Submitted:
17 January 2023
Posted:
17 January 2023
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Abstract

Keywords:
Environmental Significance
Introduction
Radiocarbon Summary
Revelle Isotopic Anomaly
CO2 Finite Reserve Model
- There is a continuous CO2 outflow AOUT, from the atmosphere to a global carbon mixing reservoir, the flow being proportional to the CO2 atmospheric level, ACO2, as listed (Data Ref 1,2). The constant of proportionality is the inverse turnover time, T (IPCC 2013 Glossary); it determines the initial rate of fall of the 14C bomb pulse, (Figures 2 and 3), and is a solution parameter.
- Carbon is returned to the atmosphere from the reservoir via an inflow of CO2. The amount returned, AIN, is calculated by "balancing the budget" of outflow with the known atmospheric growth of CO2, Δ(ACO2) and fossil fuel emissions input AFF, as shown in Figure 1. CO2 inflow from a reservoir in which atmospheric CO2 has previously accumulated hinders the fall in value of 14C. Hence it predominantly determines the shape of the tail of the 14C bomb pulse, the rate of fall of δ13C, and recent δ13C levels, see Figure 3, Figure 4 and Figure 5. Note that some inflows are roughly independent of atmospheric CO2 level (e.g., fire / respiration) while others may be dependant upon pressure difference (e.g., oceanic flux). Both types of inflow are computed within this balanced budget method. The relative reservoir size, RCO2, is a solution parameter.
- Total fossil fuel emissions inflows (CO2FF) are derived from known listings (Data Ref 3). A portion of the inflow, as described by an Airborne Factor, AF, is directly mixed into the atmosphere, while the remaining portion (1-AF) is absorbed directly by the reservoir. This does not imply the absorption is instantaneous, because each cycle is annual. AF is a solution parameter. It predominantly determines the shape of the tail of the 14C bomb pulse, the rate of fall of δ13C, and recent δ13C levels Figure 3, Figure 4 and Figure 5.
- Inflow of 14CO2 from known listed atmospheric atomic weapon detonations B14, (Data Ref 5) are assumed to be linearly related to the bomb yield. The conversion factor Yb (14C [in 1820 background units] per megaton) is a solution parameter. It has the main effect of scaling the bomb pulse portion of the graph after 1960, Figure 3.
- Isotopic 13C and 14C concentrations are calculated using Dalton’s mixing laws, see Appendix B. Fractionation is considered negligible at the reservoir-atmosphere boundary so fractionation factors are implicitly unity. The isotopic equilibrium is identical for 13C ,14C and 12C hence there is no Revelle exception. In accounting for isotopic concentration, it is not necessary to explicitly embed Stuiver's attenuation factor, Suess dilution or a general Revelle factor (see Radiocarbon above), because they are implicitly represented. The initial values i.e. δ13Cinit, Δ14Cinit , determine the initial level of the curves in Figure 3 and Figure 4 and for δ13CFF determine the curve slopes in Figure 4 and Figure 5. δ13Cinit, Δ14Cinit and fossil fuel δ13Cff content are solution parameters.





Results
6. Discussion
7. Conclusions
Acknowledgments
Appendix A. Notes on Tans 1993 and Tans 2022
Appendix B. Notes on Isotopic Mixtures and Radiocarbon Levels
Appendix C. Implementation
Appendix D. Attenuation Factor of 14C and 13C
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| Parameter | Symbol | Value | SD ± |
| Turnover Time = ACO2 /AOUT | T | 14.9 yr | 1.7 |
| Fossil-fuel Inflow Fraction | AF | 0.54 | 0.11 |
| Nuclear Bomb Yield* | Yb | 1.60 | 0.1 |
| Rel. Reserve Size | RCO2 | 6.1 | 1.4 |
| 14C Pre-industrial | Δ14Cinit | -3.0‰ | 10‰ |
| 13C Pre-industrial | δ13Cinit | -6.7‰ | 0.2‰ |
| 13C fossil fuel | δ13Cff | -20.8‰ | 4‰ |
| Duration | 1750 - | 2020 | 1850 - | 2020 | 1960 - | 2020 | ||
| GTC | % | GTC | % | GTC | % | |||
| CO2FF Supplied | ||||||||
| CO2FF delivered to Atmos. (AF) | 246 | 54 | 245 | 54 | 202 | 45 | ||
| CO2FF delivered to Rsvr. (1-AF) | 208 | 46 | 207 | 46 | 170 | 38 | ||
| CO2FF Total | 454 | 100 | 452 | 100 | 372 | 82 | ||
| CO2FF Destination | ||||||||
| CO2FF present in Atmos. | 120 | 26 | 120 | 26 | 99 | 26 | ||
| CO2FF present in Rsvr. | 333 | 74 | 333 | 74 | 273 | 72 | ||
| CO2FF Total | 454 | 100 | 452 | 100 | 382 | 100 | ||
| Atmospheric Growth | ||||||||
| Atmos. CO2 Growth due to CO2FF | 120 | 43 | 120 | 44 | 99 | 49 | ||
| Atmos. CO2 Growth due to non-Foss* | 162 | 57 | 152 | 56 | 104 | 51 | ||
| Atmospheric Growth Total | 282 | 100 | 272 | 100 | 204 | 100 | ||
| Reservoir Growth | ||||||||
| Reservoir Growth due to CO2FF | 333 | 333 | 273 | |||||
| Reservoir Growth due to non-Foss* | -158 | -143 | -97 | |||||
| Reservoir Growth Total | 171 | 185 | 171 | |||||
| Atmospheric Outflow | ||||||||
| Atmos Outflow CO2FF | 292 | 291 | 245 | |||||
| Atmos Outflow non-Foss | 11473 | 7459 | 2806 | |||||
| Atmospheric Outflow Total | 11765 | 7750 | 3051 | |||||
| Reservoir Outflow | ||||||||
| Reservoir Outflow CO2FF | 166 | 166 | 143 | |||||
| Reservoir Outflow non-Foss | 11636 | 7606 | 2907 | |||||
| Reservoir Outflow Total | 11802 | 7772 | 3050 | |||||
| CO2FF rel. to CO2 atmos. 2020† (%) | 120/876 | 13.7 | 120/876 | 13.7 | 99/876 | 11.3 | ||
| Average Annual Flux from Reservoir | 43.77 | 45.79 | 50.96 | |||||
| Average Annual Flux to Reservoir | 43.63 | 45.67 | 50.99 |
Data References
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