Difference between revisions of "Smallmouth Bass Page"
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*[http://gcdamp.com/index.php?title=Nonnative_Invasive_Aquatic_Species Nonnative Invasive Aquatic Species] | *[http://gcdamp.com/index.php?title=Nonnative_Invasive_Aquatic_Species Nonnative Invasive Aquatic Species] | ||
+ | *[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf Habitat suitability information: Smallmouth bass] | ||
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*[https://www.usbr.gov/uc/progact/amp/twg/2022-04-13-twg-meeting/20220413-Near-TermThreatSmallmouthBassEstablishmentGlenCanyonDam-Presentation-508-UCRO.pdf Near-Term Threat of Smallmouth Bass Establishment below Glen Canyon Dam ] | *[https://www.usbr.gov/uc/progact/amp/twg/2022-04-13-twg-meeting/20220413-Near-TermThreatSmallmouthBassEstablishmentGlenCanyonDam-Presentation-508-UCRO.pdf Near-Term Threat of Smallmouth Bass Establishment below Glen Canyon Dam ] | ||
*[https://www.usbr.gov/uc/progact/amp/twg/2022-01-13-twg-meeting/20220113-AnnualReportingMeeting-FishModellingSupportManagementDecisions-508-UCRO.pdf Fish modelling to support management decisions ] | *[https://www.usbr.gov/uc/progact/amp/twg/2022-01-13-twg-meeting/20220113-AnnualReportingMeeting-FishModellingSupportManagementDecisions-508-UCRO.pdf Fish modelling to support management decisions ] | ||
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+ | ! <h2 style="margin:0; background:#cedff2; font-size:120%; font-weight:bold; border:1px solid #a3b0bf; text-align:left; color:#000; padding:0.2em 0.4em;">Flow fluctuations</h2> | ||
+ | |- | ||
+ | |style="color:#000;"| | ||
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+ | Large fluctuations in water level can affect reproductive success | ||
+ | (Pflieger 1975; Montgomery et al . 1980). Ideal spawning conditions include | ||
+ | one or more substantial rises in water level a week or two prior to bass | ||
+ | nesting (Pflieger 1975) and relatively stable water levels while nesting is in | ||
+ | progress (Watson 1955; Pflieger 1975). Rising water may flush nest areas with | ||
+ | cold water, causing nest desertion and halting embryo development (Watt 1959; | ||
+ | Montgomery et al. 1980). Falling water levels may drive guarding males off, | ||
+ | limit water circulation around eggs, and increase predation, resulting in | ||
+ | lower reproductive success (Neves 1975; Montgomery et al. 1980).[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf] | ||
+ | |||
+ | Fry seem to be especially vulnerable to flood conditions and fluctuating | ||
+ | water levels (Larimore 1975). A rapid drop in water level may trap them in | ||
+ | areas where they will become dessicated (Montgomery et al . 1980). A stream | ||
+ | rise of only a few inches may displace advanced fry newly risen from the nest | ||
+ | (Webster 1954). Most fry remain in shallow water (Doan 1940; Forney 1972), | ||
+ | although some may be found at depths of 4.6.-6.1 m (Stone et al. 1954; Forney | ||
+ | 1972). Fry 20-25 mm in length cannot maintain themselves in current velocities | ||
+ | > 200 mm/sec (Larimore and Duever 1968). An increase in turbulence during | ||
+ | flood conditions creates conditions with which smallmouth fry appear unable to | ||
+ | cope (Webster 1954). Fry cannot tolerate and are displaced at high turbidities | ||
+ | (2,000 JTU) combined with an increase in water velocity, but they will not be | ||
+ | displaced at moderate turbidities (250 JTU) (Larimore 1975). Low water temperatures during flood conditions will reduce fry swimming ability (Larimore | ||
+ | and Duever 1968).[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf] | ||
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elevation (Minckley 1973). [https://www.usbr.gov/lc/phoenix/biology/azfish/pdf/smallmouthbass.pdf] | elevation (Minckley 1973). [https://www.usbr.gov/lc/phoenix/biology/azfish/pdf/smallmouthbass.pdf] | ||
− | '''Temperature:''' | + | '''Temperature:''' Temperatures may be the most important single factor limiting distribution |
+ | of smallmouth bass (Robbins and MacCrimmon 1974; Coutant 1975). Faster | ||
+ | growth rates of adult smallmouth bass are generally associated with higher | ||
+ | summer temperatures (Doan 1940; Brown 1961; Forney 1972). Faster growth rates | ||
+ | occur in southern reservoirs, resulting in earlier death than in northern | ||
+ | regions (Coutant 1975). In the summer, bass inhabit warmer shoreline areas of | ||
+ | large lakes in the North and deeper, cooler waters in the South (Coutant | ||
+ | 1975). Growth does not begin until water temperatures reach 10-14° C (Coble | ||
+ | 1975). Field data indicate that adults prefer temperatures of about 21-27° C | ||
+ | in the summer (Clancey 1980). Smallmouth bass have been reported "sunning" | ||
+ | themselves in pools with water temperatures of about 26.7° C in summer (Munther | ||
+ | 1970). | ||
+ | |||
+ | Temperature preferences of smallmouth bass vary considerably depending on | ||
+ | the acclimation temperature (Ferguson 1958; Cherry et al. 1975; Coutant 1975). | ||
+ | Smallmouth bass acclimated at 2.2-30.0° C selected temperatures of 20-32° C in | ||
+ | laboratory tests (Mathur et al. 1981). Adult bass in the laboratory preferred | ||
+ | temperatures of 28° C (Ferguson 1958; Bennett 1965) to 31° C (Barans and Tubb | ||
+ | 1973; Coutant 1975). Optimum growth rates in the lab occurred at temperatures | ||
+ | from 26-29° C (Peek 1965; Shuter et al. 1980; Wrenn 1980). Upper lethal | ||
+ | temperatures for adults were above 32.3° C (Coble 1975). | ||
+ | |||
+ | When temperatures drop to 15-20° C, adults seek deep, dark areas (Webster | ||
+ | 1954; Munther 1970). At about 10° C, bass become inactive and seek shelter | ||
+ | (Coble 1975; Shuter et al. 1980). At 6-7° C, most smallmouth bass are beneath | ||
+ | the rock substrate, with few remaining on top (Munther 1970). The lower | ||
+ | lethal temperature is near freezing (Coble 1975). Bass will congregate around | ||
+ | warm springs in winter when available (Coutant 1975).[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf] | ||
− | '''Turbidity and Dissolved Oxygen: ''' | + | '''Turbidity and Dissolved Oxygen: '''Smallmouth bass apparently can tolerate periodic turbidity (Webster 1954; |
+ | Cleary 1956), although excessive turbidity and siltation will reduce a population (Coutant 1975). Hubert and Lackey (1980) reported a typical smallmouth | ||
+ | bass habitat to have very low turbidity, usually < 25 JTU, and almost never | ||
+ | > 75 JTU (except under flood conditions when turbidity is sometimes as high as | ||
+ | 250 JTU).[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf] | ||
− | '''Salinity: ''' | + | '''Salinity: '''Smallmouth occur at pH levels of 5.7 (Clady 1977) to 9 (Paragamian 1979), |
+ | although optimum pH is 7.9-8.1 (Funk and Pflieger 1975). Butler (1972) found | ||
+ | that smallmouth bass cover-seeking behavior was reduced at pH levels < 6, and | ||
+ | the lower lethal pH level was 3. Smallmouth bass populations are more productive in clearer, less fertile | ||
+ | reservoirs several years after impoundment that have low total dissolved | ||
+ | solids (TDS = 100-350 ppm) (Jenkins 1975, 1976).[https://apps.dtic.mil/sti/pdfs/ADA323294.pdf] | ||
'''Reproduction: '''Spawning occurs from March though May in Arizona, when water temperatures reach 15C | '''Reproduction: '''Spawning occurs from March though May in Arizona, when water temperatures reach 15C |
Revision as of 14:33, 25 July 2022
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Smallmouth Bass (Micropterus dolomieui)The predatory threat of invasive and large-bodied piscivorous taxa such as smallmouth bass in the upper Colorado River basin is substantial. For example, based on results of a bioenergetics model, Johnson et al. (2008) ranked smallmouth bass as the most problematic invasive species because of their high abundance, habitat use that overlaps with most native fishes, and ability to consume a wide variety of life stages of native fishes (Bestgen et al. 2008). Expanded populations of piscivores such as smallmouth bass are a major impediment to conservation actions aimed at recovery efforts for the four endangered fishes in the upper Colorado River basin (U.S. Fish and Wildlife Service 2002a, b, c, d). [1] |
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