<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">OJAS</journal-id><journal-title-group><journal-title>Open Journal of Animal Sciences</journal-title></journal-title-group><issn pub-type="epub">2161-7597</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ojas.2014.45031</article-id><article-id pub-id-type="publisher-id">OJAS-50120</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Rearing Velocity Impacts on Landlocked Fall Chinook Salmon (&lt;i&gt;Oncorhynchus tshawytscha&lt;/i&gt;) Growth, Condition, and Survival
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>imothy</surname><given-names>M. Parker</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Michael</surname><given-names>E. Barnes</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>South Dakota Department of Game, Fish and Parks, Spearfish, McNenny State Fish Hatchery, South Dakota, USA</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>Timothy.Parker@state.sd.us(IMP)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>11</day><month>09</month><year>2014</year></pub-date><volume>04</volume><issue>05</issue><fpage>244</fpage><lpage>252</lpage><history><date date-type="received"><day>12</day>	<month>July</month>	<year>2014</year></date><date date-type="rev-recd"><day>27</day>	<month>August</month>	<year>2014</year>	</date><date date-type="accepted"><day>13</day>	<month>September</month>	<year>2014</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Juvenile landlocked Chinook salmon (
  Oncorhynchus tshawytscha) (mean &#177; SD initial weight 2.6 &#177; 0.7 g, fork length 6.3 &#177; 0.5) were reared in three different water velocities [0.5, 1.5 and 3.0 body length/s (BL/s)] for four weeks to determine possible effects of water velocity on growth, condition, and survival. Fish were sampled for weight, fork length, condition factor, hepatosomatic index (HSI), viscerosomatic index (VSI), and fin erosion after four weeks of feeding to satiation. At the end of the feeding trial, the fish were handled and transported to simulate stocking, with survival observed over the following 10 d. Following four weeks of feeding, fish reared in 0.5 and 1.5 BL/s had the same growth and food conversion ratio, but fish reared at 3.0 BL/s had a significant reduction in both metrics. Furthermore, fish reared at 1.5 BL/s had a significantly higher condition factor than fish reared in other treatments. No significant differences were found for HSI, VSI, fin erosion, or survival. The results from this study indicate that a moderate velocity (1.5 BL/s), which is necessary for circular tanks to be self-cleaning, is not detrimental to fish growth or condition, but a faster water velocity (3.0 BL/s) negatively affects fish growth and food utilization.
 
</p></abstract><kwd-group><kwd>Chinook Salmon</kwd><kwd> &lt;i&gt;Oncorhynchus tshawytscha&lt;/i&gt;</kwd><kwd> Velocity</kwd><kwd> Circular Tanks</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Using rearing velocities to exercise cultured fish has been shown to influence fish growth [<xref ref-type="bibr" rid="scirp.50120-ref1">1</xref>] - [<xref ref-type="bibr" rid="scirp.50120-ref3">3</xref>] and food con- version [<xref ref-type="bibr" rid="scirp.50120-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref5">5</xref>] . Rainbow trout (Oncorhynchus mykiss) forced to swim at 1 body length/s (BL/s) grew twice as much and had more efficient protein conversion than unexercised fish over a six week period [<xref ref-type="bibr" rid="scirp.50120-ref1">1</xref>] . However, the effect of exercise on Chinook salmon (Oncorhynchus tshawytscha) led to reduced growth. Kiessling et al. [<xref ref-type="bibr" rid="scirp.50120-ref6">6</xref>] showed that Chinook salmon swimming at speeds of 0.5 - 1.5 BL/s for 212 days had the same growth rate, but higher swimming speeds resulted in increased feed consumption and decreased food conversion ratios (FCR). However, decreased growth performance of Chinook salmon reared at higher water velocities may be compen- sated by increased fish quality [<xref ref-type="bibr" rid="scirp.50120-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref7">7</xref>] and increased post-stocking survival [<xref ref-type="bibr" rid="scirp.50120-ref8">8</xref>] .</p><p>Exercised fish have been shown to have increased swimming performance [<xref ref-type="bibr" rid="scirp.50120-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref10">10</xref>] and reduced stress [<xref ref-type="bibr" rid="scirp.50120-ref11">11</xref>] . Swimming comes with energetic costs which may result in decrease FCR, but exercised fish are better suited for environments with moving water. The swimming performance of brook trout (Salvelinus fontinalis) has been shown to be significantly improved in exercised fish, consequently allowing them to swim farther in rapidly moving water [<xref ref-type="bibr" rid="scirp.50120-ref2">2</xref>] . Gallaugher et al. [<xref ref-type="bibr" rid="scirp.50120-ref10">10</xref>] showed that exercised Chinook salmon are able to increase their maximum oxygen consumption, enabling them to provide oxygen for the physiological processes associated with swimming. Therefore, exercise reduces the metabolic cost of swimming and allows for the maintenance of physiological functions, resulting in post-stocking benefits.</p><p>Cresswell and Williams [<xref ref-type="bibr" rid="scirp.50120-ref8">8</xref>] found that brown trout (Salmotrutta) reared in indoor tanks and acclimated to flowing water (i.e. exercise) had a higher percentage of recapture after stocking into flowing waters. In addition, exercised fish may be more aesthetically pleasing to angler post-stocking due to reduced fin erosion. Exercised Arctic char (Salvelinus alpinus) had significantly reduced fin damage compared to fish reared in standing water [<xref ref-type="bibr" rid="scirp.50120-ref4">4</xref>] .</p><p>No previous studies have been conducted examining the effects of exercise on growth of landlocked Chinook salmon in general or landlocked fall Chinook salmon from Lake Oahe, South Dakota. This strain of fish is rela- tively unique and has been genetically isolated from all other strains of Chinook salmon since 1989 [<xref ref-type="bibr" rid="scirp.50120-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.50120-ref13">13</xref>] . Because this salmon population is maintained solely by stocking, and progeny may be limited during certain years [<xref ref-type="bibr" rid="scirp.50120-ref13">13</xref>] , using exercise to improve hatchery rearing performance and post-stocking survival is important. Ad- ditionally, it is unknown how tank velocities required for tanks to be self-cleaning influence production. Thus, the objective of this study was to investigate the effects of rearing velocity on Lake Oahe fall Chinook salmon growth, condition, and survival.</p></sec><sec id="s2"><title>2. Materials and Methods</title><p>Fish were reared at McNenny State Fish Hatchery, Spearfish, South Dakota, using progeny of landlocked fall Chinook salmon from Lake Oahe obtained for spawning on October 22, 2013. The fish began feeding on De- cember 23, 2013 and were reared using standard hatchery practices until the beginning of the experiment. On February, 26, 2014 fish (mean &#177; SD initial weight 2.6 &#177; 0.7 g , fork length 6.3 &#177; 0.5 cm , n = 70) were combined into two tanks ( 196.25 kg ) and then randomly distributed to nine, 2000-L circular tanks ( 1.8 m in diameter and 0 .8 m deep) at equal densities of approximately 8076 fish (48.1 &#177; 0.3 kg /tank).</p><p>Three velocity treatments (0.5, 1.5, and 3.0 BL/s) were assigned to the nine tanks (n = 3). A velocity of 0.5 BL/s was not enough to force fish to swim continuously into the current and fish were able to haphazardly swim in their tanks. This treatment was used as a proxy for a non-swimming group because it allowed for the fish to not have to continuously swim and provided some rotation in the water to assist with maintaining clean tanks. Water velocity was adjusted by manipulating the angle of the spray bar and determined by recording the time it took for a neutral buoyant object to orbit the tank. Ten fish from each tank were measured for weight and fork length every seven days. Water velocity was re-checked every seven days as well.</p><p>Well water at a constant temperature of 11˚C (total hardness as CaCO<sub>3</sub>, 360 mg/L; alkalinity as CaCO<sub>3</sub>, 210 mg/L; pH, 7.6; total dissolved solids, 390 mg/L) was supplied to the tanks at approximately 47.8 L /min. Fish were fed every 15 minutes during daylight hours using automatic feeders with 1.0 mm extruded sinking 45-19 salmon diet (Skretting; Tooele, Utah). Feeding rates were determined by the hatchery constant method [<xref ref-type="bibr" rid="scirp.50120-ref14">14</xref>] , with a planned feed conversion of 1.1 and a maximum growth rate of 0.08 cm /day, a rate which is at or above satiation for this strain at McNenny Hatchery. Dead fish were removed daily and weighed. At the end of four weeks of feeding, biomass for each tank was determined by weighing the entire tank. Along with tank biomass, data was also collected from 20 individual fish per tank, including fork length to the nearest 1.0 mm , weight to the nearest 0.001 g , pectoral fin length to the nearest 0.1 mm , liver weight to the nearest 0.001 g , and viscera weight to the nearest 0.0001 g . The following equations were used:</p><disp-formula id="scirp.50120-formula437"><graphic  xlink:href="http://html.scirp.org/file/5-1400262x5.png"  xlink:type="simple"/></disp-formula><p><inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/5-1400262x6.png" xlink:type="simple"/></inline-formula>[<xref ref-type="bibr" rid="scirp.50120-ref15">15</xref>]</p><disp-formula id="scirp.50120-formula438"><graphic  xlink:href="http://html.scirp.org/file/5-1400262x7.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.50120-formula439"><graphic  xlink:href="http://html.scirp.org/file/5-1400262x8.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.50120-formula440"><graphic  xlink:href="http://html.scirp.org/file/5-1400262x9.png"  xlink:type="simple"/></disp-formula><p>As part of weighing the entire tank for biomass determination at the end of four weeks, the fish, which were part of hatchery production, were loaded into a transfer tank using dipnets containing approximately 10 kg per net load. The fish were then transported to another part of the hatchery complex for continued rearing in larger units prior to stocking. The entire procedure (netting and transportation) took approximately 20 min per tank. To ascertain any possible effects of exercise on post-handling mortality and stress, 100 fish from each tank were returned to their original experimental tanks. Mortality and fin erosion were monitored for these fish for the next 10 d.</p><p>Data was analyzed using the SPSS (9.0) statistical analysis program (SPSS, Chicago, Illinois, USA). Growth, FCR, VSI, HSI, fin erosion, and condition factor were analyzed using One-Way ANOVA with a Tukey post-hoc test. Weekly changes in fork length were analyzed using a One-Way ANOVA for each week. Data was consider significantly different when P &lt; 0.05.</p></sec><sec id="s3"><title>3. Results</title><p>Following 28 days of feeding, the fastest swimming treatment (3.0 BL/s) had a significantly lower weight gain than the other two treatments, but the weight gain of fish reared at the other two velocities was not significantly different (<xref ref-type="fig" rid="fig1">Figure 1</xref>). FCR results followed a similar pattern (<xref ref-type="fig" rid="fig2">Figure 2</xref>). Changes in fork length each week during the duration of the experiment were not significantly different (<xref ref-type="table" rid="table1">Table 1</xref>). However, P values decreased over time</p><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> Mean (&#177;SD) weight gain (%) of landlocked fall Chinook salmon reared at three different water velocities (body length/s = BL/s) for four weeks. Means with different letters are significantly different (P &lt; 0.05, n = 3)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x10.png"/></fig><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Mean (&#177;SD) fork length (cm) of landlocked fall Chinook salmon reared in three different water velocities. Ten in- dividuals were measured per tank (body length/s = BL/s; n = 3)</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle"  colspan="3"  >Velocity (BL/s)</th><th align="center" valign="middle" ></th></tr></thead><tr><td align="center" valign="middle" >Week</td><td align="center" valign="middle" >0.5</td><td align="center" valign="middle" >1.5</td><td align="center" valign="middle" >3.0</td><td align="center" valign="middle" >P</td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >6.6 &#177; 0.2</td><td align="center" valign="middle" >6.4 &#177; 0.1</td><td align="center" valign="middle" >6.4 &#177; 0.2</td><td align="center" valign="middle" >0.197</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >7.0 &#177; 0.2</td><td align="center" valign="middle" >6.9 &#177; 0.1</td><td align="center" valign="middle" >6.7 &#177; 0.1</td><td align="center" valign="middle" >0.103</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >7.2 &#177; 0.3</td><td align="center" valign="middle" >7.3 &#177; 0.2</td><td align="center" valign="middle" >7.1 &#177; 0.1</td><td align="center" valign="middle" >0.559</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >7.7 &#177; 0.1</td><td align="center" valign="middle" >7.8 &#177; 0.1</td><td align="center" valign="middle" >7.4 &#177; 0.2</td><td align="center" valign="middle" >0.058</td></tr></tbody></table></table-wrap><p>and approached significance by Week 4.</p><p>Survival was unaffected by swimming velocity during the four week feeding trial, and for ten days after moving (<xref ref-type="table" rid="table2">Table 2</xref>). The moderate swimming speed treatment (1.5 BL/s) led to a significant increase in condition factor compared to the slow (0.5 BL/s) and fast (3.0 BL/s) swimming speeds (<xref ref-type="fig" rid="fig3">Figure 3</xref>). However, there were no significant differences in HSI or VSI (<xref ref-type="fig" rid="fig4">Figure 4</xref> and <xref ref-type="fig" rid="fig5">Figure 5</xref>). There were also no significant differences in fin erosion among the velocity treatments at the end of the feeding trial or post-handling (<xref ref-type="fig" rid="fig6">Figure 6</xref> and <xref ref-type="fig" rid="fig7">Figure 7</xref>).</p><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Mean (&#177; SD) food conversion ratio (FCR) of landlocked fall Chi- nook salmon reared at three different water velocities (body length/s = BL/s) for four weeks. Means with different letters are significantly different (P &lt; 0.05, n = 3)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x11.png"/></fig><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Mean (&#177; SD) condition factor (K) of landlocked fall Chinook sal- mon reared at three different water velocities (body length/s = BL/s) for four weeks. Means with different letters are significantly different (P &lt; 0.05, n = 3)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x12.png"/></fig><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Mean (&#177; SD) percent survival of landlocked fall Chinook salmon reared in three different water velocities during a four week feeding trial and ten days post-handling (n = 3)</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Trial</th><th align="center" valign="middle" >Velocity (BL/s)<sup>a</sup></th><th align="center" valign="middle" >% Survival</th></tr></thead><tr><td align="center" valign="middle" >Feeding</td><td align="center" valign="middle" >0.5</td><td align="center" valign="middle" >99.91 &#177; 0.03</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >1.5</td><td align="center" valign="middle" >99.88 &#177; 0.04</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >99.82 &#177; 0.01</td></tr><tr><td align="center" valign="middle" >Post-handling</td><td align="center" valign="middle" >0.5</td><td align="center" valign="middle" >100.00 &#177; 0.00</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >1.5</td><td align="center" valign="middle" >100.00 &#177; 0.00</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >100.00 &#177; 0.00</td></tr></tbody></table></table-wrap><fig id="fig4"  position="float"><label><xref ref-type="fig" rid="fig4">Figure 4</xref></label><caption><title> Mean (&#177; SD) hepatosomatic index (HSI) of landlocked fall Chinook salmon reared at three different water velocities (body length/s = BL/s) for four weeks (n = 3). No significant differences were found between the treat- ments</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x13.png"/></fig><fig id="fig5"  position="float"><label><xref ref-type="fig" rid="fig5">Figure 5</xref></label><caption><title> Mean (&#177; SD) visceral-somatic index (VSI) of landlocked fall Chinook salmon reared at three different water velocities (body length/s = BL/s) for four weeks (n = 3). No significant differences were found between the treatments</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x14.png"/></fig><fig id="fig6"  position="float"><label><xref ref-type="fig" rid="fig6">Figure 6</xref></label><caption><title> Mean (&#177; SD) pectoral fin erosion of landlocked fall Chinook salmon reared at three different water velocities (body length/s = BL/s) for four weeks (n = 3). No significant differences were found between the treatments</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x15.png"/></fig><fig id="fig7"  position="float"><label><xref ref-type="fig" rid="fig7">Figure 7</xref></label><caption><title> Mean (&#177; SD) pectoral fin erosion ten days after handling stress of landlocked fall Chinook salmon reared at three different water velocities (body length/s = BL/s) for four weeks (n = 3). No significant differences were found between the treatments</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1400262x16.png"/></fig></sec><sec id="s4"><title>4. Discussion</title><p>The negative impacts on growth and FCR associated with the 3.0 BL/s swimming speed likely indicates an in- creased energetic cost compared to the two lesser velocities. However, 1.5 BL/s which is required for tanks to sufficiently be self-cleaning did not result in any reduction in growth or FCR in comparison to fish in the 0.5 BL/s. The water velocity in the 0.5 BL/s treatments was slow enough that fish were not forced to continuously swim and were able to randomly swim in their tank. Chinook salmon have been shown to have an exponential increase in oxygen consumption as swimming speeds increase [<xref ref-type="bibr" rid="scirp.50120-ref10">10</xref>] . Kiessling et al. [<xref ref-type="bibr" rid="scirp.50120-ref5">5</xref>] also found that Chinook salmon exercised at speeds of 0.5 and 1.5 BL/s had no difference in growth, but the fish swimming at 1.5 BL/s had a less efficient FCR. The lack of difference in growth in the fish swimming at 0.5 and 1.5 BL/s may be due to improved physiological functions in fish swimming at 1.5 BL/s offsetting the increase in energetic cost asso- ciated with swimming. Rainbow trout were shown to have a 10% decrease in oxygen consumption when swim- ming at a constant speed and switching from active to ram ventilation [<xref ref-type="bibr" rid="scirp.50120-ref16">16</xref>] . Furthermore, Gallaugher et al. [<xref ref-type="bibr" rid="scirp.50120-ref10">10</xref>] showed the exercised Chinook salmon had improved osmoregulation, enabling them to multitask physiological functions while swimming, such as prioritizing the metabolic processes associated with digestion [<xref ref-type="bibr" rid="scirp.50120-ref9">9</xref>] . Unlike Kiessling et al. [<xref ref-type="bibr" rid="scirp.50120-ref6">6</xref>] who noted a decrease in food utilization efficiency when Chinook salmon were swimming at 1.5 BL/s compared to 0.5 BL/s, we found no difference in FCR between fish swimming at the same speeds. However, Kiessling et al. [<xref ref-type="bibr" rid="scirp.50120-ref6">6</xref>] used much larger fish ( 75 g ) in a much longer experiment (212 d). The Our FCR data is similar to previous studies using Lake Oahe Chinook salmon reared at high density [<xref ref-type="bibr" rid="scirp.50120-ref17">17</xref>] . Thus, even though swimming has energetic cost, the increased energy utilized is offset by improvements to physiological functions. It should be noted that our FCR values may not be directly comparable with those of other studies, because FCR can be influenced by feeding rates, feeding strategies, fish size, rearing density, and water tempera- tures [<xref ref-type="bibr" rid="scirp.50120-ref18">18</xref>] - [<xref ref-type="bibr" rid="scirp.50120-ref23">23</xref>] . Additionally, these results may only apply for Lake Oahe Chinook salmon at this size and age as it is unknown how size and age influences the effects of exercise on these fish.</p><p>Survival in our study was unaffected by treatment and hatchery handling. However, Cresswell and Williams [<xref ref-type="bibr" rid="scirp.50120-ref8">8</xref>] showed that brown trout acclimated to flowing water had a higher percentage of recapture post-stocking in flowing waters. Furthermore, Woodward and Smith [<xref ref-type="bibr" rid="scirp.50120-ref11">11</xref>] noted that exercised rainbow trout had significantly lower plasma cortisol levels when allowed to rest, which may indicate that exercised trout are better adapted to handle stress, even in water with no flow. Our handling procedures likely did not adequately mimic the stressors associated with actual stocking, making it difficult to predict whether our treatment conditions could enhance post-stocking. Barton et al. [<xref ref-type="bibr" rid="scirp.50120-ref24">24</xref>] found that brief handling led to elevated plasma cortisol levels for only 2 h, while stocking caused cortisol levels to remain elevated for 4 to 8 d. Therefore, in future studies it is critical for handling procedures to induce a large amount of stress to clearly understand the effects of exercise on post- stocking survival.</p><p>The lack of significant differences in the weekly lengths among the treatment groups is likely due to the short length of this study. The decrease in P values as the study progressed suggests that fish sizes may have become significantly different in future weeks had the experiment continued. Christiansen et al. [<xref ref-type="bibr" rid="scirp.50120-ref25">25</xref>] did not detect a significant increase in the weights of resting and exercising Arctic charr until 42 days. Unfortunately, our study had to conclude after four weeks (28 days) because the fish needed to be transferred to larger tanks as part of hatchery production. Although not significantly different, trends in the data appear to indicate that the fish swimming at 1.5 BL/s were smallest after one week of swimming and were the largest by the end of the experi- ment. If this is an accurate trend, it may indicate that these fish initially had a period of acclimation, which would be consistent with the results of Woodward and Smith [<xref ref-type="bibr" rid="scirp.50120-ref11">11</xref>] .</p><p>Bosakowski and Wagner [<xref ref-type="bibr" rid="scirp.50120-ref26">26</xref>] found that density and environmental conditions were significantly related to fin erosion. Furthermore, Arctic charr fed in excess and allowed to haphazardly swim in their tanks had in- creased aggressive behavior and damaged fins [<xref ref-type="bibr" rid="scirp.50120-ref4">4</xref>] . It was expected that fish in the 0.5 BL/s would exhibit in- creased aggressive behavior resulting in increased fin erosion, but this did not occur. The lack of significant dif- ferences in fin erosion among the treatments likely indicates a relative lack of environmental stress and a lack of aggressive behavior.</p><p>The increase in condition factor of fish swimming at 1.5 BL/s possibly indicates that the fish did have in- creased energy status via whole body total lipids [<xref ref-type="bibr" rid="scirp.50120-ref27">27</xref>] . Furthermore, similar results to ours were found by J&#248;rgensen and Jobling [<xref ref-type="bibr" rid="scirp.50120-ref28">28</xref>] in which Atlantic salmon (Salmosalar) swimming at 1.5 and 2.0 BL/s had a signifi- cant increase in condition factor compared to resting fish. However, J&#248;rgensen and Jobling [<xref ref-type="bibr" rid="scirp.50120-ref28">28</xref>] did not have a treatment group comparable to fish swimming at 3.0 BL/s. We were surprised that fish swimming at 3.0 BL/s did not result in a significantly reduced HSI as a result of the increased energy demand caused by the high ve- locity, anticipating that the strenuous exercise would lead to decreased glycogen stores and subsequent reduc- tions in liver weight. However, Chellappa et al. [<xref ref-type="bibr" rid="scirp.50120-ref29">29</xref>] found that HSI was poor at indicating the energy status of three-spined stickleback (Gasterosteus aculeatus), noting that during periods of low food availability, water content increased in the liver as glycogen reserves were mobilized. Therefore, fish swimming at 3.0 BL/s may have had reduced glycogen reserves which were not accurately reflected by the HSI values. We also anticipated that VSI would decrease in the fish forced to swim at 3.0 BL/s, due to a relative decrease in the amount of vis- ceral fat. However, very little fat was observed in any of the treatment groups. The GI tract was nearly absent of attached visceral fat, despite being fed at or slightly above satiation. This could indicate that that energy was be- ing allocated to growth and not stored. The fish used in this study were at a life stage in which rainbow trout have been shown to have a low amount of lipid content (2%) [<xref ref-type="bibr" rid="scirp.50120-ref30">30</xref>] . However, after this stage, lipid content ra- pidly increases until the fish are 20 g with approximately 6% lipid [<xref ref-type="bibr" rid="scirp.50120-ref30">30</xref>] . It is likely that if the experiment were to be conducted over a longer period of time, or until fish were of a size where more energy was allocated to ener- gy storage, the VSI data would be more insightful to the energetics of each the treatment groups.</p><p>In conclusion, the results from our study indicate that moderate swimming speeds required for tanks to be self-cleaning (1.5 BL/s) have no negative impact on landlocked fall Chinook salmon growth or feed conversion ratio. Furthermore, 1.5 BL/s appears to have a positive impact on fish condition factor, indicating that a mod- erate swimming speed of 1.5 BL/s improves the energy status in landlocked fall Chinook salmon from Lake Oahe. However, further longer term studies need to be done, and such studies should include observations on post-stocking survival.</p></sec><sec id="s5"><title>Acknowledgements</title><p>The authors thank Patrick Nero , Eric Krebs , Kristen Becket , and Dennis Bailey for their assistance with this study.</p></sec></body><back><ref-list><title>References</title><ref id="scirp.50120-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Houlihan, D. and Laurent, P. (1987) Effects of Exercise Training on the Performance, Growth, and Protein Turnover of Rainbow Trout (Salmogairdneri). Canadian Journal of Fisheries and Aquatic Sciences, 44, 1614-1621.http://dx.doi.org/10.1139/f87-195</mixed-citation></ref><ref id="scirp.50120-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Leon, K.A. (1986) Effect of Exercise on Feed Consumption, Growth, Food Conversion, and Stamina of Brook Trout. 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