The Soils of The Regional Municipality of Ottawa=Carleton
The Soils of The Regional Municipality of Ottawa=Carleton
The Soils of The Regional Municipality of Ottawa=Carleton
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graphic regions . <strong>The</strong>refore, the C values for specific crops in<br />
Ottawa-Carleton, calculated on the basis <strong>of</strong> climatic, crop<br />
andmanagementdatafrom this region, will not necessarily be<br />
the same ad C values for the same crops that are developed for<br />
other areas in Ontario .<br />
<strong>The</strong> C factor represents the components <strong>of</strong> sheet and rill<br />
erosion which are most easily controlled or modified through<br />
management ; whereas the given attributes <strong>of</strong> a field or area,<br />
namely the climate (or more specifically the annual erosive<br />
rainfall), soils and landscape are represented by the R, K and<br />
LS components <strong>of</strong> the USLE, respectively .<br />
Information on crop and management practices specific<br />
to the Ottawa-Carleton region was obtained from agricultural<br />
extension personnel . This included information on the<br />
amount and quality <strong>of</strong> soil protection provided during and<br />
between crops ; the type and timing <strong>of</strong> tillage operations ; and<br />
estimated seedbed preparation, planting, and harvest dates .<br />
<strong>The</strong> climatic information was obtained from previouslypublished<br />
erosion indices (30) .<br />
Basically, a C factor is the ratio between the amount <strong>of</strong><br />
soil eroded from a field under a specific crop and management<br />
system to the amount <strong>of</strong> soil which would be eroded<br />
from the same field kept in a bare, continuously fallow state .<br />
C factor values range from 0 to 1 . A value <strong>of</strong> 1 represents a<br />
bare, continuously-fallow condition . When this value is<br />
applied to the rest <strong>of</strong> the equation, the soil loss calculated<br />
form the physical attributes alone (RKLS) essentially remains<br />
the same . However, as the value <strong>of</strong> C approaches 0, this represents<br />
an increasingly greater reduction inthe potential erosion<br />
due to the effects <strong>of</strong> the crop and management systems . An<br />
extreme C value <strong>of</strong> approximately 0 would indicate that the<br />
crop and management system has virtually eliminated the<br />
chance <strong>of</strong> erosion occurring .<br />
C values that are between the two extremes represent the<br />
proportion by which the soil loss from a bare field would be<br />
reduced under an alternative crop and/or management sys<br />
tem . For example, a C value <strong>of</strong> 0.50 (conventional fall tillage<br />
<strong>of</strong> silage corn following field crops, see Table 17) indicates<br />
that this type <strong>of</strong> crop and management practice reduces the<br />
long-term, average annual potential erosion to 50 010 <strong>of</strong> that<br />
which would have occurred on bare soil. If all other factors<br />
are held constant, a winter wheat crop (C = 0 .27) planted on<br />
the same field after conventional tillage in the fall would<br />
reduce the potential erosion to 27 076, compared to the loss<br />
during bare soil conditions . Potential soil losses would be<br />
reduced to 2 016 if alfalfa (C = 0.02) were present onthe field .<br />
Generally, C values are lowest (ie . reflect good erosionreducing<br />
potential) for crop and management systems that<br />
cover and protect the soil for the longest period <strong>of</strong>time, espe<br />
cially during peak annual rainfall periods . Good crop growth,<br />
a high percent final canopy cover, residues <strong>of</strong> plant materials<br />
left in the soil and practices whichleave residue on the surface<br />
alsocontribute to relatively low C values .<br />
Table 16. LS-values for different combinations <strong>of</strong> slope length and slope gradient<br />
Slope<br />
Gradient<br />
Percent 10 15 20 25 30 40<br />
Slope Length (m)<br />
SO 60 75 100 125 150 200 250 300<br />
0 .2 .063 .069 .073 .076 .080 .084 .088 .091 .095 .101 .105 .109 .116 .121 .125<br />
0 .5 .076 .083 .088 .092 .095 .101 .105 .109 .114 .121 .126 .131 .139 .145 .151<br />
0 .8 .090 .098 .104 .108 .112 .119 .124 .129 .135 .143 .149 .155 .164 .172 .178<br />
2 .144 .162 .177 .189 .200 .218 .233 .246 .263 .287 .307 .324 .353 .377 .399<br />
3 .205 .232 .253 .270 .285 .311 .333 .351 .376 .410 .438 .463 .504 .539 .570<br />
4 .256 .301 .338 .369 .397 .446 .487 .524 .573 .643 .703 .756 .849 .928 .998<br />
5 .306 .375 .433 .485 .531 .613 .685 .751 .839 .969 1 .08 1 .19 1 .37 1 .53 1 .68<br />
6 .385 .472 .545 .609 .667 .770 .861 .943 1 .05 1 .22 1 .36 1.49 1.72 1 .93 2.11<br />
8 .568 .695 .803 .898 .983 1 .14 1 .27 1 .39 1 .56 1 .80 2 .01 2 .20 2 .54 2.84 3 .11<br />
10 .784 .960 1 .11 1 .24 1 .36 1.57 1 .75 1 .92 2.15 2 .48 2 .77 3.04 3.51 3.92 4.29<br />
12 1 .03 1.27 1 .46 1 .63 1 .79 2 .07 2 .31 2.53 2.83 3 .27 3 .65 4 .00 4 .62 5.17 5.66<br />
14 1 .13 1.61 1.86 2.08 2.28 2 .63 2.94 3.22 3.60 4.16 4 .65 5.09 5.88 6.57 7.20<br />
16 1 .63 1 .99 2.30 2 .57 2.82 3 .25 3 .63 3.98 4.45 5 .14 5 .75 6.30 7 .27 8.13 8.90<br />
18 1.97 2.41 2.78 3 .11 3 .41 3.93 .4.40 4.82 5.39 6.22 6 .95 7.62 8.80 9 .83 10 .8<br />
20 2 .34 2.86 3.30 3 .69 4 .05 4 .67 5 .22 5.72 6.40 7.39 8.26 9 .05 10.4 11 .7 12 .8