When first hatched, and before the disappearance of the yolk sac, the larvae (European) feed on larval snails and crustaceans, on diatoms, and on peridinians, but they soon begin taking copepods, and depend exclusively on these for a time after they get to be 12 mm. long, especially on the little Pseudocalanus elongatus. As they grow older they feed more and more on the larger copepods and amphipods, pelagic shrimps, and decapod crustacean larvae.
"The herring is a plankton feeder.... Examination of 1,500 stomachs showed that adult herring near Eastport were living solely on copepods and on pelagic euphausiid shrimps (Meganyctiphanes norwegica), fish less than 4 inches long depending on the former alone, while the larger herring were eating both." (Collette et al., 2002)
When first hatched, and before the disappearance of the yolk sac, the larvae (European) feed on larval snails and crustaceans, on diatoms, and on peridinians, but they soon begin taking copepods, and depend exclusively on these for a time after they get to be 12 mm. long, especially on the little Pseudocalanus elongatus. As they grow older they feed more and more on the larger copepods and amphipods, pelagic shrimps, and decapod crustacean larvae.
Boosted regression tree (Molina 2024) investigated relationships between environmental indicators and Atlantic herring recruitment estimated in the assessment.
Larval and juvenile food (zooplankton), egg predation, and temperature always highest influence
Maps of key areas for Herring assessment indices. The full VAST model grid is shown in brown.
NEFSC survey strata definitions are built into the VAST northwest-atlantic
extrapolation grid already. We defined additional new strata to address the recreational inshore-offshore 3 mile boundary. The area within and outside 3 miles of shore was defined using the sf
R package as a 3 nautical mile (approximated as 5.556 km) buffer from a high resolution coastline from thernaturalearth
R package. This buffer was then intersected with the current FishStatsUtils::northwest_atlantic_grid
built into VAST and saved using code here. Then, the new State and Federal waters strata were used to split NEFSC survey strata where applicable, and the new full set of strata were used along with a modified function from FishStatsUtils::Prepare_NWA_Extrapolation_Data_Fn
to build a custom extrapolation grid for VAST as described in detail here.
Use as a basis the new herring stock assessment in Woods Hole Assessment Model (WHAM) (Stock et al., 2021).
We are using the devel
version of WHAM: https://github.com/timjmiller/wham/tree/devel
Model mm192 is our starting point.
Zooplankton indices were explored as covariates on herring recruitment.
Recruitment is modeled as deviations from the "recruitment scaling parameter", leaving one option for modeling effects of covariates on recruitment: "controlling".
A "controlling" recruitment covariate results in a time-varying recruitment scaling parameter.
We explored indices with different zooplankton groups, seasons, and regions according to herring life history and results from the boosted regression tree:
We evaluated
Short story:
Under the above conditions, most models with and without the recruitment link converged for all covariates
Models with the Jan-Jun (Spring) large copepods covariate also converged with input as millions of cells and VAST estimated SE
I'm still figuring out where to find all the diagnostics in WHAM, so "converged" may not be "a good model"
Way too much detail including false starts
Models with no covariates had slightly better AIC than comparable models with recruitment links
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m10 ar1 none logmean-est_1 TRUE TRUE -1793.611 0 -3325.2 0.8684 0.5901 -0.2314 m14 ar1 controlling-lag-0-linear logmean-est_1 TRUE TRUE -1794.325 0.6 -3324.6 0.8999 0.5844 -0.2296 m2 rw none logmean-est_1 TRUE TRUE -1790.837 3.5 -3321.7 0.8683 0.5901 -0.2314 m6 rw controlling-lag-0-linear logmean-est_1 TRUE TRUE -1791.227 4.7 -3320.5 0.8844 0.5846 -0.23 m11 ar1 none meanmil-logsigmil TRUE TRUE -1509.570 566.1 -2759.1 0.8682 0.5901 -0.2314 m15 ar1 controlling-lag-0-linear meanmil-logsigmil TRUE TRUE -1510.349 566.5 -2758.7 0.9081 0.592 -0.2379 m3 rw none meanmil-logsigmil TRUE TRUE -1506.709 569.8 -2755.4 0.8594 0.5907 -0.2362 m7 rw controlling-lag-0-linear meanmil-logsigmil TRUE TRUE -1507.424 570.4 -2754.8 0.8104 0.594 -0.2448
Without covariate, recruitment variance is 0.823, and with is 0.797; lgCopeSpring2 beta_1 is -0.407, CI -1.063, 0.25
Without covariate, recruitment variance is 0.823, and with is 0.804; lgCopeSpring2 beta_1 is -0.45, CI -1.438, 0.538
Without covariate, recruitment variance is 0.823, and with is 0.791; lgCopeSpring2 beta_1 is -4.5\times 10^{-4}, CI -0.00128, 3.8\times 10^{-4}
Without covariate, recruitment variance is 0.823, and with is 0.793; lgCopeSpring2 beta_1 is -4.3\times 10^{-4}, CI -0.00126, 4\times 10^{-4}
Models with no covariates had slightly better AIC than the ar1 model with recruitment links
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m10 ar1 none logmean-est_1 TRUE TRUE -1797.177 0 -3332.4 0.8682 0.5901 -0.2314 m2 rw none logmean-est_1 TRUE TRUE -1796.175 0.1 -3332.3 0.8682 0.5901 -0.2314 m14 ar1 controlling-lag-1-linear logmean-est_1 TRUE TRUE -1797.931 0.5 -3331.9 0.8486 0.6001 -0.2333 m6 rw controlling-lag-1-linear logmean-est_1 TRUE FALSE -1794.370 --- --- --- --- ---
Without covariate, recruitment variance is 0.823, and with is 0.79; smcopeFall2 beta_1 is -1.013, CI -2.715, 0.689
Model with ar1 covariate had slightly better AIC than models without recruitment links
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m14 ar1 controlling-lag-1-linear logmean-est_1 TRUE TRUE -1791.900 0 -3319.8 0.814 0.5966 -0.2327 m2 rw none logmean-est_1 TRUE TRUE -1789.657 0.5 -3319.3 0.8683 0.5901 -0.2314 m10 ar1 none logmean-est_1 TRUE TRUE -1790.469 0.9 -3318.9 0.8683 0.5901 -0.2314 m6 rw controlling-lag-1-linear logmean-est_1 TRUE FALSE -1785.746 --- --- --- --- ---
Without covariate, recruitment variance is 0.823, and with is 0.77; smcopeSepFeb2 beta_1 is -0.85, CI -1.883, 0.182
Both rw and ar1 models worked with covariates, rw better fit
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m6 rw controlling-lag-1-linear logmean-est_1 TRUE TRUE -1791.981 0.0 -3322.0 0.7592 0.6023 -0.2327 m14 ar1 controlling-lag-1-linear logmean-est_1 TRUE TRUE -1792.464 1.1 -3320.9 0.7943 0.5971 -0.2329 m2 rw none logmean-est_1 TRUE TRUE -1790.196 1.6 -3320.4 0.8682 0.5901 -0.2314 m10 ar1 none logmean-est_1 TRUE TRUE -1790.734 2.5 -3319.5 0.8683 0.5901 -0.2314
Without covariate, recruitment variance is 0.823, and with is 0.762; smcopeSepFeb2 beta_1 is -1.01, CI -2.11, 0.089
Without covariate, recruitment variance is 0.823, and with is 0.757; smcopeSepFeb2 beta_1 is -0.976, CI -2.044, 0.093
Models with and without ar1 covariates linked to recruitment had the same AIC
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m2 ar1 none logmean-est_1 TRUE TRUE -1771.328 0.0 -3272.7 0.8682 0.5901 -0.2314 m4 ar1 controlling-lag-0/1-linear logmean-est_1 TRUE TRUE -1773.347 0.0 -3272.7 0.8529 0.5922 -0.2313 m1 rw none logmean-est_1 TRUE TRUE -1767.742 3.2 -3269.5 0.8683 0.5901 -0.2314 m3 rw controlling-lag-0/1-linear logmean-est_1 TRUE TRUE -1769.627 3.4 -3269.3 0.8001 0.5976 -0.2321
Without covariates, recruitment variance is 0.823, and with is 0.755; smcopeSepFeb2 beta_1 is -0.88, CI -1.929, 0.169
Sep-Feb small copepods m14
Same pattern by area
Model ecov_process ecov_how ecovdat conv pdHess NLL dAIC AIC rho_R rho_SSB rho_Fbar m4 rw controlling-lag-1-linear logmean-est_1 TRUE TRUE -1827.543 0 -3393.1 0.6543 0.5984 -0.2323 m3 rw none logmean-est_1 TRUE TRUE -1826.370 0.4 -3392.7 0.8682 0.5901 -0.2314 m8 ar1 controlling-lag-1-linear logmean-est_1 TRUE TRUE -1826.627 3.8 -3389.3 0.6714 0.598 -0.2324 m7 ar1 none logmean-est_1 TRUE TRUE -1825.511 4.1 -3389 0.8682 0.5901 -0.2314 m2 rw controlling-lag-1-linear mean-est_1 TRUE TRUE -1650.465 354.2 -3038.9 0.6473 0.5976 -0.2321 m1 rw none mean-est_1 TRUE TRUE -1649.265 354.6 -3038.5 0.8594 0.5907 -0.2362 m6 ar1 controlling-lag-1-linear mean-est_1 TRUE TRUE -1649.607 357.9 -3035.2 0.6643 0.5971 -0.2322 m5 ar1 none mean-est_1 TRUE FALSE -1644.890 --- --- --- --- ---
Without covariate, recruitment variance is 0.823, and with is 0.79; LarvalTempDuration beta_1 is 2.066, CI -0.657, 4.789
Without covariate, recruitment variance is 0.823, and with is 0.791; LarvalTempDuration beta_1 is 2.032, CI -0.711, 4.775
Collette, B. B. et al. (2002). Bigelow and Schroeder's Fishes of the Gulf of Maine, Third Edition. 3rd ed. edition. Washington, DC: Smithsonian Books. ISBN: 978-1-56098-951-6.
Stock, B. C. et al. (2021). "The Woods Hole Assessment Model (WHAM): A general state-space assessment framework that incorporates time- and age-varying processes via random effects and links to environmental covariates". En. In: Fisheries Research 240, p. 105967. ISSN: 0165-7836. DOI: 10.1016/j.fishres.2021.105967. URL: https://www.sciencedirect.com/science/article/pii/S0165783621000953 (visited on May. 26, 2021).
Slides available at https://noaa-edab.github.io/presentations
Contact: Sarah.Gaichas@noaa.gov
"The herring is a plankton feeder.... Examination of 1,500 stomachs showed that adult herring near Eastport were living solely on copepods and on pelagic euphausiid shrimps (Meganyctiphanes norwegica), fish less than 4 inches long depending on the former alone, while the larger herring were eating both." (Collette et al., 2002)
When first hatched, and before the disappearance of the yolk sac, the larvae (European) feed on larval snails and crustaceans, on diatoms, and on peridinians, but they soon begin taking copepods, and depend exclusively on these for a time after they get to be 12 mm. long, especially on the little Pseudocalanus elongatus. As they grow older they feed more and more on the larger copepods and amphipods, pelagic shrimps, and decapod crustacean larvae.
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