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Summary schematic of karst landscape and speleothem formation. CO 2 from the atmosphere, root-respiration, and decomposition of soil organic matter (SOM) is dissolved into groundwater and speciates into carbonic acid (H 2 CO 3 ) and bicarbonate (HCO 3- ). H 2 CO 3 is responsible for the dissolution of limestone and the incorporation of Ca 2+ , CO 32- and additional HCO 3- into solution. The water subsequently percolates into a cave, which ventilates seasonally, and CO 2 is degassed from solution into low- p CO 2 cave-air driving the precipitation of calcite (CaCO 3 ). 

Summary schematic of karst landscape and speleothem formation. CO 2 from the atmosphere, root-respiration, and decomposition of soil organic matter (SOM) is dissolved into groundwater and speciates into carbonic acid (H 2 CO 3 ) and bicarbonate (HCO 3- ). H 2 CO 3 is responsible for the dissolution of limestone and the incorporation of Ca 2+ , CO 32- and additional HCO 3- into solution. The water subsequently percolates into a cave, which ventilates seasonally, and CO 2 is degassed from solution into low- p CO 2 cave-air driving the precipitation of calcite (CaCO 3 ). 

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Speleothems (cave calcite deposits) are a well-recognized terrestrial paleoclimate proxy. The most commonly constructed records from speleothem geochemical data are made from the measurement of stable oxygen isotope ratios (δ18O). This is most often accomplished by the analysis of CO2 on a gas-source IRMS, also allowing for the simultaneous measure...

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... runoff events into the cave entrance) or as groundwater. This source water then travels through the soil horizon, into the epikarst (a highly weathered/fractured portion of the host-rock), the host-rock, and into caves ( Figure 1). Fairchild et al. (2006) combined these zones into the dissolution region and the precipitation region. ...
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... CO 2 concentrations, δ 13 C s values, and δ 13 C r values also varied temporally during the period of study. δ 13 C r varied only slightly (< 1‰; Table 2), while δ 13 C s varied seasonally with the highest values measured during the summer (Figure 9, Figure 10).  13 C r values calculated using Davidson's (1995) equation were indistinguishable from values calculated from Keelng plot y-intercepts ( Figure 11). ...
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... 13 C r varied only slightly (< 1‰; Table 2), while δ 13 C s varied seasonally with the highest values measured during the summer (Figure 9, Figure 10).  13 C r values calculated using Davidson's (1995) equation were indistinguishable from values calculated from Keelng plot y-intercepts ( Figure 11). ...
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... δ 13 C s values are consistent with two-endmember mixing between atmospheric CO 2 (regional measured average δ 13 C surface = -9.0 ± 0.1‰ and pCO 2 = 397 ppm) and soil-respired CO 2 (where δ 13 C r = δ 13 C s -4.4‰; Figure 11). If the soil CO 2 concentration is above ~4000 ppm, then the atmospheric component would represent less than 10% of soil CO 2 and have a small effect (based on our data ~0.5 to 1‰) on δ 13 C s . ...
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... we contrast the values of juniper δ 13 C s with predicted equilibrium CO 2 δ 13 C values (calculated from directly-sourced δ 13 C DIC ), we find a small difference during the central Texas summer (Figure 9, Figure 10). With the persistence of severe drought conditions through these months soil pCO 2 was significantly lower, likely as a result of decreased plant productivity and significant plant death (Figure 9, Figure 10). ...
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... we contrast the values of juniper δ 13 C s with predicted equilibrium CO 2 δ 13 C values (calculated from directly-sourced δ 13 C DIC ), we find a small difference during the central Texas summer (Figure 9, Figure 10). With the persistence of severe drought conditions through these months soil pCO 2 was significantly lower, likely as a result of decreased plant productivity and significant plant death (Figure 9, Figure 10). During this low-pCO 2 season, the relative contribution of atmospheric CO 2 , to total soil CO 2 increased and the depth where soil CO 2 only records biologic CO 2 shifted to greater depths in the soil profile (Figure 9, Figure 10). ...
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... the persistence of severe drought conditions through these months soil pCO 2 was significantly lower, likely as a result of decreased plant productivity and significant plant death (Figure 9, Figure 10). During this low-pCO 2 season, the relative contribution of atmospheric CO 2 , to total soil CO 2 increased and the depth where soil CO 2 only records biologic CO 2 shifted to greater depths in the soil profile (Figure 9, Figure 10). With the return of precipitation and lower surface temperatures subsequent to drought conditions, there was a strong response in the amount of live vegetation present, increased soil pCO 2 , and convergence of δ 13 C s and equilibrium drip water CO 2 values (Figures 8, 10). ...
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... this low-pCO 2 season, the relative contribution of atmospheric CO 2 , to total soil CO 2 increased and the depth where soil CO 2 only records biologic CO 2 shifted to greater depths in the soil profile (Figure 9, Figure 10). With the return of precipitation and lower surface temperatures subsequent to drought conditions, there was a strong response in the amount of live vegetation present, increased soil pCO 2 , and convergence of δ 13 C s and equilibrium drip water CO 2 values (Figures 8, 10). Given that soil profiles in central Texas are thin (typically 30-45 cm thick), our deepest soil gas well was 34 cm. ...
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... et al. (1999) documented juniper roots at NB that extended at least 9 m into the subsurface and oak roots as deep as ~25 m. Sampling sites within the cave are located in a chamber approximately 40 m below the surface, which would allow a large distance for vadose groundwater to equilibrate with plant root respired CO 2 (modified by diffusion) before it enters the cave (Figure 14). ...
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... contrast our work with δ 13 C DIC values of drip water in other caves, we compiled the maximum range of available drip water δ 13 C values from studies in Gibraltar, Italy, Austria, and Florida ( Figure 16 production in the soil horizon and/or epikarst must also be sufficiently high to overwhelm host-rock and PCP inputs. Therefore, in these caves we hypothesize that the primary control on the carbon isotope composition of drip water is respiration from the dominant deeply-rooted vegetation in the region and any subsequent change in δ 13 C DIC must occur via processes within the cave. ...
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... conditions conducive to CO 2 degassing from drip water, any drip site where T total is maximized should elicit a shift in δ 13 C cc (on the order of ~0.47‰/hour; Figure 15) temporally that would be measurable in a speleothem calcite record. One mechanism to increase T total would be to modify the flow path that drip water follows after entering the cave and prior to falling onto a speleothem. ...
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... further explore the influence of T total on δ 13 C DIC we evaluated drip rate variability over the same interval of the modern calcite record produced by Feng et al. (in prep.), and found covariation between δ 13 C cc and drip-rate ( Figure 18). We contrasted this observation with drip water data from St. Michaels Cave, Gibraltar (Mattey et al., 2010) and for at least one drip site observed a similar covariation between drip-rate and δ 13 C DIC values, which we would expect to be 'translated' into equal-magnitude variations in δ 13 C cc (Figure 19). ...
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... further explore the influence of T total on δ 13 C DIC we evaluated drip rate variability over the same interval of the modern calcite record produced by Feng et al. (in prep.), and found covariation between δ 13 C cc and drip-rate ( Figure 18). We contrasted this observation with drip water data from St. Michaels Cave, Gibraltar (Mattey et al., 2010) and for at least one drip site observed a similar covariation between drip-rate and δ 13 C DIC values, which we would expect to be 'translated' into equal-magnitude variations in δ 13 C cc (Figure 19). For the other drip sites in the Mattey et al. (2010) study we saw a trend between drip-rate and the magnitude of carbon isotope variations. ...
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... highest magnitude changes in δ 13 C cc occurred when pCO 2 and drip-rate were at a minimum (e.g. January 2006 and January 2008) Figure 19. Drip-rate and δ 13 C cc covariation adapted from Mattey et al. (2010) at the Flowstone drip site. ...

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