COMPARING METEORIC 10BE, IN SITU 10BE AND NATIVE 9BE ACROSS THREE WATERSHEDS
We leached 9Be from 206 samples by reacting powdered sands in 6M HCl for 24 hours while reacting in a heated ultrasonic bath – a method that did not leach 9Be in mineral grains. This is significant because 9Be in grain coatings is subject to the same post-depositional influences as 10Bemet, while 9Be incorporated into mineral matrixes is uninfluenced by post-depositional conditions, similar to 10Beis. The leachate was analyzed by ICP-OES.
Samples show different 10Bemet /9Be correlations with 10Beis across sampling locations. Samples from the Mekong River watershed in China have a positive correlation between 10Beis and 10Bemet (R2=0.46, n=119) and a stronger positive correlation between 10Beis and 10Bemet/9Be (R2=0.69). Samples from the Barron River Watershed in Queensland Australia have no correlation between 10Beis and 10Bemet (R2=0.05, n=16) but a positive correlation between 10Beis and 10Bemet/9Be (R2=0.56). Samples from the Potomac River Watershed in east-central North America show no correlation between 10Beis and 10Bemet (R2=0.06, n=71) or 10Beis and 10Bemet/9Be (R2=0.00). Considering all data, correlations between 10Bemet/9Be ratios and 10Beis (R2=0.70, n=206) are only slightly stronger than correlations between 10Beis and 10Bemet (R2=0.66). These results suggest that while measuring 9Be can improve correlations between 10Bemet and 10Beis, further study is needed to understand the variables that influence Be dynamics across a diversity of watersheds.