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Koontz, J., D.G. Huggins, C.C. Freeman, D.S. Baker - Central Plains ...

Koontz, J., D.G. Huggins, C.C. Freeman, D.S. Baker - Central Plains ...

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CDF<br />

100<br />

90<br />

80<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

0 1 2 3 4 5 6 7<br />

atrazine µg/L<br />

Figure 37. Cumulative distribution frequency (CDF) of atrazine of in reference (Phase I) and<br />

random (Phase II) populations.<br />

Resampled sites<br />

Four sites were resampled from Phase I (2005) and Phase II (2008); only three have all tiers of<br />

assessment data. Forney Lake, which lies in the Western Corn Belt <strong>Plains</strong>, was completely<br />

drained during summer 2005 when this area experienced drought conditions. Only disturbance<br />

assessments and FQA data were obtained there. The disturbance assessment score for 2005 and<br />

2008 were very similar, 12 and 13 respectively. FQI was 12.02 in 2005 and 16.26 in 2008.<br />

Richness values in 2005 (40 all plants, 32 native plants) were considerably higher than in 2008<br />

(18 for both). The dramatic difference in the scores is undoubtedly a consequence of the<br />

hydrological disturbance of drought and deluge, which promotes changes in plant community<br />

diversity. In 2005 there was only one hydrophyte species reported; there were six in 2008. The<br />

most dramatic shift in plant community structure was seen in the number of therophytes<br />

(annuals) present, which dropped from 20 in 2005 to one in 2008. Manipulation of wetland<br />

water level has been one of the most endearing best management practices for maintaining<br />

wetland floristic quality (Mitsch and Gooselink 2008).<br />

The other three sites are located in the <strong>Central</strong> Irregular <strong>Plains</strong> ecoregion and all three assessment<br />

tiers were accomplished during both survey phases. Swan Lake is a lacustrine, unconsolidated<br />

bed wetland type. There were noticeable differences in floristic and water quality as well as<br />

macroinvertebrate MMI scores. Though there are differences in the disturbance assessment<br />

scores, the difference is limited considering that scoring was reported by a different evaluator<br />

each year. In 2005 the disturbance assessment score was 12; in 2008 it was 14, with the most<br />

changes occurring in the hydrological attributes section – a section that be expected to change<br />

somewhat due to differing climatic conditions. Floristic quality assessments and<br />

macroinvertebrate metric indices indicated that this site had become more degraded in overall<br />

quality over the three-year period. Water chemistry measures show a trend in higher<br />

concentrations of nutrients and lower pesticide concentrations in the 2005 sampling season. It is<br />

52 of 84<br />

Phase One<br />

Phase Two

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