This paper synthesizes data collected from bowhead whales (Balaena mysticetus) landed by Alaskan Eskimos between 1973 and 1982. From these data, and from the literature, length at birth has been estimated to be 4‐4.5 m, length at one year to be 8‐2 m, length at sexual maturity to be 14 m in females, and maximum length to be 20 m. Sexual activity, possibly mating, has been observed in March through May and the length of gestation is estimated to be 13 months. The calving period appears to extend from March through August, with the peak in births occurring in May. Lactation may extend for one year. Evidence has been provided for a pregnancy rate (percentage pregnant in mature female catch) of 015 and it has been suggested that calving occurs every three to six years. Gross annual reproductive rate (based on calf sightings) is estimated to be at least 3–6%. Sources of mortality are discussed. The sex ratio of animals taken by Eskimos is 0.83: 1.00 (females to males) and is not significantly different from unity. Summary The conclusions drawn in each of the preceding sections are likely to be re‐evaluated as more information becomes available. Still, it is suggested that the length at birth is 4–4.5 m, length at one year is 8.2 m, length at sexual maturity is 14 m in females, and the maximum attainable length is 20 m. Conception is most likely to occur in late winter while the whales congregate in Bering Sea polynyas, whereas the peak in calving appears to occur in May. Consequently, it has been hypothesized that the gestation time is greater than one year, but less than two. By analogy with other right whales and sparse data collected, the duration of lactation is assumed to be one year, although this is arguable. The pregnancy rate of mature females, calculated from ovarian data, is 0.15, projecting a calving interval of approximately seven years. The gross annual reproductive rate generated from field data is 3.6–12.4%. The sex ratio of the harvested animals is 0.83: 1.0, and it is assumed that this does not reflect the whole population. Whatever changes are yet to be made in the understanding of the bow‐head life history, all of the traits delineated are consistent with those predicted for slowly reproducing animals, the quintessential K‐strategist. We are most grateful to the scores of field biologists who have helped us count whales and sample those landed by the Eskimos, and who have contributed ideas and enthusiasm. In addition, we thank R. Tarpley for information on ovaries collected in 1982, J. Breiwick for running several sex ratio estimates, and H. Marsh for her generous assistance with the ovarian histology. Under contract to us R. Davis and W. Koski of L.G.L., environmental research associates, provided the photogrammetric measurements. An earlier, less complete version of our paper was submitted in 1982 as an unpublished report (document SC/34/PS1) to the International Whaling Commission, resulting in many valuable comments from members of the Scientific Committee. P. Best, D. Chapman, and an anonymous...
Fish‐guiding screens of different porosities were tested with juvenile spring chinook salmon (Oncorhynchus tshawytscha) in a laboratory model that simulated a turbine intake and gatewell (a vertical shaft in a dam that extends from the forebay deck to the ceiling of the intake). The study was part of a program to develop methods for preventing mortality of juvenile salmon and steelhead trout (Salmo gairdneri) in Kaplan turbines of low‐head dams on the Columbia and Snake Rivers. If large numbers of juvenile fish could be guided into gatewells, a method of safely bypassing them around turbines might be devised. Three types of screens (wood, and single and double layers of spiral‐weave conveyor belt) were attached to the intake ceiling at an angle of 45° to the flow; their lengths were adjusted to intercept one‐third or two‐thirds of the total flow into the intake. The screen with the greatest porosity (constructed of a single layer of belting) gave the highest guiding efficiency; 87% of the test fish were diverted into the gatewell. We believed that water deflected under the screen carried fish with it, but our tests indicated that some fish swam upwards out of the flow and into the gatewell. Diversion of 3% of the intake flow up through a gatewell with a single opening into the intake increased the guiding efficiency of only the double‐layer screen. Diversion of flow through a gatewell with two openings caused a significant percentage of the guided fish to leave the gatewell and reenter the intake.
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