Life History Assessment of Cusk, a Data‐Poor Species, in U.S. Waters

Abstract

Cusk Brosme brosme are fished across the northern Atlantic Ocean, but even basic biological data are limited in part by their difficult‐to‐sample deep and structured habitats. We sampled fish from a variety of sources across the Gulf of Maine to provide comprehensive life history information (age and size at maturity, fecundity, sex ratio, growth) for this data‐poor species considered by National Oceanic and Atmospheric Administration Fisheries as a species of concern. Gonad histology and gonadosomatic index data indicated peak spawning in late spring (May–June), with limited spawning activity into summer. The histologically derived length at 50% maturity for female Cusk was 39.5 cm TL. Fecundity varied from a quarter million to four million oocytes, with a positive allometry versus size indicating that larger females have proportionally higher fecundity than smaller females. Male Cusk had unusually low gonadal investment for a gadiform, and males of all sizes examined (down to 21 cm) had spermatozoa present. Male maturity was equivocal even when the relative proportions of sperm stages were quantified through image analysis of gonad histology; further anatomical and physiological studies of small males are required to assess functional maturity in male cusk. The sex ratio at length indicated more males at larger sizes, and males had faster growth and larger size at age than females. Condition patterns also suggested lower condition for females than males after spawning and generally less variable condition for males. Gonadal investment, relative condition, and growth patterns all suggest differences in energy allocation between the sexes. This data‐poor species has an uncertain stock status in U.S. waters; therefore, the results of the current work provide important information to its management.

A longline survey for spurdog distribution and life history along the Norwegian coast

“…Similarly, tusk and common ling were sampled in much of the surveyed area. Such species are considered data‐limited due to gaps in data, unreliable age estimates, and difficulties related to sampling at depths and habitats they usually inhabit (Elvarsson et al., 2018; Kutti et al., 2014; McElroy et al., 2022). These boreal species are vulnerable to depletion and climate warming due to their large size, long generation time, slow growth, late maturity, and low fecundity (Cheung et al., 2022; Lloret et al., 2021; Serrat & Muñoz, 2022), and thus demand greater monitoring and research efforts to improve assessments, like many elasmobranchs.…”