04.03.2014 Views

Poland - IOW

Poland - IOW

Poland - IOW

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Material and Methods 21<br />

f<br />

=<br />

S<br />

P<br />

− S<br />

S<br />

P<br />

MIX<br />

[2.4b]<br />

Water column end-members were calculated from the means of all water column samples<br />

during each campaign. As groundwater end-member the well samples were used. In addition<br />

mixing was calculated with pore water samples with the lowest salinity during each sampling<br />

campaign as groundwater end-member. However, pore water samples present no true<br />

groundwater end-members. As they all had salinities >0, f had to be adapted as followed:<br />

f<br />

=<br />

S<br />

S<br />

P<br />

P<br />

− S<br />

− S<br />

MIX<br />

GW<br />

[2.4c]<br />

The conservative mixing of 15 N-NH 4 + values (δ MIX ) was calculated as well:<br />

δ<br />

MIX<br />

=<br />

f<br />

∗C<br />

GW<br />

∗δ<br />

GW<br />

+<br />

C<br />

( 1−<br />

f )<br />

MIX<br />

∗C<br />

P<br />

∗δ<br />

P<br />

[2.4d]<br />

δ denotes the NH + 4 isotopic values. End-members were achieved in the same way as for<br />

concentration mixing.<br />

Deviations of actual samples from the theoretical conservative mixing lines indicate<br />

additional sources or sinks in the mixing gradient. For the concentration mixing that means<br />

higher values than predicted point towards additional sources and lower values towards<br />

additional sinks.

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!