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Trail:

Ecosystems

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Scientific papers - Ecosystems - Page 4 


 
2. Colorado CWD cluster (Tables 2 & 3)
 
Herbage drawn from an 80 mile cross section of the CWD endemic cluster zone in North central Colorado (Fig. 4) consistently demonstrated excessive levels of the divalent cation, calcium, at 1.19% total dry matter. However, the levels of Mn recorded in this specific batch of herbage/soil samples were low; averaging out at 39.5 mg/kg in herbage and 9.3 ppm in the soil. These samples were drawn during the drought conditions of July 1998 following three months of dry weather. (NB. Soil Mn is rendered considerably less available during drought conditions (31) whilst the protracted daylight of the mid summer period decreases levels of Mn in plant tissues (65). However, soil sampling carried out the previous autumn on 13-25 October 1997 across the CWD cluster zone - following a period of rain and snow - recorded considerably higher levels of Mn averaging out at 317 mg/kg from the same test locations. It is possible that the recent increase in acid rainfall occurring along the CWD section of the Front Range during the winter rain/snow season is also assisting an increased uptake of 'available Mn' from the soil into the herbage. Ca also averaged high concentrations of 2.55% dry matter in the autumn 1997 tests.

Table 2   Analyses of herbage samples drawn across the CWD-endemic region of the Colorado Front Range on 12/7/98 - 16/7/98; readings in mg/kg dry basis, unless marked % w/w dry basis

Location
N%
K%
Ca%
Cu
Fe
Mo
Se
P%
Mg%
Mn
Na%
Zn
B
Co
CWD region
 
1     Horsetooth
1.66
1.89
0.77
5.8
84.8
0.10
.080
.15
.2
 38
.01
19.0  
19.8
.090
  5     Owl Canyon
2.63
1.46
2.04
9.1
80.7    
2.03
.250
.21
.40
30
.01
19.2    
36.6
.160
  6     Poudre Canyon
1.54
1.67
0.76
5.0
69.7    
0.16
.240
.19
.18
37
.00
19.7    
19.6
.110
  7     Teds Place
5.03
5.81
2.05
7.1
194.8    
1.68
.065
.40
.40
44
.01
25.9    
42.9
.220
  9     Black Canyon
2.21
1.83
0.71
6.6
365.7    
1.06
.064
.26
.16
50
.00
105.7    
18.2
.040
12     H-Bar-G Ranch
1.76
1.92
0.83
5.6
131.9    
1.16
.270
.24
.19
38
.00
45.0    
21.9
.050
        Av CWD
2.47
2.43
1.19
6.5
154.6    
1.03
.161
.24
.25
40
.005
39.0    
26.5
.111
Category
mean
mean
very
high
low
mean
mean
low
low
low
mean
very
low
low
mean
mean

Levels of Al/S/V/Ni/Cr/F/As/Cd/Pb/Sn were normal at all sites tested.

Table 3   Analyses of top soils drawn across the CWDcluster zone of the North Central Colorado Front Range and a CWD-free zone in Utah on 12-16/7/98 and 20/9/97 respectively

Test Site
pH
P
K
Mg
Cu
B
Na
Zn
Ca
Mo
Fe
S
Se
Mn
Mn
CWD ZONE COLORADO
(1997)
 1     Horsetooth Mt
7.0
6.0
250
309   
1.4
0.7
3.3
1.0
2576
0.0
14   
36.7 
.09 
6.4  
333  
  2     Spring Creek
6.6
3.8   
115
167   
1.3
0.4
2.4
0.9
1541
0.1
28   
23.1
.18
15.0   
261   
  3     Horsetooth Re
6.8
4.0   
101
280   
0.8
0.5
3.5
0.9
1635
0.1
22   
27.1
.24
8.0   
300   
  4     Livermore
8.7
5.4   
290
72   
1.0
0.8
1.4
1.1
2833
0.0
2   
34.4
.09
2.0   
373   
  5     Owl Canyon
8.6
6.0   
221
153   
0.8
0.7
5.2
0.9
3777
0.1
11   
32.9
.18
5.0   
229   
  6     Poudre Canyon
7.4
7.4   
247
97   
2.7
0.7
2.0
2.8
1512
0.0
16   
24.1
.10
9.0   
465   
  7     Teds Corner
6.8
25.4   
506
99   
2.5
0.8
3.9
3.0
2251
0.1
37   
33.2
.19
18.0   
320   
  8     Bellvue
8.3
29.2   
236
248   
2.1
1.0
9.9
1.7
3295
0.1
9   
42.9
.13
3.0   
99   
  9     Black Canyon
6.7
29.4   
395
170   
3.8
0.8
4.3
9.1
1418
0.3
50   
21.9
.16
20.0   
329   
10     Black Canyon
6.4
5.6   
175
146   
0.9
0.5
3.1
1.5
1822
0.3
51   
19.2
.16
10.0   
468   
11     H-Bar-G Ranch
6.6
6.6   
249
150   
1.3
0.5
1.9
0.8
1194
0.1
29   
17.0
.06
7.0   
341   
12     H-Bar-G Ranch
6.5
4.8   
167
110   
1.4
0.5
3.5
2.9
1260
0.1
38   
18.7
.12
8.0   
293   
 
        Av CWD
7.2
10.6   
246
166   
1.6
0.6
3.7
2.2
2093
0.1
25   
27.6
.14
9.3   
317   
        Category
high
low
mean
mean
very
low
low
very
low
mean
mean
low
high
mean
low
mean
very high
 
CWD-FREE UTAH
Gt Cottonwood
7.6
11.4   
194
177   
10.7   
0.6
275
61   
2056
0.2
52   
67.7
.26
25.0   
 
Lt Cottonwood
7.2
9.4   
 91
75   
5.1   
x
x
8   
x
1.3
88   
x
x
32.0   
 
Av CWD-free
7.4
10.4   
142
126   
7.9   
0.6
275
35   
2056
0.7
70   
67.7
.26
25.0   
 
Category
mean
low
low
mean
high
low
high
high
very
mean
mean
high
very
high
very
high
mean
high
 

 

All samples analysed by National Resources Management Ltd on dry basis. x = insufficient sample for test
Cu/Zn were as EDTA extractable mg/l.
Na/Ca/K/Mg were as ammonium nitrate extractable mg/l.
Fe/Mn were as DPTA extractable mg/l.
B as hot water soluble Mg/l.
Mo as Tamms extractable mg/l.
S as available phosphate buffer soluble mg/l.
Se as 'total' mg/kg.
P as sodium bicarbonate extractable mg/l
Levels of Sn/Hg/F/I/Cr/Ni/Co/Pb/As/Al/V/Cd were normal at all locations tested.

However, soil sampling carried out the previous autumn on 13-25 October 1997 across the CWD cluster zone-following a period of rain and snow - recorded considerable higher levels of Mn averaging out at 317 mg/kg from the same test locations. It is possible that the recent increase in acid rainfall occurring along the CWD section of the Frong Range during the winter rain/snow season is also assisting an increased uptake of 'available Mn' from the soil into the herbage. Ca also averaged high concentrations of 2.55% dry matter in the autumn 1997 tests. Interestingly, local ranchers in the CWD zone consider that the increased incidence rate of CWD correlates with the increase in population density of deer and elk in the 'Rocky Mountain National Park' region - the epicentre of the CWD cluster. They also report an increase in the consumption of pine needles by deer/elk in the overpopulated region, who have progressively switched onto this abnormal substitute ration since competition for the limited supplies of normal foods has increased. Pine needles contain high concentrations of certain cations, particularly in acid rainbelt districts: Mn being recorded at excessive concentrations ranging between 214-5810 p.p.m. (67).
 


Fig. 4   Mapdepicting sample locations of the comparative study between
the scrapie endemic and scrapie-free valleys near SKURETRI, N. Iceland.
Sample numbers correspond with the numbered farms of Table 1.

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