W. Hickel et al., THE HUMAN IMPACT IN THE GERMAN BIGHT - EUTROPHICATION DURING 3 DECADES (1962-1991), Helgolander Meeresuntersuchungen, 47(3), 1993, pp. 243-263
The human impact in the German Bight, in the form of anthropogenic eut
rophication, has been documented by a 30-year time-series measurement
near the island of Helgoland. Since 1962, the Biologische Anstalt Helg
oland has measured inorganic nutrients and phytoplankton abundance fro
m daily samples at Helgoland Roads, a position 60 km off the main sour
ce of eutrophication, the River Elbe. Since the early 'sixties, phosph
ate concentrations rose for about a decade, levelling off to about twi
ce the former concentrations for another decade, and then decreasing (
since 1982) as a result of phosphate-reducing measures. Nitrate concen
trations, however, have only increased since 1980/81, following Elbe r
iver flood events. In 1987, three times the former concentrations were
reached. A decrease has been observed only since 1991. This different
development of phosphorus and nitrogen eutrophication led to a shift
of inorganic N/P-ratios in the German Bight. The phosphate increase wa
s more pronounced in the late summer ''regeneration made'' conditions,
the nitrate increase in the winter months. The eutrophication is not
restricted to the inner German Bight and coastal waters of a salinity
of < 33, but has also occurred in more saline waters at S > 33 psu (pr
actical salinity unit), as characteristic for the outer German Bight.
In this more saline water, phosphate and nitrate maximum levels occurr
ed three years later, compared with the average Helgoland data, which
are more representative of the inner German Bight. It is suggested tha
t suspended particulate organic matter, as a long-distance carrier of
nutrients, might have caused this delayed eutrophication in the outer
German Bight waters. While the human impact is obvious as to nutrient
concentrations, it is less obvious in phytoplankton stock enhancement.
A general increase in phytoplankton biomass (about 3-4 times) was fou
nd, but this was mainly due to unidentified nanoflagellates of unknown
trophic state, and subject to methodological errors. The causal relat
ionships of phytoplankton stocks and eutrophication are not clearly un
derstood, as natural variability is large and hydrographical factors p
ossibly dominate. Additional nutrient input by Elbe river floods did n
ot always result in elevated phytoplankton stocks near Helgoland, whil
e extended periods of vertical density stratification of the German Bi
ght water caused large plankton blooms.