Recommendations for 2016 Delta Smelt Recovery

The Symposium on the possible extinction of smelt held on March 29, 2016 offered no real solutions or solid recommendations for recovery of the two smelt species on the brink of extinction.  My own presentation focused on the cause of the population crash of Delta Smelt, not prescriptions for recovery, which had been a topic of some of my previous posts on smelt in this blog.  The panel discussion at the end of the day of presentations brought out mostly old ideas and restoration strategies that have been unsuccessful over the past 40 years. There was little hope and a lot of pessimism from the panel.  Some panelists recalled that estuary flows and exports are likely important factors, but also lamented that these are hard to change.  Specific panelists held out hope that restoring wetlands and marshes, increasing aquatic food abundance, and reducing toxins might bring the smelt back under present water management.  With that background, I thought I should add my own suggestions for how to proceed during the year that may be our last opportunity to help smelt (Figure 1).

Figure 1. Summer Townet Survey indices 2002-2015. (2015 was zero.)

Figure 1. Summer Townet Survey indices 2002-2015. (2015 was zero.)

This year is a wetter year, not unlike the recovery year 2010 (Figure 1).  So if there is the same level of protection as in 2010, smelt might show signs of recovery with a positive response to good conditions.  However, if they do not respond favorably, it would suggest that Delta smelt need more drastic actions to prevent extinction. Below I describe the basic protections provided in 2010, recommend added actions, suggest several still more drastic prescriptions, and recall planned long-term actions that need to get moving.

Figure 2. Daily average Delta outflow spring 2010. Source: CDEC.

Figure 2. Daily average Delta outflow spring 2010. Source: CDEC.

Prescription 1 – Limit Spring Exports as in 2010

Year 2010 had relatively good spring Delta outflows (Figure 2).  So far, April, 2016 has also started modestly not unlike 2010, with Delta outflows between 20,000 and 40,000 cfs..  Unless there is more rain, we can expect a sharp drop in outflow later in April this year as reservoir flood control releases cease.  This would create flow conditions similar to those of 2010.   Given the likely releases from storage combined with declining runoff,  it would be reasonable to consider the actions prescribed in 2010 to protect smelt as a place to start this year: limit exports to about 1500 cfs.  There will be strong pressure soon to increase exports to the maximum allowed under the biological opinions (5000-6000 cfs) unless the US Fish and Wildlife Service accepts the recommendation of the Smelt Working Group and limits exports. The Service limited exports in 2010.  It has also largely done so in March and early April, 2016, to protect larval Delta Smelt that were observed in surveys in the lower San Joaquin River.  A low level of export of 1500 cfs and -1800 cfs OMR would be consistent with actions in April in 2010  (Table 1).  A low level of export may also be prescribed by NMFS to protect salmon and steelhead in April and May.

A continued low export prescription of a 2500 cfs limit through May 2010 was likely protective until such time as young smelt were able to transport downstream from Delta spawning grounds to the low salinity zone rearing area located in Suisun Bay under the 15,000-20,000 Delta outflows.  Figure 3 shows the continued presence of Delta smelt in the Delta during May 2010.

By June many smelt had reached the eastern Bay out of the influence of the export pumps (Figures 4 and 5).  Exports of 6300 cfs and -5000 OMR1 allowed under the Smelt Biological Opinion appeared to be protective in June 2010 as long as outflows were above 10,000 cfs.

Table 1.  Monthly average export rates and OMRs in spring 2010, the year following the drought years of 2007-2009 which exhibited some smelt recovery.

Month 2010 Exports 2010 OMRs
April 1500 -4600 to +1200
May 2400 -1100 to +1250
June 6300 -4800 to -1200

Prescription 2 – Sustain Delta Outflows through July

Delta outflows are necessary to move smelt west to Suisun Bay through the spring.  A minimum daily average outflow of 15,000 cfs in April and May would simulate 2010 outflows (Figure 2), and would be consistent with historical relatively wet year outflows.  These outflows are necessary to maintain the Low Salinity Zone west of the Delta in Suisun Bay, outside the influence of the South Delta export pumps.  In June and July, a daily average outflow of at least 10,000 cfs would sustain smelt and the Low Salinity Zone west of the Delta away from the influence of the South Delta export pumps, and would be consistent with outflows in 2010 and 2011.  The existing minimum monthly average outflow allowed in June of a wet or normal year under the Delta standards is 7100 cfs.  The minimum outflow allowed in July of a wet or normal year (2010) is a monthly average of 8000 cfs.  Daily averages could be adjusted to accommodate spring and neap tides as long as a minimum monthly average of 8,000-10,000 cfs is maintained.  Note near maximum exports (11,400 cfs) were maintained in July in both recovery years 2010 and 2011 with June-July Delta outflows at or above 8000 cfs, because an outflow of 8000 cfs for the most part keeps smelt west of the Delta, outside the influence of the pumps.

More Protective Prescriptions

  1. Maintain -5000 OMR limit in July. Though maximum exports were maintained in July 2010 and 2011, some smelt remained in the north Delta into the summer (Figure 6) and were vulnerable to such higher exports.  Lowering exports would save smelt (and pelagic habitat), water in storage, and reduce Delta water temperatures.
  2. Provide Delta daily minimum outflows of 15,000 cfs in June, 10,000 cfs in July, and 6,000 cfs in August. These outflows would be more consistent with June 2010 and July-August 2011, and would ensure that smelt and the Low Salinity Zone are maintained in Suisun Bay (Figure 7).
  3. Employ Fall X2 Wet-Year Prescription. Maintains X2 and Low Salinity Zone in Suisun Bay in fall.

Additional Prescriptions

  1. Open Delta Cross Channel in May and June. Opening the Cross Channel Gates will increase westward flow at Jersey Point (“QWEST”) and reduce the entrainment of smelt, the Low Salinity Zone, and Delta pelagic habitat by the export pumps.
  2. Install False River Barrier. Closing False River will reduce the entrainment of smelt and pelagic habitat into Franks Tract on flood tides from the lower San Joaquin River near Jersey Point.
  3. Increase spring and summer flow down Yolo Bypass into Cache Slough. Increasing inflows from Knights Landing Ridge Cut and the Sacramento Deepwater Ship Channel, and reducing diversions from the lower Yolo Bypass and Cache Slough, will increase net flows out of Yolo Bypass-Cache Slough complex into Sacramento River in west Delta.

Expedite Future Actions

  1. Divert water from the Sacramento River at Fremont Weir into Yolo Bypass in April and May. A proposed notch in the Fremont Weir would flood the Yolo Bypass in the spring of more water years and would increase the magnitude and duration of flood flows in years when the existing weir level allows flooding.
  2. Operate gate at upper end of Sacramento Deepwater Ship Channel. This will allow added inflow into the Ship Channel and lower Cache Slough Complex from the Sacramento River at the northern end of the Delta.
  3. Move the North Bay Aqueduct intake from the Cache Slough complex to the Sacramento River.
  4. Stock hatchery-reared Delta smelt into Low Salinity Zone in Suisun Bay in summer of wet years, or in late fall/early winter of drier years.
Figure 3. May 2010 Delta smelt distribution from 20-mm Survey.

Figure 3. May 2010 Delta smelt distribution from 20-mm Survey.

Figure 4. Early June 2010 Delta smelt distribution from 20-mm Survey.

Figure 4. Early June 2010 Delta smelt distribution from 20-mm Survey.

Figure 5. June 2010 Delta smelt distribution from Summer Townet Survey.

Figure 5. June 2010 Delta smelt distribution from Summer Townet Survey.

Figure 6. Late June 2010 Delta smelt distribution from 20-mm Survey.

Figure 6. Late June 2010 Delta smelt distribution from 20-mm Survey.

Figure 7. Early July 2011 Delta smelt distribution from 20-mm Survey.

Figure 7. Early July 2011 Delta smelt distribution from 20-mm Survey.

  1.  OMR is Old and Middle River flows in South Delta showing influence of South Delta export pumps when negative.  For example: exports near 6000 cfs create OMRS about -5000 cfs, the limit prescribed through June in the Smelt Biological Opinion.

San Joaquin Salmon Restoration – Update

On March 8, I posted some questions about the San Joaquin salmon restoration program and its upcoming release of hatchery smolts. On March 18, CDFW released 105,000 hatchery smolts into the San Joaquin River near Merced.1

The release coincided with the modest peak in annual San Joaquin River flow (Figure 1). Delta outflow peaked near 70,000 cfs at that time. Water temperatures were also below the stressful level of 68°F (20°C) (Figure 2). Smolt releases in the past two years did not have such good conditions, and few survived to reach the Delta. In contrast, in the week following this year’s release nearly 500 of these marked Spring-Run smolts have shown up in fish salvage at the South Delta export facilities , a clear indication that many survived to the Delta. The salvage numbers also indicate the released smolts had to take a tough route through the Delta with no assurance that they were successful in reaching the Bay even under the high wet year Delta outflows. It remains to be seen how well these smolt releases from the past three years fare in terms of survival to the Bay (Chipps Island Trawl Survey) and Ocean (coastal fisheries returns). I stand by my recommendation of barging the smolts to the Golden Gate, which would assure 99% survival to the Ocean.

Figure 1. Hourly flow in the San Joaquin River near Vernalis from March 5 to April 4, 2016.

Figure 1. Hourly flow in the San Joaquin River near Vernalis from March 5 to April 4, 2016.

Figure 2. Water temperature (Deg F) in the San Joaquin River below Merced from March 5 to April 4, 2016.

Figure 2. Water temperature (Deg F) in the San Joaquin River below Merced from March 5 to April 4, 2016.

Smelt Update – April 1, 2016

Since the last update, Delta and longfin smelt have continued their trends of record low numbers, as shown in the most recent Smelt Larvae Survey and 20-mm Survey. They are not yet gone, but close. It remains to be seen whether the good conditions provided so far in this wet winter 2016 can lead to some form of recovery for these two endangered species.

Longfin Smelt

With the high winter flows, the young from this year’s spawn are now distributed well to the west, although some remain in the north Delta (Figure 1). Their numbers continue at record low levels (Figure 2) despite a wet winter.

Figure 1. Longfin smelt catch in mid-March in Survey #1 of 20-mm Survey.

Figure 1. Longfin smelt catch in mid-March in Survey #1 of 20-mm Survey.

Figure 2. Average catch-per-unit-effort of young longfin smelt in mid-March 20-mm surveys from 2008-2016.

Figure 2. Average catch-per-unit-effort of young longfin smelt in mid-March 20-mm surveys from 2008-2016.

Delta Smelt

Delta smelt have yet to grow into the size range captured in the 20-mm Survey, but remain present in the last Smelt Larvae Survey (Figure 3). High winter through-Delta flows have resulted in a slightly more westward distribution than in recent drought years such as 2013 (Figure 4). Although numbers collected are very low, it is too early to determine relative production for 2016 compared to previous years in the Smelt Larvae Survey or the 20-mm Survey. Under similar wet winter-spring conditions in 2010 and 2011, Delta smelt had modest population improvements. It remains to be seen if the very low adult spawning population this year (in comparison to the populations in 2010 and 2011) can lead to some form of recovery in the population under this year’s relatively wet conditions.

Figure 3. Delta smelt larvae catch distribution in mid-March 2016 Smelt Larvae Survey.

Figure 3. Delta smelt larvae catch distribution in mid-March 2016 Smelt Larvae Survey.

Figure 4. Delta smelt larvae catch distribution in mid-March 2013 Smelt Larvae Survey.

Figure 4. Delta smelt larvae catch distribution in mid-March 2013 Smelt Larvae Survey.

Winter Run Salmon – “Species in the Spotlight”

Winter Run

Species in the Spotlight

The National Marine Fisheries Service (NMFS) has included the Sacramento River Winter-Run Chinook Salmon in its “Species in the Spotlight,”1 one of the eight species under NMFS’s jurisdiction nationwide that are most at risk of extinction.

On its website, NMFS describes the condition of Winter-Run (in italics below):

State and Federal Agencies, public organizations, non-profit groups and others in California’s Central Valley have formed strong partnerships to save Sacramento River winter-run Chinook salmon. Efforts to protect winter-run Chinook salmon include restoring habitat, utilizing conservation hatchery programs, closely monitoring the population, and carefully managing scarce cold water. Additional key actions needed to safe guard winter-run Chinook salmon from further declines include:

  • Improving management of Shasta Reservoir’s storage in order to provide cold water for spawning adults, eggs, and fry, stable summer flows to avoid de-watering redds, and winter/spring pulse flows to improve smolt survival through the Delta. (Note: badly needed as these actions have been generally lacking especially in the past two years.)
  • Completing the Battle Creek Salmon and Steelhead Restoration Project and reintroducing winter-run Chinook salmon to the restored habitat. (Note: Badly needed with little progress made in regard to Winter Run.)
  • Reintroducing winter-run Chinook salmon into the McCloud River. (Note: Badly needed with little progress made.)
  • Improving Yolo Bypass fish habitat and passage so juveniles can more frequently utilize the bypass for rearing and adults can freely pass from the bypass back to the Sacramento River. (Note: Badly needed with little progress made.)
  • Managing winter and early spring Delta conditions for improved juvenile survival. (Note: During the past four years of drought, Delta outflow has almost always been inadequate for emigrating juveniles.)
  • Conducting landscape-scale restoration throughout the Delta to improve the ecosystem’s health and support native species. (Note: Little progress has been made.)
  • Expanding LSNFH facilities to support both the captive broodstock and conservation hatchery programs; (Note: In progress. The hatchery program released 600,000 smolts in February last year and 400,000 in February this year. The releases are made in Redding where flows have been too low for good survival because Shasta Reservoir is retaining all its inflow. Much greater survival would be achieved if the smolts were trucked downstream to mid-river and then barged to the Bay.)
  • Evaluating alternative control rules used to limit incidental take of winter-run Chinook salmon in ocean fisheries. (Note: Ongoing and in progress. Fishery harvest for all races of Chinook will likely be curtailed this year.)

Number One Threat

The most serious threat to Winter Run and the major cause of the nearly complete loss of the past two years’ production relates to the first item in the above list: improving management of Shasta Reservoir cold water storage is essential. The change from a 58°F daily-average water temperature standard at Redding (last summer) to 53°F as proposed by NMFS will greatly help by alleviating sporadic lethal conditions that occurred last summer (Figures 1 and 2).

Achieving non-lethal conditions through the summer is possible by conserving Shasta Reservoir’s cold-water pool, which is best achieved by reducing inputs of warm water from Whiskeytown Reservoir (from Lewiston-Trinity reservoirs) into Keswick Reservoir via the Spring Creek Powerhouse (Figure 3). This source of warm water made up about 15% of the release to the Sacramento River from Keswick Reservoir, and required use of extra Shasta’s cold-water pool water to meet the relaxed temperature standard of 58°F in the upper Sacramento River below Keswick in Redding.

Another source of warm water to Keswick Reservoir was from daily afternoon peak power releases from Shasta Dam (Figure 4). High releases in afternoons raised water temperatures in Keswick Reservoir, requiring more cold-water pool release to compensate for warm water inputs. Apparently, the operations were too complicated for Reclamation to maintain the required 58°F average daily temperature at the mouth of Clear Creek (CCR gage: Figure 1). Operations at other times (e.g., first week in August) indicate clearly that Reclamation had the capability of keeping the water temperature well below lethal levels.

Figure 1. Lethal water temperature extremes for salmon eggs and fry (red circles) near Redding in summer 2015. Green circles denote non-lethal conditions that can be maintained with proper management of Shasta’s cold-water pool.

Figure 1. Lethal water temperature extremes for salmon eggs and fry (red circles) near Redding in summer 2015. Green circles denote non-lethal conditions that can be maintained with proper management of Shasta’s cold-water pool.

Figure 2. Episodes of high water temperature in Keswick Reservoir (red circles) in summer 2015. Peaks were due to hydropower peaking and specific operations of the Shasta Temperature Control Intake Tower to powerhouses at Shasta Dam.

Figure 2. Episodes of high water temperature in Keswick Reservoir (red circles) in summer 2015. Peaks were due to hydropower peaking and specific operations of the Shasta Temperature Control Intake Tower to powerhouses at Shasta Dam.

Figure 3. Warm water (red circle) entering Keswick Reservoir from Whiskeytown Reservoir via Spring Creek Powerhouse in summer 2015. Daily range of 1°F is due to hydropeaking operations.

Figure 3. Warm water (red circle) entering Keswick Reservoir from Whiskeytown Reservoir via Spring Creek Powerhouse in summer 2015. Daily range of 1°F is due to hydropeaking operations.

Figure 4. Warm water releases (red circle) from Shasta Reservoir during daily hydropeaking operations in summer 2015. Release water temperatures in the first week of August and September were lower because of lower afternoon hydropower peaking releases of warm water along with more night-morning cold water pool releases.

Figure 4. Warm water releases (red circle) from Shasta Reservoir during daily hydropeaking operations in summer 2015. Release water temperatures in the first week of August and September were lower because of lower afternoon hydropower peaking releases of warm water along with more night-morning cold water pool releases.

 

Feinstein Gets Some Water, but Smelt Get Some Back

In my March 12 post, I related that Senator Feinstein’s request for higher Delta exports would put the Delta Smelt population in the Delta at further risk of extinction. Well, she received her wish, and exports increased from 6000 cfs to 8000 cfs (11,400 cfs is maximum pumping capacity) in the week after her request when storms brought more inflow to Delta from the San Joaquin River.

However, the higher exports were short–lived, because the 3/14-3/17 Smelt Larvae Survey picked up larval smelt for the first time this year (Figure 1 – green dots). Exports dropped below 5000 cfs again. Though only two newly hatched larvae were collected in the central Delta, their presence is a concern. The presence of larval smelt shows that smelt are spawning in the lower San Joaquin River in the central Delta. According to the Smelt Working Group the net negative flows shown in red in Figure 1 for late March indicate a “medium” risk to smelt and a likelihood that larval smelt will be drawn toward the south Delta export pumps.1 The -5000 cfs Old and Middle River (OMR) reverse flows are the maximum allowed under the Smelt Biological Opinion.

In its review of the results of particle tracking model runs, the Smelt Working Group concluded: “Members stressed the importance of weighing more heavily the results from inserting (particles) at Prisoner’s Point, given the consistent catch of adults there this year and the hydrologic proximity of that location to the south Delta (as compared to Jersey Point). For OMR flow of -5000 cfs, approximately 20% of the particles inserted at Prisoners Point were entrained into the South Delta. For an OMR flow of -2500 cfs, approximately 10% of particles inserted at Prisoners Point were entrained into the South Delta. For an OMR flow of – 1250 cfs, less than 10% of particles inserted at Prisoners Point were entrained into the South Delta.” Prisoners Point is the green dot from the right on the Figure 1 map. In all likelihood, larval smelt are now being drawn or will soon be drawn into the south Delta. It is too early to determine what portion of the population is subject to this risk. But given the unprecedented depressed condition of the smelt population after four years of drought, the risk is significant.

On March 24, after review of “Smelt Working Group’s March 21 recommendations,2 the U.S. Fish and Wildlife Service “determined”3 that the OMR should be no more negative than -2500 cfs on a 14-day average, and no more negative than -3150 cfs on a five-day average. Reclamation took a slightly more liberal interpretation in the subsequent week’s operations (Figure 2), staying nearer -3500 cfs most of the week with no apparent interest in reaching a -2500 cfs 14-day average. It could be that the Service meant to recommend a -3500 cfs OMR limit. Or maybe the Service got a call from Senator Feinstein’s office. We shall see what this week’s meetings and determinations offer.

In any event, the risk to Delta Smelt remains “medium” at combined exports of about 3500-4000 cfs. With an export capacity of 11,400 cfs, Delta outflow still exceeding 50,000 cfs, reservoirs continuing to release snowmelt, and San Luis Reservoir in the San Joaquin Valley only half full, there will be continued cry for more exports and for approval of the Tunnels. In the meantime, it appears from Figure 1 that some smelt larvae and a good amount of snowmelt are escaping west to Suisun Bay, while some larval smelt remain at risk in the central Delta.

Figure 1.  Net daily flow in Delta in late-March 2016. (Gage data source:  USGS). Green dots are location of seven Delta Smelt larvae collected in Survey 6 of Smelt Larvae Survey (http://www.dfg.ca.gov/delta/data/sls/CPUE_Map.asp ).

Figure 1. Net daily flow in Delta in late-March 2016. (Gage data source: USGS). Green dots are location of seven Delta Smelt larvae collected in Survey 6 of Smelt Larvae Survey (http://www.dfg.ca.gov/delta/data/sls/CPUE_Map.asp ).

Figure 2. OMR March 23 to March 28.  (Source: CDEC)

Figure 2. OMR March 23 to March 28. (Source: CDEC)