N and P in B. Everett Jordan Reservoir
The figure below is from a post-impoundment survey
of Jordan Lake by U. N. C. - Chapel Hill scientists.
The station was located near the Vista Point park area
between US 64 and the dam on the New Hope River arm of the lake.
Background Information about the Data
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These are graphs of oxygen and nutrient chemicals at a single
station in Jordan Lake over time.
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Notice that the time course (X-axis) is three years, and
that
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only alternate months are labeled.
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These three years were the first three after the new dam
was closed and the reservoir filled completely.
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Each chemical is on a separate graph.
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The two lines on each graph represent data from the surface
water and from water near bottom.
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At "Conservation Pool" (usual sustained water level of the
lake), the station was about 5 m deep.
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At this depth, the bottom sample was usually below a summer
thermocline.
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However, cool, stormy weather or high runoff could mix the
lake as deep as 5 m, even in summer.
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Data were taken approximately once a month.
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At this interval, short-term events such as temporary summer
mixing may not have shown up in the data.
Nutrient Behaviors
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Oxygen and ammonia graphs show when the lake was thermally
stratified
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Shallow and deep water concentrations diverged.
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Why was oxygen lower near the bottom?
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Why was oxygen higher in winter months than in summer months
near the surface?
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What do the oxygen data reveal about the process of fall
overturn in Jordan Lake?
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How do you explain the relationships between oxygen and ammonia
concentrations through seasonal cycles?
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Why was ammonia / ammonium ion higher near the bottom?
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What processes might tie low oxygen to high ammonia?
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Nitrite + nitrate did not differ between surface and near-bottom
levels.
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However, they oscillated strongly with season, dropping to
very low concentrations during summer.
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Were the same processes causing the oscillations at both
shallow and deep levels, or did different processes produce the similar
patterns independently?
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Total phosphorus concentrations appeared to be relatively
low most of the time.
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Remember that total P will include all inorganic and organic,
all dissolved and all particulate, all living and all non-living forms
of phosphorus. Contrast this with the nitrogen data, which cover
only two of the dissolved, inorganic forms.
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Sustained TP concentrations were actually fairly high for
a lake, between 20 and 50 mg L-1
at the surface in mid-summer.
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They look low because of the large "spike" of TP near bottom
in July 1983.
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Nutrient concentrations are often very high in new reservoirs,
but then decline over the next few years as the water and inundated soils
reach a new equilibrium.
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Why do you think TP was generally at its highest levels for
the year near bottom in late summer?
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What is the relationship between dissolved oxygen and TP
concentrations near bottom?
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How do you explain the January 1984 increase in TP at both
surface and deep levels?
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N:P ratios can indicate which of these two nutrients is most
likely to be limiting phytoplankton primary production at any given place
and time.
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You do not have information in these graphs about organic
N, but compare the (nitrite+nitrate+ammonia)/TP ratio.
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During which time intervals do you think N was probably an
important limiting factor for algal primary production?
Maintained by Sam Mozley, s_mozley@ncsu.edu
Last revised October 6, 2000