Mj. Kemp et Wk. Dodds, Spatial and temporal patterns of nitrogen concentrations in pristine and agriculturally-influenced prairie streams, BIOGEOCHEMI, 53(2), 2001, pp. 125-141
Long-term data on nitrogen chemistry of streams draining Konza Prairie Biol
ogical Station (Konza), Kansas were analyzed to assess spatial and temporal
patterns and examine the influence of agricultural activity on these patte
rns. Upland watersheds of Konza are predominantly tallgrass prairies, but a
gricultural fields and riparian forests border the lower reaches of the str
eams. We have up to 11 years of data in the relatively pristine upland reac
hes and 4 years of data on wells and downstream reaches influenced by ferti
lized croplands. Seasonal and spatial patterns in total nitrogen (TN) conce
ntrations were driven largely by changes in the nitrate (NO3-) concentratio
ns. A gradient of increasing NO3- concentrations occurred from pristine upl
and stream reaches to the more agriculturally-influenced lowland reaches. N
itrate concentrations varied seasonally and were negatively correlated with
discharge in areas influenced by row-crop agriculture (p = 0.007). The NO3
- concentrations of stream water in lowland reaches were lowest during time
s of high precipitation, when the relative influence of groundwater drainag
e is minimal and water in the channel is primarily derived from upland prai
rie reaches. The groundwater from cropland increased stream NO3- concentrat
ions about four-fold during low-discharge periods, even though significant
riparian forest corridors existed along most of the lower stream channel. T
he minimum NO3- concentrations in the agriculturally influenced reaches wer
e greater than at any time in prairie reaches. Analysis of data before and
after introduction of bison to four prairie watersheds revealed a 35% incre
ase of TN concentrations (p < 0.05) in the stream water channels after the
introduction of bison. These data suggest that natural processes such as bi
son grazing, variable discharge, and localized input of groundwater lead to
variation in NO3- concentrations less than 100-fold in prairie streams. Ro
w-crop agriculture can increase NO3- concentrations well over 100-fold rela
tive to pristine systems, and the influence of this land use process over s
pace and time overrides natural processes.