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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 ...

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

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major wetland classes when ANOVA and Tukey-Kramer tests were performed using wetland<br />

surface area as a factor. However, size significantly differed between lacustrine and both<br />

palustrine and riverine sites as indicated by Kruskal-Wallace non-parametric analysis and Z tests<br />

(p = 0.006). When area (acres) was placed in a Pearson correlation matrix, it was found to<br />

correlate positively with orthophosphate (PO4), total phosphorus, and atrazine concentrations<br />

with all relationships being significant (p = 0.05). When robust linear regression analysis was<br />

performed, the relationships between area and both PO4 and total phosphorus concentrations<br />

were not significant and adjusted R 2 values were essentially zero. The relationship between area<br />

and atrazine concentrations remained significant, but the amount of variance explained was small<br />

(p = 0.013, R 2 = 0.10). Further analysis and discussion of the atrazine concentrations of the<br />

wetland population will consider the significance of this relationship.<br />

Depth to Flood<br />

Depth to flood (DTF) was used as a surrogate for flood return period. The value of DTF was<br />

calculated using the KARS floodplain model and defined as the river height above river channel<br />

height needed to create a surface connection to the wetland either by backfill or sidespilling at<br />

the topographically lowest wetland boundary (Kastens 2008). Kruskal-Wallace non-parametric<br />

medians analysis revealed that the riverine class (n = 6) was significantly lower in depth to flood<br />

than lacustrine (n = 21) or palustrine (n = 32) classes (p = 0.043, regular Z variables significant).<br />

This should be expected given that riverine sites are either backwater channels or sloughs that<br />

become connected with the Missouri River channel at much more frequent intervals than sites<br />

more set back from the channel. ANOVA and Kruskal-Wallace tests revealed significant<br />

differences in DTF between the sample populations within the Western Corn Belt <strong>Plains</strong> and the<br />

<strong>Central</strong> Irregular <strong>Plains</strong>. The mean DTF value for the CIP wetlands was 7.81 while the WCB<br />

wetland population had a mean value of 3.71. The Interior River Valleys and Hills sample<br />

population (n = 5) had a mean DTF value of 4.72, which was not significantly different from<br />

either the WCB or CIP wetland population values. The fact that DTF values positively<br />

correlated with the linear distance from the Missouri River channel (R 2 = 0.91, p < 0.001)<br />

reflects the fact that floodplain valley widens and contracts along its lower portion and that sites<br />

within the CIP have greater distances of overland flow and significantly less connectivity with<br />

the floodplain (Figure 22).<br />

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