E. Transformation of the Australian mining industry and future prospects. Mining Technology 2020, 129 (3), 120–134. 10.1080/25726668.2020.1786298. [DOI] [Google Scholar]
  234. Li W.; Hsu C.-Y. GeoAI for Large-Scale Image Analysis and Machine Vision: Recent Progress of Artificial Intelligence in Geography. ISPRS International Journal of Geo-Information 2022, 11 (7), 385. 10.3390/ijgi11070385. [DOI] [Google Scholar]
  235. Smith W. D.; Maier W. D. The geotectonic setting, age and mineral deposit inventory of global layered intrusions. Earth-Sci. Rev. 2021, 220, 103736. 10.1016/j.earscirev.2021.103736. [DOI] [Google Scholar]
  236. Dong J.; Metternicht G.; Hostert P.; Fensholt R.; Chowdhury R. R. Remote sensing and geospatial technologies in support of a normative land system science: status and prospects. COSUST 2019, 38, 44–52. 10.1016/j.cosust.2019.05.003. [DOI] [Google Scholar]
  237. Gorelick N.; Hancher M.; Dixon M.; Ilyushchenko S.; Thau D.; Moore R. Google Earth Engine: Planetary-scale geospatial analysis for everyone. Remote Sens. Environ. 2017, 202, 18–27. 10.1016/j.rse.2017.06.031. [DOI] [Google Scholar]
  238. Planetary Computer; Microsoft, 2022. [Google Scholar]
  239. Kopp S.; Becker P.; Doshi A.; Wright D. J.; Zhang K.; Xu H. Achieving the Full Vision of Earth Observation Data Cubes. Data 2019, 4 (3), 94. 10.3390/data4030094. [DOI] [Google Scholar]
  240. Bauer P.; Dueben P. D.; Hoefler T.; Quintino T.; Schulthess T. C.; Wedi N. P. The digital revolution of Earth-system science. Nature Computational Science 2021, 1 (2), 104–113. 10.1038/s43588-021-00023-0. [DOI] [PubMed] [Google Scholar]
  241. Graciano A.; Rueda A. J.; Feito F. R. Real-time visualization of 3D terrains and subsurface geological structures. Adv. Eng. Software 2018, 115, 314–326. 10.1016/j.advengsoft.2017.10.002. [DOI] [Google Scholar]
  242. Schokker J.; Sandersen P.; de Beer J.; Eriksson I.; Kallio H.; Kearsey T.; Pfleiderer S.; Seither A.. 3D Urban Subsurface Modelling and Visualisation - A Review of Good Practices and Techniques to Ensure Optimal Use of Geological Information in Urban Planning; COST Action Sub-Urban, 2017. [Google Scholar]
  243. Baumberger R.; Oesterling N.. The National Geological Model: Towards mastering the Digital Transformation in Switzerland. In Three-Dimensional Geological Mapping and Modeling; Vancouver, BC, 2018; pp 19–23. [Google Scholar]
  244. Guo J.; Wang X.; Wang J.; Dai X.; Wu L.; Li C.; Li F.; Liu S.; Jessell M. W. Three-dimensional geological modeling and spatial analysis from geotechnical borehole data using an implicit surface and marching tetrahedra algorithm. Eng. Geol. 2021, 284, 106047. 10.1016/j.enggeo.2021.106047. [DOI] [Google Scholar]
  245. Guo H.; Li X.; Wang W.; Lv Z.; Wu C.; Xu W. An event-driven dynamic updating method for 3D geo-databases. Geo-Spat. Inf. Sci. 2016, 19 (2), 140–147. 10.1080/10095020.2016.1182808. [DOI] [Google Scholar]
  246. Marker B.; Turner A. K.. Legislation, regulation and management. In Applied Multidimensional Geological Modeling; Turner A. K., Kessler H., Van der Meulen M., Eds.; John Wiley & Sons, 2021; pp 35–68. [Google Scholar]
  247. Grieves M.Virtually Intelligent Product Systems: Digital and Physical Twins. In Complex Systems Engineering: Theory and Practice; Flumerfelt S., Schwartz K. G., Mavris D., Briceno S., Eds. American Institute of Aeronautics and Astronautics: Reston, VA, 2019; pp 175–200. [Google Scholar]
  248. Rasheed A.; San O.; Kvamsdal T. Digital Twin: Values, Challenges and Enablers From a Modeling Perspective. IEEE Access 2020, 8, 21980–22012. 10.1109/ACCESS.2020.2970143. [DOI] [Google Scholar]
  249. Zobl F.; Marschallinger R. GeoBIM - Subsurface Building Information Modelling. GEOinformatics 2008, 8 (11), 40–43. [Google Scholar]
  250. Huang M. Q.; Ninić J.; Zhang Q. B. BIM, machine learning and computer vision techniques in underground construction: Current status and future perspectives. Tunnel. Underground Space Technol. 2021, 108, 103677. 10.1016/j.tust.2020.103677. [DOI] [Google Scholar]
  251. Gore A. The digital earth: understanding our planet in the 21st century. Australian surveyor 1998, 43 (2), 89–91. 10.1080/00050348.1998.10558728. [DOI] [Google Scholar]
  252. Coalition for Digital Environmental Sustainability . Action Plan for a Sustainable Planet in the Digital Age; United Nations: 2022. 10.5281/zenodo.6573509. [DOI] [Google Scholar]
  253. Van Oosterom P.; Stoter J.. 5D data modelling: full integration of 2D/3D space, time and scale dimensions; International Conference on Geographic Information Science, 2010; Springer: 2010; pp 310–324. [Google Scholar]
  254. Turner A. K.; Kessler H.; Van der Meulen M.. Introduction to modeling terminology and concepts. In Applied Multidimensional Geological Modeling, Turner A. K.; Kessler H.; Van der Meulen M., Eds.; John Wiley & Sons, 2021; pp 3–33. [Google Scholar]
  255. Breunig M.; Bradley P. E.; Jahn M.; Kuper P.; Mazroob N.; Rösch N.; Al-Doori M.; Stefanakis E.; Jadidi M. Geospatial Data Management Research: Progress and Future Directions. ISPRS International Journal of Geo-Information 2020, 9 (2), 95. 10.3390/ijgi9020095. [DOI] [Google Scholar]
  256. Baumann P. A General Conceptual Framework for Multi-Dimensional Spatio-Temporal Data Sets. Environ. Model. Software 2021, 143, 105096. 10.1016/j.envsoft.2021.105096. [DOI] [Google Scholar]
  257. European Commission . Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions - A European strategy for data. Official Journal of the European Union, COM/2020/66 final, 2020. [Google Scholar]
  258. van den Brink L.; Barnaghi P.; Tandy J.; Atemezing G.; Atkinson R.; Cochrane B.; Fathy Y.; Garcia Castro R.; Haller A.; Harth A.; Janowicz K.; Kolozali S.; van Leeuwen B.; Lefrancois M.; Lieberman J.; Perego A.; Le-Phuoc D.; Roberts B.; Taylor K.; Troncy R. Best practices for publishing, retrieving, and using spatial data on the web. Semantic Web 2018, 10 (1), 95–114. 10.3233/SW-180305. [DOI] [Google Scholar]
  259. European Commission . Directive 2007/2/EC of the European Parliament and of the Council of 14 March 2007 establishing an Infrastructure for Spatial Information in the European Community (INSPIRE). Official Journal of the European Union, L 108, 1–14, 2007. [Google Scholar]
  260. Deep-time Digital Earth (DDE) 2020–2030; International Union of Geological Sciences IUGS: Yangcheng, China, 2022. [Google Scholar]
  261. Wang C.; Hazen R. M.; Cheng Q.; Stephenson M. H.; Zhou C.; Fox P.; Shen S.-z.; Oberhänsli R.; Hou Z.; Ma X.; Feng Z.; Fan J.; Ma C.; Hu X.; Luo B.; Wang J.; Schiffries C. M. The Deep-Time Digital Earth program: data-driven discovery in geosciences. Natl. Sci. Rev. 2021, 8 (9), nwab027. 10.1093/nsr/nwab027. [DOI] [PMC free article] [PubMed] [Google Scholar]
  262. Xu L. D. The contribution of systems science to Industry 4.0. Systems Research and Behavioral Science 2020, 37 (4), 618–631. 10.1002/sres.2705. [DOI] [Google Scholar]
  263. Åm K.; Heiberg S. Public-private partnership for improved hydrocarbon recovery - Lessons from Norway’s major development programs. Energy Strategy Reviews 2014, 3, 30–48. 10.1016/j.esr.2014.06.003. [DOI] [Google Scholar]
  264. Prahalad C. K.; Ramaswamy V. Co-creation experiences: The next practice in value creation. J. Interact. Mark. 2004, 18 (3), 5–14. 10.1002/dir.20015. [DOI] [Google Scholar]
  265. Scott M.; Jones M.. Management of Public Geoscience Data; International Mining for Development Centre (IM4DC): Perth, Australia, 2014. [Google Scholar]
  266. Nad A.; Jooshaki M.; Tuominen E.; Michaux S.; Kirpala A.; Newcomb J. Digitalization Solutions in the Mineral Processing Industry: The Case of GTK Mintec, Finland. Minerals 2022, 12 (2), 210. 10.3390/min12020210. [DOI] [Google Scholar]
  267. Sun Z.; Sandoval L.; Crystal-Ornelas R.; Mousavi S. M.; Wang J.; Lin C.; Cristea N.; Tong D.; Carande W. H.; Ma X.; Rao Y.; Bednar J. A.; Tan A.; Wang J.; Purushotham S.; Gill T. E.; Chastang J.; Howard D.; Holt B.; Gangodagamage C.; Zhao P.; Rivas P.; Chester Z.; Orduz J.; John A. A review of Earth Artificial Intelligence. Comput. Geosci. 2022, 159, 105034. 10.1016/j.cageo.2022.105034. [DOI] [Google Scholar]
  268. Litvinenko V. S. Digital Economy as a Factor in the Technological Development of the Mineral Sector. Nat. Resour. Res. 2020, 29 (3), 1521–1541. 10.1007/s11053-019-09568-4. [DOI] [Google Scholar]
  269. Ghorbani Y.; Zhang S. E.; Nwaila G. T.; Bourdeau J. E. Framework components for data-centric dry laboratories in the minerals industry: A path to science-and-technology-led innovation. Extr. Ind. Soc. 2022, 10, 101089. 10.1016/j.exis.2022.101089. [DOI] [Google Scholar]
  270. McCuaig T. C.; Hronsky J. M. A.; Kelley K. D.; Golden H. C.. The Mineral System Concept: The Key to Exploration Targeting. In Building Exploration Capability for the 21st Century; Society of Economic Geologists: 2014; Vol. 18, p 0. [Google Scholar]
  271. Lawrence M. G.; Williams S.; Nanz P.; Renn O. Characteristics, potentials, and challenges of transdisciplinary research. One Earth 2022, 5 (1), 44–61. 10.1016/j.oneear.2021.12.010. [DOI] [Google Scholar]
  272. UNEA . Mineral Resource Governance. United Nations Environment Programme, 2019. [Google Scholar]
  273. Wilkinson M. D.; Dumontier M.; Aalbersberg I. J.; Appleton G.; Axton M.; Baak A.; Blomberg N.; Boiten J.-W.; da Silva Santos L. B.; Bourne P. E.; Bouwman J.; Brookes A. J.; Clark T.; Crosas M.; Dillo I.; Dumon O.; Edmunds S.; Evelo C. T.; Finkers R.; Gonzalez-Beltran A.; Gray A. J. G.; Groth P.; Goble C.; Grethe J. S.; Heringa J.; ’t Hoen P. A. C.; Hooft R.; Kuhn T.; Kok R.; Kok J.; Lusher S. J.; Martone M. E.; Mons A.; Packer A. L.; Persson B.; Rocca-Serra P.; Roos M.; van Schaik R.; Sansone S.-A.; Schultes E.; Sengstag T.; Slater T.; Strawn G.; Swertz M. A.; Thompson M.; van der Lei J.; van Mulligen E.; Velterop J.; Waagmeester A.; Wittenburg P.; Wolstencroft K.; Zhao J.; Mons B. The FAIR Guiding Principles for scientific data management and stewardship. Sci. Data 2016, 3 (1), 160018. 10.1038/sdata.2016.18. [DOI] [PMC free article] [PubMed] [Google Scholar]
  274. Ubaldi B.Open Government Data: Towards Empirical Analysis of Open Government Data Initiatives; Organisation for Economic Cooperation and Development: 2013. 10.1787/5k46bj4f03s7-en. [DOI] [Google Scholar]
  275. Recommendation of the Council on Enhancing Access to and Sharing of Data; Organisation for Economic Co-operation and Development, 2022.
  276. Integrated Geospatial Information Framework: A Strategic Guide to Develop and Strengthen National Geospatial Information Management - Part 1: Overarching Strategic Framework; World Bank, United Nations Committee of Experts on Global Geospatial Information Management (UN-GGIM): New York, 2018. [Google Scholar]
  277. UN-GGIM . The Global Statistical Geospatial Framework; United Nations: New York, 2019. [Google Scholar]
  278. Tate M.; Bongiovanni I.; Kowalkiewicz M.; Townson P. Managing the “Fuzzy front end” of open digital service innovation in the public sector: A methodology. IJIM 2018, 39, 186–198. 10.1016/j.ijinfomgt.2017.11.008. [DOI] [Google Scholar]
  279. Gray S. J.; Hellman N.; Ivanova M. N. Extractive Industries Reporting: A Review of Accounting Challenges and the Research Literature. Abacus 2019, 55 (1), 42–91. 10.1111/abac.12147. [DOI] [Google Scholar]
  280. 2017 Resource Governance Index; Natural Resource Governance Institute (NRGI): New York, 2017. [Google Scholar]
  281. Van Alstine J. Critical reflections on 15 years of the Extractive Industries Transparency Initiative (EITI). Extr. Ind. Soc. 2017, 4 (4), 766–770. 10.1016/j.exis.2017.10.010. [DOI] [Google Scholar]
  282. EITI Progress Report 2022; Extractive Industries Transparency Initiative (EITI): Oslo, Norway, 2022. [Google Scholar]
  283. Proposals for a Relevant and Dynamic EU Sustainability Reporting Standard-Setting; European Financial Reporting Advisory Group (EFRAG): Brussels, Belgium, 2021. [Google Scholar]
  284. Geels F. W.; Schwanen T.; Sorrell S.; Jenkins K.; Sovacool B. K. Reducing energy demand through low carbon innovation: A sociotechnical transitions perspective and thirteen research debates. ERSS 2018, 40, 23–35. 10.1016/j.erss.2017.11.003. [DOI] [Google Scholar]
  285. IGF Guidance for Governments: Environmental Management and Mining Governance; Intergovernmental Forum on Mining, Minerals, Metals and Sustainable Development (IGF): Winnipeg, 2021. [Google Scholar]
  286. Vision 2050 - Time to Transform: How business can lead the transformations the world needs; World Business Council for Sustainable Development (WBCSD): Geneva, Switzerland, 2021. [Google Scholar]
  287. Transforming Extractive Industries for Sustainable Development; United Nations Executive Office of the Secretary-General (EOSG): New York, 2021. DOI: 10.18356/27082245-22. [DOI] [Google Scholar]
  288. Berg F.; Koelbel J. F.; Rigobon R. Aggregate confusion: The divergence of ESG ratings. Rev. Financ. 2022, 26 (6), 1315–1344. 10.1093/rof/rfac033. [DOI] [Google Scholar]
  289. Petravatzi E.; Müller D. B.; Lundhaug M.; Liu G.; Cullen J.; Simoni M. U.; Dittrich M.; Cao Z.; Murguía D.; Hirschnitz-Garbers M.; Hamadová B.. MinFuture Roadmap - A Roadmap Towards Monitoring the Physical Economy; Nottingham, UK, 2018. [Google Scholar]
  290. Fonseca A.; McAllister M. L.; Fitzpatrick P. Measuring what? A comparative anatomy of five mining sustainability frameworks. Miner. Eng. 2013, 46–47, 180–186. 10.1016/j.mineng.2013.04.008. [DOI] [Google Scholar]
  291. General Requirements for Disclosure of Sustainability-related Financial Information. General Requirements Exposure Draft; Exposure Draft IFRS S1 International Sustainability Standards Board (ISSB): London, 2022. [Google Scholar]
  292. Haasnoot M.; Biesbroek R.; Lawrence J.; Muccione V.; Lempert R.; Glavovic B. Defining the solution space to accelerate climate change adaptation. Reg. Environ. Change 2020, 20 (2), 37. 10.1007/s10113-020-01623-8. [DOI] [Google Scholar]
  293. Giesekam J.; Norman J.; Garvey A.; Betts-Davies S. Science-Based Targets: On Target?. Sustainability 2021, 13 (4), 1657. 10.3390/su13041657. [DOI] [Google Scholar]
  294. Wiek A.; Binder C. Solution spaces for decision-making—a sustainability assessment tool for city-regions. Environ. Impact Assess. Rev. 2005, 25 (6), 589–608. 10.1016/j.eiar.2004.09.009. [DOI] [Google Scholar]
  295. Rockström J.; Gupta J.; Lenton T. M.; Qin D.; Lade S. J.; Abrams J. F.; Jacobson L.; Rocha J. C.; Zimm C.; Bai X.; Bala G.; Bringezu S.; Broadgate W.; Bunn S. E.; DeClerck F.; Ebi K. L.; Gong P.; Gordon C.; Kanie N.; Liverman D. M.; Nakicenovic N.; Obura D.; Ramanathan V.; Verburg P. H.; van Vuuren D. P.; Winkelmann R. Identifying a Safe and Just Corridor for People and the Planet. Earth's Future 2021, 9 (4), e2020EF001866 10.1029/2020EF001866. [DOI] [Google Scholar]
  296. European Commission . Directive 2019/1024 of the European Parliament and of the Council of 20 June 2019 on open data and the re-use of public sector information. Official Journal of the European Union, L 172, 56–83, 2019. [Google Scholar]
  297. European Commission . Commission Implementing Regulation (EU) 2023/138 of 21 December 2022 laying down a list of specific high-value datasets and the arrangements for their publication and re-use. Official Journal of the European Union, L 19, 43–75, 2023. [Google Scholar]
  298. Koninkrijk der Nederlanden . Regulation on the National Key Registry for the Subsurface (Regeling basisregistratie ondergrond, BRO). Minister van Binnenlandse Zaken en Koninkrijksrelaties, Nederlande, 2021. [Google Scholar]
  299. Norwegian Petroleum Directorate . Diskos Handbook, Version 2.0; May 2019; Norwegian Petroleum Directorate: Stavanger, Norway, 2019. [Google Scholar]
  300. Olje-og energidepartementet . Forskrift om ressursforvaltning i petroleumsvirksomheten (ressursforskriften). 2021. [Google Scholar]
  301. Kolbjørnsen O.; Hammer E.; Pruno S.; Wellsbury P.; Kusak M. In Norwegian Released Wells Project: Study Design, Material Preparation, Measurements and Data Analysis; SPWLA 63rd Annual Logging Symposium, 2022; 2022. [Google Scholar]
  302. Ostrom E. A General Framework for Analyzing Sustainability of Social-Ecological Systems. Science 2009, 325 (5939), 419–422. 10.1126/science.1172133. [DOI] [PubMed] [Google Scholar]
  303. Steffen W.; Crutzen P. J.; McNeill J. R. The Anthropocene: are humans now overwhelming the great forces of nature. Ambio 2007, 36 (8), 614–621. 10.1579/0044-7447(2007)36[614:TAAHNO]2.0.CO;2. [DOI] [PubMed] [Google Scholar]
  304. Bateman I. J.; Mace G. M. The natural capital framework for sustainably efficient and equitable decision making. Nat. Sustainability 2020, 3 (10), 776–783. 10.1038/s41893-020-0552-3. [DOI] [Google Scholar]
  305. Steffen W.; Rockström J.; Richardson K.; Lenton T. M.; Folke C.; Liverman D.; Summerhayes C. P.; Barnosky A. D.; Cornell S. E.; Crucifix M.; Donges J. F.; Fetzer I.; Lade S. J.; Scheffer M.; Winkelmann R.; Schellnhuber H. J. Trajectories of the Earth System in the Anthropocene. Proc. Nat. Acad. Sci. U.S.A. 2018, 115 (33), 8252–8259. 10.1073/pnas.1810141115. [DOI] [PMC free article] [PubMed] [Google Scholar]
  306. Wackernagel M.; Hanscom L.; Jayasinghe P.; Lin D.; Murthy A.; Neill E.; Raven P. The importance of resource security for poverty eradication. Nat. Sustainability 2021, 4 (8), 731–738. 10.1038/s41893-021-00708-4. [DOI] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

es3c03088_si_001.pdf (765.1KB, pdf)

Articles from Environmental Science & Technology are provided here courtesy of American Chemical Society

RESOURCES