Abstract

Abstract. Kirchner (2016a) demonstrated that aggregation errors due to spatial heterogeneity, represented by two homogeneous subcatchments, could cause severe underestimation of the mean transit times (MTTs) of water travelling through catchments when simple lumped parameter models were applied to interpret seasonal tracer cycle data. Here we examine the effects of such errors on the MTTs and young water fractions estimated using tritium concentrations in two-part hydrological systems. We find that MTTs derived from tritium concentrations in streamflow are just as susceptible to aggregation bias as those from seasonal tracer cycles. Likewise, groundwater wells or springs fed by two or more water sources with different MTTs will also have aggregation bias. However, the transit times over which the biases are manifested are different because the two methods are applicable over different time ranges, up to 5 years for seasonal tracer cycles and up to 200 years for tritium concentrations. Our virtual experiments with two water components show that the aggregation errors are larger when the MTT differences between the components are larger and the amounts of the components are each close to 50 % of the mixture. We also find that young water fractions derived from tritium (based on a young water threshold of 18 years) are almost immune to aggregation errors as were those derived from seasonal tracer cycles with a threshold of about 2 months.

Highlights

  • Environmental tracers are commonly used to obtain transit time distributions (TTDs) in groundwater systems (Małoszewski and Zuber, 1982) or catchments (McDonnell et al, 2010)

  • We first demonstrate the relationships between mean transit time and tritium concentration for mixed systems (Fig. 3) by assuming constant annual input tritium concentration of 2 TU over time, i.e. without the bomb pulse during the nuclear age and only natural background concentrations are present

  • The red points indicate the assumed water components and the red dashed line is the mixing relationship between them described by Eqs. (9) and (12)

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Summary

Introduction

Environmental tracers are commonly used to obtain transit time distributions (TTDs) in groundwater systems (Małoszewski and Zuber, 1982) or catchments (McDonnell et al, 2010). TTDs provide important information about transport, mixing, and storage of water in systems and on the retention and release of pollutants. Mean transit times (MTTs) determined from these distributions provide practical information for various aspects of water resources management. MTTs have been used to estimate the volume of groundwater storage providing baseflow in catchments (Morgenstern et al, 2010; Gusyev et al, 2016) and to predict lag times and life expectancies of contaminants in the subsurface (Hrachowitz et al, 2016). The drinking water securities of wells in New Zealand are partly assessed by an absence of water with less than 1-year travel time by the New Zealand drinking water

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