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<br />PERFORMANCE OF PIT TAG INTERROGATION SYSTEMS <br /> <br />411 <br /> <br />efticiency varied with flow level (ANOV A, flow X <br />design interaction: P = 0.004), prompting us to run <br />separate tests by flow level. These tests showed that the <br />3 X 2 design had higher detection efficiencies for <br />upstream-moving fish than the 2 X I design and that <br />the 2 X 2 and 3X I designs did as well as the 3 X 2 in <br />high flow, whereas only the 2 X 2 did as well as the 3 X <br />2 design in low flow (AND V As and Tukey's tests: P < <br />0.05). For the 2 X 1 system, the precision of detection <br />efticiency for upstream-moving fish during high flow <br />was much poorer (Rattlesnake Creek, CV = 55%; <br />Beaver Creek, CV = 79%) compared with any other <br />design we tested (all other configurations, CV < 9%). <br />For downstream-moving fish, all four designs had <br />detection efficiencies with good precision (CV < 8%). <br />The observed differences in detection efficiencies for <br />combinations of flow level and direction of fish were <br />complex, but proved to be important to consider if <br />faced with limitations in number of antenna~ or arrays <br />that can be placed at a given site. <br /> <br />Discussion <br /> <br />The high PIT tag detection efficiencies of 96% to <br />almost 100% that we achieved for PIT-tagged <br />salmonids passing our 3 X 2 interrogation systems in <br />Rattlesnake and Beaver creeks can largely be attributed <br />to a redundancy of arrays that maintained detection <br />fields over most of, but not all, the stream width and <br />water colunm.Stream stage height was a factor, our <br />systems doing better in low flow than high flow, but <br />the difference was limited to a few percentage points <br />that may be biologically meaningless to many <br />applications, depending on the number of fish moving <br />through the system and the value of each detection <br />evenl to the study being conducted. <br />Stream stage height is probably a major factor in the <br />potential for fish to escape detection. What constitutes. <br />high flow will be site dependent. We used tag-detection <br />range to determine the division between low and high <br />flow. The number of fish passage events recorded <br />during high flow was somewhat low, so we did not <br />break flow level into additional categories. However, <br />we did not detect fish when stage height exceeded 1.94 <br />m in Rattlesnake Creek and 2.03 m in Beaver Creek. <br />We do not know whether this was a result of the <br />interrogation system becoming less efficient, whether <br />fish had a decreased tendency to move at high flows, or <br />both. Because the distinction between low and high <br />flow was based on water depth and the read distance of <br />the weakest PIT tag used in the watershed (BE-type in <br />Rattlesnake Creek, ST-type in Beaver Creek), this <br />probably introduced a bias into detectability. Not only <br />did the newer tags offer increased read range. but they <br />also increa~ed the chance that they would be detected at <br /> <br />_ Upstflitam <br />c:::J f>t.Nmgtrc"'" <br /> <br /> 100 <br />l 00 <br />~ <br />" <br />" <br />'il <br />~ 96 <br />" <br />0 <br />"" <br />~ .... <br />~ <br /> S2 <br /> 00 <br /> <br /> <br /> <br />Low 1-119" <br />_C!eOl< <br /> <br />Low High <br />Ral:tft~&nake ClOOk <br /> <br />FIGURE 6.-Efficiency of detection of PIT-tagged fLsh <br />moving upstream or downstream (mean + SE) past PIT tag <br />interrogation systems consisting of three alT'dYs and six <br />antennas in Ratdesnake and Beaver creeks under two flow <br />conditions: low (SO.l4 mOfs in Rattlesnake Creek and S0.57 <br />m3fs in Beaver Creek) and high (>0.14m3fs and >0.57 m3fs). <br /> <br />a wider range of orienl'ation to an antenna's interroga- <br />tion field and to stronger EMF-interfering noise levels. <br />These differences in tag models could have differen- <br />tially contributed to an underestimate or overestimate <br />of detection efficiency at low- and high-flow levels <br />(Horton et al. 2007). New models of PIT tags are likely <br />to be available in the future and readily adopted by <br />users, especially when older models are pha<ied out of <br />production and become unavailable. Based on the need <br />to eliminate bias of estimates for detection efficiency. <br />researchers and managers may need to anticipate these <br />changes in their study designs. <br />The arrays with hybrid antennas clearly outper- <br />formed those with pass-by antennas for detecting <br />PIT -tagged fish moving downstream during high flow, <br />but the opposite was true for detecting fish moving <br />upstream in high flow. No distinction between antenna <br />types was evident for detection of fish moving during <br />low flow. These findings may be important to <br />researchers faced with a choice among the type of <br />antennas and number of arrays to use because of, for <br />example, lack of funds or limitations imposed by the <br />site. This choice would probably be more effective if <br />based on the configuration that will probably perform <br />best for the fish behavior that it is most desired to track <br />and for the stream characteristics during the period of <br />interest. By using a mix of antenna types, but limiting <br />the use of the more flow-dependent hybrid type to a <br />single array, our systems appeared to have been a good <br />combination for maintaining high detection efticiency <br />during both low and high flow for downstream- and <br />upstream-moving fish. <br />The hybrid-type antenna~ actively moved up and <br />down in the water column and did so regularly during <br />