Boron in the major UK rivers entering the North Sea is predominantly i
n dissolved form and concentrations show large variations in time and
space. The time-dependent feature relates to seasonal patterns linked
to flow. Boron concentrations are well described by a power relationsh
ip of the type [B] = aflow(b), where a and b are constants. In this e
quation, the a term varies from river to river in relation to the boro
n concentration at baseflow while the b term is of similar value for a
ll the rivers (around -0.5 to -0.6). The spatial variations are direct
ly linked to the degree of sewage discharge and the dilution associate
d with (i) rainfall events and (ii) the length of river reach from the
pollutant source. Boron concentrations exhibit simple chemically cons
erved water mixing behaviour. However, deviations between chloride and
boron indicate secondary chloride supplies from storm runoff, increas
ed boron contamination for part of the sampling period on one river (t
he Nidd) and possibly significant atmospheric inputs far the less poll
uted rivers. Preliminary estimates of riverine fluxes to the North Sea
are of the order of 1.6 Gg-B/year and the calculations indicate a rel
atively low rainfall component (about 25% for the cleaner rivers and m
uch lower values for the more polluted rivers). These preliminary esti
mates also indicate that about 92% of the riverine fluxes comes from t
he Humber rivers compared to the more northerly rivers. For the Humber
, preliminary estimates indicate that about 60% of the flux is associa
ted with detergent-related sources: historical mining activity may als
o provide an important source (e.g. mine drainage and land contaminate
d with fly ash and associated material disposal). This illustrates the
usefulness of boron as a tracer for non-biodegradable compounds from
anthropogenic sources. (C) 1998 Elsevier Science B.V.