My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
GENERAL31841
DRMS
>
Back File Migration
>
General Documents
>
GENERAL31841
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 7:54:44 PM
Creation date
11/23/2007 7:06:42 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
General Documents
Doc Date
7/22/1999
Doc Name
FINAL ENVIRONMENTAL IMPACT STATEMENT VOLUME 2 APPENDIX L
Media Type
D
Archive
No
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
78
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
8 <br />essential behavior patterns, such as breeding, feeding, and <br />sheltering. <br />Osmundson and Burnham (1996) summarized the status and trend of the <br />Colorado River population of Colorado pikeminnow. Thee found that <br />numbers were low but new individuals were actively recruiting to the <br />adult population, and recruitment largely occurs in pulses from <br />infrequent strong year classes. These investigators concluded that <br />low adult numbers and infrequent pulsed recruitment make this <br />population vulnerable to extirpation over time from both natural <br />fluctuations in numbers as well as from continued changes in habitat. <br />Life History <br />The life-history phases that appear to be most critical for the <br />Colorado pikeminnow include spawning, egg hatching, development of <br />larvae, and the first year of life. These phases of Colorado <br />pikeminnow development are tied closely to specific habitat <br />requirements. Natural spawning of Colorado pikeminnow is initiated on <br />the descending limb of the annual hydrograph as water temperatures <br />approach or exceed 20° C (Vanicek and Kramer 1969, Hamman 1981, Haynes <br />et al. 1984, Tyus 1990, McAda and Kaeding 1991). Temperature at <br />initiation of spawning varies somewhat by river: in t:he Green River, <br />spawning begins as temperatures exceed 20-23° C; in the: Yampa River, <br />16-23° C (Bestgen et al. 1998); in the Colorado River, 18-22° C (McAda <br />and Kaeding 1991) Spawning, both in the hatchery and under natural <br />riverine conditions, generally occurs in a 2-month time frame between <br />late June and late August. However, in the natural system, sustained <br />high flows during wet years may suppress river temperatures and extend <br />spawning into September (MCAda and Kaeding 1991). Conversely, during <br />low flow years, when the water warms earlier, spawning may commence in <br />mid June. <br />Temperature also has an effect on egg development and :hatching <br />success. In the laboratory, egg development was tested at five <br />temperatures and hatching success was found to be highest at 20° C, <br />lower at 25° C, and mortality was 100 percent at 5, 10, 15, and 30° C. <br />In addition, larval abnormalities were twice as high at 25° C than at <br />20° C (Marsh 1985). <br />Experimental tests of temperature preference of yearling (Black and <br />Bulkley 1985a) and adult (Bulkley et al. 1981) Colorado pikeminnow <br />indicated that 25° C was the most preferred temperature: for both life <br />phases. Additional experiments indicated that optimum growth of <br />yearling Colorado pikeminnow also occurs at temperatures near 25° C <br />(Black and Bulkley 1985b). Although no such tests were conducted <br />using adults, the tests with yearlings supported the conclusions of <br />Jobling (1981) that the final thermal preferendum provides a good <br />indication of optimum growth temperature, i.e., 25° C. <br /> <br />
The URL can be used to link to this page
Your browser does not support the video tag.