Failure to Protect Winter-Run Salmon in Fall 2019

In a December 2018 post, I focused on the importance of fall pulse flows in moving winter-run salmon juveniles downstream in the Sacramento River to the Delta and Bay. Without pulse flows, the juvenile winter-run are less likely to make or survive the downstream move from spawning and early rearing areas in the upper river. They are thus less likely to reach the ocean and contribute to subsequent recruitment into the adult population.

A gradual recovery of adult spawners, egg production, and wild fry production (Figure 1) has been helping recovery of the winter-run population since the population crash during the 2012-2015 drought. Wild fry production as estimated from Red Bluff screw trap collections is up sharply in 2019 (Figure 2 top chart).

However, in fall 2019, winter-run fry have received even less support in terms of river flow in their important journey to and through the Bay-Delta than in previous years. Numbers caught in lower river screw traps are very low (Figure 2 bottom chart), reflecting low movement rates from the upper river and poor survival. Both factors are a consequence of poor river flows. There are simply no reasons for Reclamation to be so stingy with Shasta Reservoir releases this fall, after a very wet year in 2019 and with Shasta Reservoir at or near a record-high level for this time of year.

A close-up of the Figure 2 data in Figure 3 shows some effort on the part of Reclamation to provide flow pulses,1 but the effort was not enough. Furthermore, Reclamation subsequently offset its meager augmentation by cutting reservoir releases in November (Figure 4). The November reduction further compromised the emigration and survival of juvenile winter-run salmon. Reclamation’s tendency to cut releases in fall and winter, the period when winter-run most depend on river flows, is pronounced in all but the wettest years (2011 and 2017) over the past decade (Figure 5). Such tendency probably has been deemed acceptable because downstream tributary flows (Battle Creek, Cow Creek, etc.) provide fall flow pulses in some years (e.g., fall 2016 Figure 6, fall 2011 Figure 7). But inflow pulses from those tributaries are downstream of the Redding spawning reach; in the spawning reach, flows come almost exclusively from Shasta Reservoir releases.

What is needed are modest flow pulses from Shasta Reservoir in fall, especially when pulses in downstream tributaries occur. Releases for several days in the 10,000-15,000 cfs range, or of slightly less magnitude when coincident with tributary flow pulses, would help emigration (and survival) of winter-run juvenile salmon from the upper river. Such pulses should not be followed by offsetting flow decreases, as have occurred this fall (Figures 3 and 4). Low flows following fall pulses cause redd dewatering or fry stranding of spring-run, fall-run, and late-fall-run salmon, which spawn in the upper river later in the season than winter-run.

The late November 2019, Thanksgiving week storm should provide ample Shasta storage and tributary flows to allow modest flow pulses from Shasta Reservoir. Such flow pulses would benefit all four salmon runs in the Sacramento River.

Figure 1. Emigration timing of juvenile winter-run salmon from the upper Sacramento River and the estimated number of juvenile salmon (millions) passing Red Bluff during water years 2004-2018. Note the poor production in critically dry 2014 and 2015 from loss of cold-water pool and associated catastrophic egg mortality.

Figure 1. Emigration timing of juvenile winter-run salmon from the upper Sacramento River and the estimated number of juvenile salmon (millions) passing Red Bluff during water years 2004-2018. Note the poor production in critically dry 2014 and 2015 from loss of cold-water pool and associated catastrophic egg mortality.

Figure 2. Daily estimated juvenile winter-run salmon catch per trap day passing Red Bluff in the upper river and Tisdale Weir in the lower river in summer-fall 2019. The numbers passing Red Bluff are strong, especially when one considers that they were the offspring of poor brood-year 2016.  

Figure 2. Daily estimated juvenile winter-run salmon catch per trap day passing Red Bluff in the upper river and Tisdale Weir in the lower river in summer-fall 2019. The numbers passing Red Bluff are strong, especially when one considers that they were the offspring of poor brood-year 2016.

Figure 3. Daily estimated juvenile winter-run salmon passage per trap day at Red Bluff in the upper river, also showing river flow in summer and fall 2019.

Figure 3. Daily estimated juvenile winter-run salmon passage per trap day at Red Bluff in the upper river, also showing river flow in summer and fall 2019.

Figure 4. Shasta/Keswick Dam releases in fall 2019, along with daily median flow average for 55 years.

Figure 5. Shasta/Keswick Dam daily average releases from 2009-2019, along with daily median flow average for 55 years.

Figure 6. Daily estimated juvenile winter-run salmon passage per trap day passing Red Bluff in the upper river and Tisdale Weir in the lower river in fall 2016. Note that the flow pulses (and associated higher catches) in early and late November were from tributary storm-related inflows. Such events had not occurred as yet in 2019 (Figure2).

Figure 7. Daily estimated juvenile winter-run salmon passage per trap day passing Red Bluff in the upper river and Tisdale Weir in the lower river in fall 2010. Note the flow pulses (and associated higher catches) in late October and in December.

 

 

 

  1. Reclamation’s sporadic 2000 cfs flow pulses in late October observable in Figures 2 and 3 were likely part of Reclamation’s contribution to maintaining Delta inflow and outflow for the Fall X2 requirement.

Sustaining wild Salmon and Steelhead above Central Valley dams

The Case for Two-Way Trap and Haul

Why should we expand spawning populations of listed salmon and steelhead to areas above dams and impassible falls in the Central Valley? The answer is: because the genetic makeup and wild traits of populations upstream of existing barriers can be controlled, restored, and preserved.

At present, the genetic makeup of salmon and steelhead populations below dams is continually being compromised by hatchery fish and strays to and from other watersheds. The one population of winter-run Chinook is confined to the spawning reach immediately below Keswick Dam and thus is subject to the potentially drastic whims of nature and man. That population is further being compromised by the increasing threat of hatchery degradation of the gene pool as winter-run hatchery fish further dominate the adult spawning population. Small, self-sustaining populations of spring-run Chinook and steelhead remain in only a few watersheds. They too are continually being threatened by strays and hatchery fish.1

One solution to maintaining genetic integrity by limiting genetic influence from hatchery-produced fish and interbreeding of genetically or behaviorally distinct runs is to implement trap-and-haul programs in isolated reaches above dams.

The National Marine Fisheries Service included requirements to establish winter-run Chinook trap-and-haul populations above Shasta Reservoir in 2009, 2010, and 2014 biological opinions on Central Valley Project (CVP) and State Water Project (SWP) operations. CALFED proposed introducing spring-run Chinook above Yuba River dams. Extensive studies have been conducted on reintroducing salmon in these areas. The requirement to establish populations upstream of Shasta has been dropped in the Trump administration’s October 2019 biological opinion for the CVP and SWP. For the moment at least, the requirement remains in state of California plans.2

The California Department of Fish and Wildlife’s California Endangered Species Act Take Permits for CVP and SWP operations should require reintroduction of salmon and steelhead upstream of an array of dams in the Sacramento River watershed. All of the sites I recommend are affected by the CVP and SWP. The state should also consider locations in the San Joaquin and Klamath River watersheds. The Klamath watershed is also affected by Reclamation’s Klamath Project, and is the present subject of the country’s largest dam removal project.

In considering potential sites I focused on the ability to maintain experimental controlled conditions as well as optimum habitat quality sites. In most cases, that meant minimal flow variation and high quality, cold reaches dominated by spring water. The sites need not be in the historical range, but should be in historically occupied watersheds (e.g., they could be upstream of impassible falls in watersheds that historically held salmon and steelhead.).

I suggest five sites in the Sacramento River watershed (Figure 1).

  1. Upper Sacramento River (above Lake Shasta) – below Lake Siskiyou dam upstream of Dunsmuir in the Box Canyon/Shasta Springs reach.
  2. Upper McCloud River (above Upper McCloud Falls) – spring-fed reach above Larkin Dam on south flank of Mt Shasta.
  3. Upper Battle Creek – Ripley Creek, tributary of South Fork, spring-fed, although presently its flow is diverted by PG&E to South Fork Powerhouse.
  4. Upper North Fork of Feather River – above or below Lake Almanor.
  5. Upper North Yuba River – above Bullards Bar Reservoir.

I have studied all of these sites and consider them feasible for reintroduction. Most have been considered for reintroduction by state and federal resource agencies. Reintroduction strategies may include releases of native-strain adult spawners, planting of eyed eggs, fry, or fingerlings, then capture and trucking to locations downstream of dams.

For more on reintroducing salmon above dams see:
https://podcast.barbless.co/reintroduction-of-winter-run-chinook-into-the-mccloud-river-jon-ambrose-noaa-nmfs/

https://www.webpages.uidaho.edu/UIFERL/pdf%20reports/Keefer%20et%20al.%20%202010%20WIL%20Chinook%20prespawn%20mortality%201.pdf

https://fishwithjd.com/2015/05/07/new-plan-developing-to-get-spring-chinook-into-north-yuba-upstream-of-bullards-bar-reservoir/

Figure 1. Historical range and present range of salmon in Sacramento-San Joaquin watershed, with suggested five locations for reintroduction via two-way-trap-and-haul shown as red dots.

Reclamation and DWR Maintain Fall X2 at Chipps Island in 2019 for the Last Time

Despite falling river flows and lower reservoir releases, the US Bureau of Reclamation and the California Department of Water Resources maintained Delta outflows and the prescribed fall salinity in the Delta (X2 located at Chipps Island, River Kilometer 74) in the last half of August, September and October 2019. They did this by sharply reducing Delta exports (Figures 1 and 2). These actions helped to maintain low salinity habitat in (and flow through) Montezuma Slough in Suisun Marsh (Figure 3).

High Delta outflow and reduced Delta exports in September and October are good for all Delta native fishes. These conditions protect wild juvenile winter run salmon that began migrating downstream into the Delta (Figure 4). Delta smelt and longfin smelt remained in the Bay, west of the Delta.

Fall X2 was a provision of the 2008 and 2009 Biological Opinions for the Long-Term Operations of the Central Valley Project and the State Water Project. It applied only in Wet and Above Normal water years. New Biological Opinions released in October 2019 have moved the initial compliance point for the Fall X2 requirement upstream to River Kilometer 80, reducing low salinity habitat by pushing it further up into the Delta. 1

 Figure 1. Delta Exports (TRP and HRO) and Outflow (DTO), and Lower Sacramento River flow at Wilkins Slough (WLK), Verona (VON), and Freeport (FPT).

Figure 1. Delta Exports (TRP and HRO) and Outflow (DTO), and Lower Sacramento River flow at Wilkins Slough (WLK), Verona (VON), and Freeport (FPT).

Figure 2. Salinity (EC) at Mallard Island (km 74), the Fall X2 prescribed location under 2008 Delta smelt biological opinion. X2 is approximately 3800 EC.

Figure 2. Salinity (EC) at Mallard Island (km 74), the Fall X2 prescribed location under 2008 Delta smelt biological opinion. X2 is approximately 3800 EC.

Figure 3. Salinity (EC) in Montezuma Slough in late summer and fall 2019.

Figure 3. Salinity (EC) in Montezuma Slough in late summer and fall 2019.

Figure 4. Winter run catch in juvenile salmon monitoring in summer-fall 2019. Sacramento beach seine stations are in the north Delta.

Figure 4. Winter run catch in juvenile salmon monitoring in summer-fall 2019. Sacramento beach seine stations are in the north Delta.

  1. For discussion of the new biological opinions, see The Good, the Bad, and the Ugly in the New Non-Jeopardy Biological Opinions for CVP/SWP, http://calsport.org/fisheriesblog/?p=2889

Klamath’s Shasta and Scott Rivers – Update Fall 2019

In two May 2017 posts1, I discussed the status of fall-run Chinook salmon in the Scott River and Shasta River through the 2016 runs. This post updates the escapement record for the two rivers through the 2018 runs with preliminary data on the 2019 runs.

Scott River

After a slight uptick in the run in 2017, the Scott fall-run 2018 escapement fell below the 2015-2017 runs (Figure 1); all were affected by the 2012-2016 drought. The run total as of mid-October 2019 was 23. It is too early for a coho update, but the run continues at minimum levels2 with a disappointing strong-brood-year 2016 performance3. A poor 2016 run is likely to lead to a poor 2019 run.

Shasta River

In sharp contrast to the Scott, the Shasta River run continues to improve over its historical record (Figure 2). The run total as of mid-October 2019 was 2,722. The Shasta River coho population remains at critically low levels.

The remarkable recent success of the Shasta River Chinook run from habitat restoration and improvements in water management (and the lack thereof on the Scott River) continues to be undermined by misinformation promoted within the agricultural community. A February 2019 article in the news outlet Grist reported:

In 2016, The Nature Conservancy announced plans to sell Shasta Big Springs Ranch. But without its water, which California Fish and Wildlife still owns, the land isn’t of much use for agriculture. And the fish don’t seem to be doing much better, either — though salmon still spawn at Big Springs, their numbers continue to fluctuate wildly from year to year. It seems that in this ecosystem so changed by people, the salmon need some local stewardship to thrive…

The Scott River remains “the most productive coho stream in California,” according to the nonprofit California Trout. When I spoke to Plank last he told me that the river was splashing. “These fish hatched on this ranch during the last drought,” Plank said. “Today, they’re returning.” [emphasis added]

The article asks the rhetorical question: “So how did such similar conservation efforts go so right at Scott River Ranch and so wrong at Shasta Big Springs Ranch?” For fall-run Chinook, at least, the numbers tell a different story. As for coho, there is no evidence that the population is going anywhere but downhill.

The difference in water management between the two rivers is readily seen in the flow records over the last four years (Figures 3 and 4). The Shasta River has improved flows, whereas the Scott River has had historically low fall flows that keep salmon from ascending from the Klamath to the Scott River spawning grounds. Low summer and fall flows (Figure 3) have also led to very poor survival of young coho and Chinook salmon over-summering in the Scott River.

Figure 1. Escapement of adult fall-run Chinook salmon to the Scott River from 1978 to 2018. Data source: CDFW.

Figure 2. Escapement of adult fall-run Chinook salmon to the Shasta River from 1978 to 2018. Data source: CDFW.

Figure 3. Scott River streamflow 2016-2019. Source: https://nwis.waterdata.usgs.gov/


Figure 4. Shasta River streamflow 2016-2019. Source: https://nwis.waterdata.usgs.gov/

 

 

The Good, the Bad, and the Ugly in the New Non-Jeopardy Biological Opinions for CVP/SWP

The Endangered Species Act (ESA) directs all federal agencies to work to conserve endangered and threatened species and to use their authorities to further the purposes of the Act. The purpose of the Act is to protect and recover imperiled species and the ecosystems upon which they depend. Protect means to not allow “take” of listed species. If some take occurs despite best efforts, then “reasonable and prudent” alternatives (RPAs) may be needed to protect the threatened or endangered species.

The US Bureau of Reclamation and its partner the California Department of Water Resources (permittees) operate the federal Central Valley Project (CVP) and the State Water Project (SWP) under federal and state ESA “take” permits issued in 2008-2009 biological opinions that included RPAs. The RPAs constrained water supply deliveries and other project operations during the past decade to protect listed salmon, smelt, sturgeon, and steelhead.

Over the past decade, the parties have reinitiated consultation to revise take permits and RPAs. The initial motivation for reinitiation was that RPAs and take limits were not protecting or recovering the listed species. The US Fish and Wildlife Service (USFWS) and the National Marine Fisheries Service (NMFS) recognized that more stringent measures were needed. A series of draft opinions were developed with further protections, culminating with a July 1, 2019 draft jeopardy opinion from NMFS on Reclamation’s proposed action as of that time. A jeopardy opinion occurs when an action is reasonably expected, directly or indirectly, to diminish a species’ numbers, reproduction, or distribution so that the likelihood of survival and recovery in the wild is appreciably reduced.

Reclamation updated its “proposed action” in response to the draft jeopardy opinion. “It must also be acknowledged that the current status of all these species continues to be imperiled, and that one of the objectives of the proposed action is to maximize the available supply of water for irrigation, municipal, and industrial deliveries.”1 Reclamation doubled down. Reclamation’s most recent proposed action includes some provisions of the 2008/2009 biological opinions’ RPAs and recent jeopardy draft BO. In response, the Services relented under pressure from the Trump administration, replaced technical staff with a new group of managers, and recently issued final non-jeopardy opinions.

The new proposed action from Reclamation can now go into effect without RPAs that would hinder Reclamation from maximizing water deliveries. The new Biological Opinions will govern project operations under a wide array of vague commitments to protect and recover listed species: some good, some bad, and some simply ugly.2

The Good (Well, as Good as it Gets)

  1. Delta Smelt Conservation Hatchery
    This is long past due. However, the proposal is vague and limited in potential scope and funding commitment.
  2. New Habitat
    Most measures that require new habitat in the new BO were prescribed in past BOs. Now there are new vague commitments. Some listed species (e.g., Delta smelt) have populations too small to benefit from new habitat.
  3. Hatchery Management
    New and updated old prescriptions, though vague, are badly needed, especially for converting the program focus from mitigation hatcheries to conservation hatcheries.
  4. Proposed Funding for research and restoration
    The BOs contain an estimated total of $1.5 billion dollars in proposed funding to support threatened and endangered fish survival and recovery through research and restoration actions. However, the proposed funding is not dedicated and is vague, particularly in that much of the effort and funding may go to prior commitments that have not been funded.
  5. Delta Cross Channel Improvements
    Proposed upgrades to the Delta Cross Channel Gates are helpful but vague. The Delta Cross Channel should be screened, as should nearby Georgiana Slough.
  6. Modifying the Head of Old River Scour Hole
    This action is OK but addresses only one of many predation hotspots for salmon and steelhead caused by human actions and man-made structures in lower San Joaquin River.
  7. Fish Passage on Deer Creek (a non-Project watershed)
    This is one positive action for listed spring-run salmon among many in NMFS’s Central Valley Salmon Recovery Plan. All of the actions in the Recovery Plan should be included and funded. Deer Creek, a tributary to the lower Sacramento River, has a spawning run of wild spring-run salmon. Deer Creek does not have a project dam on it, but Deer Creek salmon pass through the lower Sacramento River and Delta. Deer Creek salmon and all other salmon-bearing tributary populations are thus affected by project operations.
  8. Adult Straying Barrier on the Knights Landing Outfall Gate (a flood and drainage system)
    This was constructed under prior commitments but failed.
  9. A “drought toolbox” to prioritize a proactive approach to drought planning, including early coordination with senior water right users
    Proactive coordination is fine and good, but the BOs contain no commitment to reduce diversions by senior Settlement and Exchange contractors or any others during droughts.
  10. Support for NMFS Steelhead Monitoring and Collaboration Activities with Non- Project Tributaries
    Monitoring may inform mitigation. However, monitoring in itself is not mitigation. All recovery plan actions should be supported because CVP/SWP operations and facilities have had major adverse effects on all Central Valley steelhead populations.
  11. $14 million commitment to expedited implementation of the Battle Creek Restoration Project including reintroduction of winter-run Chinook salmon
    The commitment to fund actions on Battle Creek is long overdue, but the funding in the BO is inadequate by an order of magnitude.
  12. A stronger commitment to actions maintaining low-salinity habitat in the Delta Smelt Summer-Fall Habitat Action with commitments regarding Suisun Marsh Salinity Control Gate (SMSCG) operations and projects for other elements of habitat
    It is important to acknowledge the importance of summer-fall habitat representing half of the smelt life-cycle, but the commitment in the BO is vague and likely ineffective as formulated. Rather than being used more often, the SMSCG should simply be removed. It has been a detriment to smelt, salmon, steelhead, and sturgeon populations since its use began in 1989.

The BAD

  1. Drought Mitigation
    Drought mitigation in the BOs focuses on maintaining Shasta Reservoir’s cold-water-pool. The proposed action drops mitigation actions for wet years such as Fall X2. The proposed action drops previous OMR constraints that provided some protection in drought years. The one-hand-giveth-while-the-other-taketh-away approach is an old tired gambit. The ostensible improvement at Lake Shasta eliminates numeric targets for Shasta carryover storage.
  2. Real time management – protect when and where the fish are
    This is poor prescription because some listed species populations are so low that they are undetectable (e.g., Delta smelt). Larval life stages also go undetected. Past detection rates even for larger populations have been poor, and actions to reduce impacts have been gamed and trimmed to the bone. Real time detection does not protect primary productivity and food sources and other elements of critical habitats. The managers charged with managing have a long history of choosing water supply over fish protection.
  3. A more detailed description of Shasta Dam operations and a commitment to Cold Water Management Tiers
    This prescription does not protect listed winter-run salmon in droughts from thermal shock or dewatering of redds, which are the primary factors in recent low survival and production. Prior RPA and Recovery Plan requirements to fix problems with Spring Creek powerhouse (Whiskeytown Lake thermal curtain) and Shasta Dam warm water power releases are not included in the new salmon BO.
  4. “New” Science
    A commitment to maintaining long-term monitoring programs and recognizing past and present science is needed. “New” science funded and conducted by water contractors or federal/state project operators will ensure any new science will be biased – foxes assessing their effects on the henhouse. The science and its presentation and analyses have become more and more controlled by water supply entities, and less and less by resource agencies. The BOs give more control of science to water suppliers. The revisions to the draft BOs are clear evidence of the new realignment of roles and new controls on science.
  5. Performance Metrics for managing Old and Middle River reverse flows to limit salmonid loss to similar levels observed under the previous BiOp through explicit reductions in export pumping.
    The BOs’ performance measures for reverse flows are vague, ineffective, and unenforceable. Wild components of salmon populations were hard hit in droughts under previous BOs. “Similar” levels of loss are not protective and will not promote recovery.
  6. Performance Metrics for incubation and juvenile production of salmonids under the proposed Shasta Cold Water Pool Management strategy
    The BOs’ performance measures for cold water management at Lake Shasta are vague, ineffective, and unenforceable.
  7. Commitments to manage Old and Middle River reverse flows for limiting larval and juvenile delta smelt entrainment based on modeled recruitment estimates
    OMR rules have been one of the major restrictions on exports under the past BOs. The rules proved beneficial to the listed species survival (primarily reduced salvage and improved through-Delta survival of tagged salmon smolts). The new strategy would allow changes that would allow greater levels of exports under OMR reverse flow prescriptions. The poor survival of San Joaquin salmon under existing rules would remain poor or further decrease. Entrainment of young smelt (not measured under existing rules), an existing serious concern, would only worsen. Modeling entrainment risk has not worked and has not been verifiable. The main risks to smelt are pulling larvae into the central Delta with its poor habitat (not just to the south Delta pumps) and the destruction of their critical pelagic rearing habitat.
  8. Independent Review Panels to evaluate the science behind actions and outcomes
    This is nothing new. There have been so many “independent” review panels. I remember working with Pete Chadwick back in the mid-70s. He consulted on my projects on the Hudson River Estuary. He and his CDFG staff working on the Bay-Delta were on the cutting edge of estuary science. They trained the next generation and they in turn trained the next. Outsiders have only verified what CDFG already well understood. Same goes for NMFS and the USFWS, as well as UC Davis. Together as IEP they manage Bay-Delta and Central Valley science more than adequately with the help of a huge cadre of capable scientists among NGOs. Water agencies and other water suppliers just can’t handle the truth, so they hire their own consultants and many outside “independent” consultants.
  9. Ramping rates specificity for reservoir releases to reduce the risk of stranding
    Ramping rates do not work for eggs and fry salmon that are in gravel beds for up to several months. Reductions in flows from Keswick Reservoir after winter-run fry have left their nests (redds) in the fall strands up to 80% of new fall-run redds.

The Ugly

  1. Commitment to implement appropriate actions after two years of low winter-run Chinook salmon egg-to- fry survival.
    Shasta operations in the 2014 and 2015 drought killed 90-95% of the egg production of winter-run salmon. The new Salmon BO would make that acceptable under the ESA. It would stretch the no-take standard to no take in more than two years out of three.
  2. More specificity on collaborative planning with specific habitat restoration and facility commitments.
    More planning for habitat restoration and facilities is not needed. Reclamation, DWR and other responsible agencies should get on with prior commitments. The history of foot-dragging on habitat restoration in the Central Valley is a worthy rival to the foot-dragging by PG&E in maintaining and upgrading its infrastructure.
  3. A commitment to sediment supplementation and food-web studies for the protection of delta smelt.
    As proposed the supplementation of sediment would come in the form of the discharge of warm, polluted agricultural drainage water full of non-native predatory fish into critical habitats of listed fish.
  4. Dynamic, real-time monitoring of changing conditions and potential species impacts, within an improved scientific and adaptive-management-based decision-making framework; avoiding or minimizing fishery impacts while increasing operational flexibility.
    Real time management will not work for rarer listed species like Delta smelt. This has been tried for three decades and has not worked. The adaptive managers will be the same managers who produced the revised non-jeopardy BOs. “Operational flexibility” is a buzzword for increased diversions, primarily Delta exports.
  5. Operational rules that lay the foundation for eventual voluntary agreements on water flows for rivers that feed into the delta. Those agreements promise even greater protections and investments in fish and the environment.
    Most of the “even greater protections” will have to backfill the protections that these BOs took away. The Voluntary Agreements offer pennies on the dollar in terms of necessary flow through the Delta into the San Francisco Bay.
  6. Eliminating or Modifying Existing RPAs and Take Limits
    • Modifying year-round temperature and Shasta reservoir storage management program to minimize effects to endangered winter-run salmon.
      NMFS and CDFW were just starting to get it right. NMFS’s 2017 draft RPA for Shasta would have required stronger carryover storage requirements.
    • Long-term passage prescriptions at Shasta Dam and re-introduction of winter-run to its native habitat in the McCloud and/or Upper Sacramento Rivers.
      They were ready to start this program after promising initial feasibility studies. The foot draggers strung it out until Trump administration officials threatened in 2019 to arrest DWR personnel who were installing equipment to begin a pilot implementation.
    • Old and Middle River flow levels that limit the strength of the reverse flows
      There will be less of the needed restrictions under Reclamation’s new plan.
    • Prescriptions for additional technological measures at the facilities to enhance screening and increase survival of fish.
      There will be fewer planned upgrades to project facilities to protect fish than were promised under the previous BOs.
    • Prescribed additional measures to improve survival of San Joaquin steelhead smolts, including both increased San Joaquin River flows and export curtailments.
      No longer apply.
    • Prescribed flow management standard, a temperature management plan, additional technological fixes to temperature control structures, and, in the long term, a passage at Nimbus and Folsom dam to restore steelhead to native habitat.
      No longer apply.
    • Prescribed year-round minimum flow regime necessary to minimize project effects to each life-stage of steelhead, including new springtime flows that will support rearing habitat formation and inundation, and create pulses that allow salmon to migrate out successfully.
      No longer apply.
    • The Fall X2 provision has been eliminated.
      This flow-salinity RPA protected longfin and Delta smelt in summer and fall of wet years.
    • Take limits have been eliminated.
      They should have been revised to be more protective.

What is Missing

So much is missing that is within state and federal governments’ power and authority in the final approved Reclamation proposal. Here is a limited selection.

  • Effective Management of Shasta Cold-Water Pool
    Missing from the BOs are controls of Spring Creek powerhouse warm water releases into Keswick Reservoir, modifications to hydropower operations, long term Shasta storage rules, and modifications of water contractor deliveries. Combinations of these actions would have alleviated winter run salmon recruitment failures in 2014 and 2015. Reclamation’s approved proposal would allow such drastic recruitment failures in future droughts.
  • Commitment to comply with water quality standards on flow, water temperature, salinity, and export restrictions
    Reclamation has made no commitment to comply with state water quality standards or other state laws.
  • Commitment to provide needed pulsed flows
    Coordinated pulsed flows are needed to increase survival of hatchery and wild salmon. None are included in Reclamation’s plan, with the possible exception of a pulse from Shasta when it is likely to spill anyway.
  • Commitment to implement recovery plan actions
    Recovery, not just protection, is needed and is required by the ESA. These BO’s do not address recovery plans. The ESA goes beyond simple mitigation. The ESA focuses on minimization of effects, enhancement, and recovery.

In Conclusion: Ugly

Reclamation’s proposed action has been approved by the Services. The proposed action includes some good concepts for protective measures (though generally the requirements are vague, underfunded and not enforceable), and a suite of bad and downright ugly actions that will harm affected listed fish species. The overall mix will lead to much confusion, wringing of hands, blaming, ignoring of responsibility, initial lawsuits, and (if the initial lawsuits fail) further lawsuits when fish metrics fail to show improvement. Some actions will take time to implement, while some are already too little too late.

The Services should have issued jeopardy opinions with a suite of appropriate RPAs. That did not happen. Instead, the Services are allowing further risk of extinction to the listed species. The best example of this is allowing expected temperature-dependent egg mortality levels for Sacramento River winter-run Chinook salmon to occur in “Tier 3 and 4 years.” Mortality due to allowed temperature exceedance was a major cause in the recent decline in the winter-run salmon population, one of the few species listed as “endangered” rather than the more common “threatened” designation. The effect the salmon BO will allow is entirely avoidable and within the control of the state and federal agencies involved in permitting the CVP. NMFS has designated winter-run as a “Species in the Spotlight”; it’s more likely that it is now a “Target for Extinction.”

  1. USFWS summary, p. 13.
  2. The US Fish and Wildlife Service’s summary of both its own Biological Opinion for smelt and the National Marine Fisheries Service’s Biological Opinion for salmon, steelhead and green sturgeon is available at: https://www.fws.gov/sfbaydelta/cvp-swp/documents/ROC_on_LTO_Summary_FINAL.pdf
    For the complete USFWS and NMFS Biological Opinions and appendices, go to: https://www.fws.gov/sfbaydelta/CVP-SWP/index.htm