Smelt -- Delta Actions Team Real-time Assessments

Weekly Assessment for Delta Operations on ESA and CESA-listed Osmerids

Last updated: Monday, March 02, 2026 at 3 PM

Executive Summary

• Entrainment management is currently active.
• Adult Delta smelt action is no longer active.
• Delta smelt were most recently detected at Suisun Marsh.
• No Delta smelt or longfin smelt salvage has been observed this water year.
• Turbidity in the central/south Delta is low to moderate.

Operational and Regulatory Conditions

• See current Weekly Fish and Water Operations Outlook document.
• Additional information also available on the SacPAS SMT page.

Delta smelt

Biological

• Delta smelt life stages:

• Abundance estimate: 9901 (95% CL: 1,407 to 35,401) as of the week of February 23–27, 2026

• Releases: A total of 163,349 cultured Delta smelt have been released for WY 2026. The most recent release of 24,606 fish occurred in Sacramento River at Rio Vista on Dec 16, 2025.

• Delta smelt count: 36 adult Delta smelt and 29 juvenile Delta smelt have been detected this water year. See Table 1 for recent detections, Figure 1 for spatial distribution, and Figure 2 for temporal distribution.

• Delta smelt salvage: 0 Delta smelt have been salvaged, and the cumulative seasonal salvage is 0.

Notes

• Since there are few recent detections of Delta smelt, estimation of distribution within the Delta is limited.
• As mentioned in EDSM reporting, fork length ranges reported for Delta smelt and longfin smelt life stages are defined by permit reporting purposes and are not intended to delineate cohorts or distinguish from hatchery or wild origin. See Table 1 caption for fork-length ranges for age groups of Delta smelt.
• See SacPAS SMT Page for additional details on releases and detection in surveys and salvage.
• Historical salvage trends can be found at: SacPAS Salvage Timing

Environmental

First Flush

• Implemented 12/25/25-01/7/26

Real-time Assessment Thresholds

Adult Delta smelt

• Adult Delta smelt action offramped on 02/12/2026

• No adult Delta smelt action was taken in WY26

• See Bay-Delta Live for recent Delta-wide turbidity conditions.

Larval/juvenile Delta smelt

Threshold: After the onset of spawning, if JPF < 0 cfs AND turbidity is \(\ge\) 12 FNU in the south Delta AND PTM modeling indicates the action would avoid \(\ge\) 5% entrainment of Delta smelt population after 30 days

• 12-station South Delta Turbidity: The most recent average turbidity was 5.7 FNU as of Feb 11, 2025

Evaluation

Delta smelt:

1. After the start of entrainment management, is JPF < 0, is daily average turbidity ≥ 12 FNU in the OMR corridor (stations OBI, HOL, and OSJ)? Has the average water temperature at Jersey Point or Rio Vista not exceeded 53.6\(^{\circ}\)F (12\(^{\circ}\)C) for 3 consecutive days and/or has this action already been taken during WY 2026?

   The adult Delta smelt entrainment action is not active and no action was taken in WY26. Temperature at Jersey Point exceeded the threshold on February 12th, 2025. Jersey Point 3-day average temperature was 12.05�C on February 10th, 12.09�C on February 11th, and 12.13�C on February 12th.

2. What is the evidence for the onset of Delta smelt spawning?

   Upstream migration for Delta smelt occurs between December and March and in response to “first flush” conditions (Sommer et al., 2011; Grimaldo et al. 2009; 2021). Historically, detections of ripe Delta smelt began in January and peaked in February and March and the majority of Delta Smelt spawning occurs at 11-15˚C (but can occur from 8-18˚C) (Damon et al. 2016). Based on historical monitoring data from the past few years, first detection of larvae in the Central and South Delta has typically occurred by mid to late March. The large majority of Delta smelt recaptures continue to be from Suisun Marsh, close to where supplemental fish were released in the fall.

3. After the onset of spawning, have the following conditions occurred: JPF < 0 cfs, average turbidity is \(\ge\) 12 FNU in the south Delta, and PTM modeling indicates the action would avoid \(\ge\) 5% entrainment of the Delta smelt population at facilities after 30 days?

   Although spawning may be occurring, JPF is above 0 cfs. SLS 5 is on the water this week and will provide an updated average south Delta turbidity. Due to JPF > 0 this week, the conditions required to trigger larval and juvenile Delta smelt entrainment management will not be met. No Delta smelt larvae have been captured in SLS surveys in WY26 to date. Therefore, if a Storm Flex were to be implemented this week, fates of particles injected at Chipps Island or Cache Slough would be most relevant for larvae, as those locations are closest to recent adult distribution. PTM with neutrally buoyant particles injected at Chipps Island and Cache Slough show 0% of particles entrained for the week ending 2/23/2026 for all OMR levels (-2,000, -3,500, -5,000, and -6,500 cfs). For week 2 (ending 3/02/2026), 0.1 and 0.3% of particles were entrained at CVP and SWP, respectively, at OMRI of -6,500 cfs, and 0% for OMRI of -5,000 cfs (see Appendix A for details). These results indicate that if Delta smelt larvae were present, the risk of entrainment under potential Stormflex operations would be low.

Longfin smelt

Biological

• Longfin smelt life stages: Adult, Juvenile

• Longfin smelt count: 413 adult, 972 juvenile, and 1776 larval longfin smelt have been detected this water year. See Table 3 for recent detections, Figure 3 for spatial distribution, and Figure 4 for temporal distribution.

• Longfin smelt salvage: 0 longfin smelt have been salvaged, and the cumulative seasonal salvage is 0.

Real-time Assessment Thresholds

Start of Entrainment Management (Adult Longfin Smelt)

• This action was not taken in WY26

Adult longfin smelt

• Threshold: JPF < 0 cfs, annual loss is on a trajectory to exceed 5% of the adult population abundance, and reduced exports will reduce entrainment in the south Delta
  • Daily average JPF: 9,820 cfs as of Mar 01, 2026
  • Adult abundance (Age 1+ LFS index): 2479.2 fish
    • 5% of abundance + 1: 125.0
  • Water year total adult longfin smelt salvage = 0

Larval/juvenile longfin smelt

• Threshold: JPF < 0 cfs AND population model demonstrates need to reduce entrainment to avoid population decline
  • Daily average JPF: 9,820 cfs as of Mar 01, 2026

Evaluation

Longfin smelt:

1. If JPF < 0, what is the trajectory of annual loss of adult longfin smelt and is it likely to exceed 5% of the adult population estimate? Is South Delta entrainment expected to decrease due to a reduction in export pumping?

   JPF is > 0 cfs and no adult longfin smelt have been detected in salvage, indicating annual loss has not begun to approach the 5% regulatory threshold.

2. For larval and juvenile longfin smelt, if JPF < 0 cfs, do particle tracking models show a moderate to high difference in particle fates across different OMRI scenarios? Does Zone of Influence modeling show moderate to high changes in hydrodynamic footprint across different OMRI scenarios? Are these effects anticipated to cause a population decline?

   JPF is currently not less than 0 cfs and is not predicted to drop below 0 cfs this week. Zone of Influence modeling indicates low differences in the hydrodynamic footprint across OMRI scenarios, with no change between current and forecasted conditions. If a Stormflex action were implemented, population-based PTM results, summarized in Appendix A, project low larval entrainment relative to estimated abundance. Modeled losses are approximately <0.1% under OMRI of both –5,000 and –6,500 cfs this week. For the week ending in 3/02/2026, larval entrainment is projected to be 0.2% and 0.3% of the larval LFS population at an OMRI of -5,000 and -6,500 cfs, respectively. These projected losses remain below levels suggesting population decline.

3. Is there additional information or other analyses that should be considered in this evaluation?

   Please see Appendix A for additional information.

End of smelt Entrainment Management

• Not relevant

References

Damon, L. J., Slater, S. B., Baxter, R. D., & Fujimura, R. W. (2016). Fecundity and reproductive potential of wild female delta smelt in the upper san francisco estuary, california. California Fish and Game, 102(4), 188–210.

Grimaldo, L. F., Smith, W. E., & Nobriga, M. L. (2021). Re-examining factors that affect delta smelt (hypomesus transpacificus) entrainment at the state water project and central valley project in the sacramento–san joaquin delta. San Francisco Estuary and Watershed Science, 19(1).

Grimaldo, L. F., Sommer, T., Van Ark, N., Jones, G., Holland, E., Moyle, P. B., Herbold, B., & Smith, P. (2009). Factors affecting fish entrainment into massive water diversions in a tidal freshwater estuary: Can fish losses be managed? North American Journal of Fisheries Management, 29(5), 1253–1270.

Sommer, T., Mejia, F. H., Nobriga, M. L., Feyrer, F., & Grimaldo, L. (2011). The spawning migration of delta smelt in the upper san francisco estuary. San Francisco Estuary and Watershed Science, 9(2).