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<br />Unwanted parasites and diseases frequently have been <br />introduced through fish transfers (Hoffman and Schubert <br />1984). Samples of the introduction stock should be examined <br />by a qualified fish pathologist prior to shipment. ldeally, <br />the sample should be quarantined for at least two weeks <br />so that parasites may complete their life cycle or become <br />numerous enough to detect (Hoffman and Schubert 1984). <br />Stock held in culture facilities often are subjected to crowded <br />conditions that may produce higher parasite loads. Culture <br />stocks should be regularly inspected for undesirable para- <br />sites and diseases. If sufficient introduction stock is available, <br />Ossiander and Wedemeyer (1973) recommended a sample <br />of at least 60 fish to determine the presence or absence of <br />a pathogen in the population. <br /> <br />The authors recognize that conditions may not allow for <br />the necessary quarantine and inspection of the introduction <br />stock. In a crisis situation where the last population of a <br />species is imminently threatened, for example, no time may <br />be available for a quarantine. Also, the transfer of wild stock <br />within a drainage presents a lower risk of introducing a new <br />parasite or disease. In such cases, a quarantine may not be <br />required. <br /> <br />D. Obtain introduction stock of sufficient number and <br />character. <br />An introduced population should be founded with enough <br />individuals to adequately reflect the genetic composition <br />present in the source population. Estimating the precise <br />number of individuals necessary to accurately reflect the <br />source population may be enigmatic. In general, a popu- <br />lation of fish from a homogeneous habitat (such as a small <br />stenothermal spring) may possess a narrower range of <br />genetic variability than a population from a heterogeneous <br />habitat (such as a eurythermal stream) (Vrijenhoek et a1. <br />1985). Therefore, a smaller number of individuals may be <br />required to encompass the available genetic variability from <br />a constant environment habitat compared to a variable <br />environment. If the source population is not threatened by <br />imminent loss, no more than 10% of the available stock <br />should be utilized annually for introductions. <br /> <br />Other important considerations include sex ratio and age <br />structure of the introduction stock. A sex ratio near 1: 1 and <br />a range of age classes should increase the chance of a <br />successful translocation. No ideal number exists, although <br />researchers have suggested that 25 males and 25 females <br />of the proper age and condition is an absolute minimum <br />to establish salmonid populations in highly controlled hatch" <br />ery settings (Allendorf and Ryman 1987; Ryman and Stahl <br />1980). Less controlled environments, where each individual <br />does not contribute equally in reproduction, require a greater <br />number of fish. <br /> <br />Collection techniques should disrupt natural habitats as <br />little as possible. Spring systems often are particularly <br />sensitive to small amounts of human disturbance. <br /> <br />E. Carefully and quickly transport stock. <br /> <br />A stress response usually results when fish experience <br />fright, discomfort, or pain (Schreck 1981). Transported stock <br />are most commonly stressed by physical handling and by <br />confinement of large numbers of individuals in small con- <br /> <br />10 <br /> <br />tainers. Loss of mucus or scales, disturbance to integument, <br />or damage to internal organs can lead to shock, increased <br />susceptibility to infection, immune system suppression and/ <br />or delayed mortality (Mazeaud et al. 1977; Schreck 1981). <br />The detrimental effects of repetitive stress are cumulative <br />(Schreck 1982). Therefore, an adequate recovery period <br />should be provided between each stressful event. Stress <br />also can impair a fish's ability to learn for up to several <br />weeks (C.B. Schreck, personal communication). This could <br />block imprinting processes needed for adult homing or <br />migration. Stress can be reduced by darkness or the use of <br />anesthetics (Schreck 1981). <br />A general discussion of handling live fish is presented by <br />Stickney (1983). In addition, Johnson (1979) presented data <br />on numbers and weights of fish that can safely be transported <br />in plastic bags containing water saturated with oxygen. <br />E Introduce stock under most favorable conditions. <br />Stock should be introduced during favorable weather and <br />hydrologic conditions. Thermal stock should be avoided by <br />equalizing the transport water temperature to that of the <br />habitat. Further, introducing stock at the proper time of <br />day can reduce initial predation losses. For example, because <br />sight-feeding predators would be less active at night, in- <br />troductions into waters containing such predators should <br />occur during dark conditions. <br />G. Document the translocation. <br />It is vital that the procedures and location of introductions <br />be made available in the scientific literature. Simply filing <br />the appropriate data in a handy institutional cabinet is <br />insufficient to allow necessary accessibility. Introduction <br />data should be made available through regularly distributed <br />scientific literature, or through administrative reports of the <br />lead agency. At a minimum, the following should be <br />reported: identity of those conducting the introduction, <br />taxon involved, source of the introduction sample, numbers <br />of introduced individuals and their sex, age and/or size <br />distribution, date of introduction, and precise location of <br />the receiving habitat. <br /> <br />3. Post-Introduction Activities <br /> <br />A. Conduct systematic monitoring of introduced popula- <br />tions. <br />Regular surveys should be conducted to determine initial <br />survival, recruitment of young, and persistence through <br />environmental stochasticity (such as floods, drought, or <br />fire). During the first year, quarterly monitoring may be <br />warranted. If the population becomes established, annual <br />monitoring should be continued for many years to deter- <br />mine long-term survivorship. Life history studies of intro- <br />duced populations are advisable. Rapid evolution of life <br />history strategies has been documented in introduced pop- <br />ulations of guppies, Poecilia reticulata, as a result of new <br />predators and/or novel habitats (Reznick and Bryga 1987). <br />B. Restock if wananted. <br />In some cases, it may be advisable to supplement the initial <br />stocking of the endangered or threatened fish in order to <br />facilitate establishment or increase gene flow. Subsequent <br />electrophoretic analysis of the introduced population would <br />reveal loss of genetic variation by founder effect, genetic <br /> <br />Fisheries, Vol. 13, No.5 <br /> <br />