By William Fleenor, Amber Manfree, and Megan Nguyen
Tides are the biggest driver of Delta flows, and in Episode 2 we look at their impacts in different locations under a variety of inflow conditions. Tides have a twice-daily cycle in the region, with a range of about six feet at Martinez. In the first part of the animation, we remove all in-Delta controls and diversions and fix inflows at a common moderate early summer level to isolate effects of tidal forces from those of inflows, gates, and export diversions. When the moon and sun are more aligned (full and new moon periods), tidal magnitude is greater. Distances to the moon and sun influence tidal magnitude as do winds and barometric pressure. Winds and barometric pressure are fixed in this animation.
The main lessons are:
Tidal ‘sloshing’ greatly exceeds Delta outflows. Tidal flows can be 400,000 to 600,000 cubic feet per second (cfs) at Martinez, while net outflows are often a few thousand cfs.
A given amount of tidal force exists at the Golden Gate, and a change in one location in the estuary has effects throughout.
Sacramento and Stockton Deep Water Ship channels have been deepened and straightened with dredging, which increases tidal flows up these channels and decreases tidal flows (and mixing) in other Delta channels.
Higher Spring tides, occurring when the sun and moon are more aligned, add volume to the Delta and by themselves can produce brief net negative flows on Old and Middle Rivers.
The second part of the animation varies Delta inflows to demonstrate how inflows and tidal forces interact, again without major Delta diversions. We look at inflows lower than those previously shown, representing late summer, and two higher inflow levels. Finally, we show effects of a flood pulse moving through the Yolo Bypass. The main lessons are:
Lower inflows increase tidally driven negative flows through Old and Middle Rivers.
As inflows increase, tidal influence diminishes from the upstream direction and net negative flows from the tides cease in Old and Middle Rivers.
Flood flows through the Yolo Bypass greatly reduce tidal influences.
Modeling produces a better understanding of natural and anthropogenic influences on Delta flows, which can help improve planning and policy-making for the Delta.
Coming next in Episode 3 is an examination of flow and salinity effects of major water diversions from the Delta.
William Fleenor is a senior researcher who specializes in hydrodynamics and hydraulic modeling at the UC Davis Center for Watershed Sciences. Amber Manfree is a postdoctoral researcher with the UC Davis Center for Watershed Sciences. Megan Nguyen is a GIS researcher at the Center for Watershed Sciences.
Happy New Water Year! October 1, 2021 is the beginning of the 2022 water year in California, the traditional beginning of California’s “wet season”, such as it will be.
Although there are many fine and interesting stories from California’s current drought, so far, a few stories seem more important and worth summarizing (even though many have been widely covered).
This is a major drought. The 2020 water year was the 9-th driest year of record and this last year has been the 3rd driest, in terms of precipitation. Warmer temperatures in recent years have further reduced streamflow as more precipitation has evaporated back to the atmosphere before it could flow to streams or groundwater and further stressed ecosystems. Although this is a major drought, in most regards it is not the worst drought California has ever seen, or will see.
Most people and economic activity in California have been well-insulated from the drought. Urban users have conserved little because they have not been convinced by their local utilities and governments that it is needed, and substantial conservation remains baked in from previous droughts, though much more is possible. Indeed, from a short-term perspective, few urban areas have needed to conserve more. Urban water management, responsible for about 20% of all human water use in California, has done quite well overall, so far. There are, and will be, sizable economic damages from this drought, particularly in some local areas, but statewide, relative to California’s $2+ trillion/year economy, the drought is not a major economic event. Overall, California can afford to focus on addressing particular drought weaknesses.
Ecosystems are being hammered, especially salmon and forests. This year’s winter-run salmon, already an endangered species, is essentially lost due to too-warm releases and low water levels in Shasta reservoir. Other salmon runs are also suffering from low flows and warm temperatures. Low reservoir levels will make it more difficult to avoid repeating these problems from reservoir operation next year. Forest ecosystems are very dry, with longer and more severe fire seasons and likely many deaths of young and mature trees. Many of these effects will be greatest after the drought in precipitation “ends.” (Moyle and Rypel)
Agriculture is suffering, but mostly without catastrophe so far, because of increased groundwater pumping. Groundwater withdrawals are most of the statewide agricultural response to drought. Surface water storage has been helpful, but has far less storage capacity and is quite expensive to expand. California’s agricultural prosperity during drought relies primarily on sustainable groundwater storage. (Medellín-Azuara)
Rural drinking water wells are impacted by increased agricultural pumping. Agricultural pumping lowers water tables and often strands shallower domestic and community wells in rural areas, affecting hundreds to thousands of rural wells. Deeper agricultural pumping is also likely to accelerate the contamination of wells from nitrate in shallower groundwater. Many of those depending on shallow rural wells rely on agricultural jobs. Implementing the Sustainable Groundwater Management Act will help reduce rural drinking water well vulnerability to drought, but this hasn’t happened much yet. (Gailey)
Increased groundwater pumping increases challenges and urgency of implementing SGMA. Under the Sustainable Groundwater Management Act, all the additional groundwater pumped during this drought must be replenished from reduced pumping and additional recharge before 2040. Faced with droughts and climate change, groundwater plans will need to be made, implemented, and enforced with more spunk than most people have previously thought. This immense challenge will require major painful long-term reductions in irrigated acreage in parts of the San Joaquin Valley. (Escriva-Bou et al)
Higher temperatures are making seasonal runoff forecasts less reliable, with past forecast methods being too optimistic. Snowmelt in 2021 was about 800 taf less than predicted, based on past relationships between snowpack and runoff. This would be about a 10% over-prediction between runoff predicted and actual annual runoff – valuable water in a dry year. (Abatzoglou et al.)
An additional dry year could make this drought a whopper. Reservoir levels are everywhere nearing of exceeding new low levels, watersheds are parched, and groundwater tables are dropping. So fewer water reserves would be available for a third dry year, and much more precipitation than usual will be needed for next year to not be dry. One DWR official was recently reported as saying the coming year would have to be at 140% of average precipitation to achieve average annual runoff. Historically, 140% of average precipitation is exceeded in only 27% of years. Overall, we seem likely to see an additional dry year, in terms of runoff. (There is little year-to-year correlation of precipitation in California from year to year, and in northern California, essentially no correlation with El Nino.)
Many urban areas are preparing for an additional dry year by implementing new water rate structures which would encourage more drought and permanent water conservation while keeping urban water utilities financially solvent. This seems like a good time for water users of all sorts to prepare for an additional dry year and future droughts. Droughts are much less damaging with preparation.
Long-term preparation gaps. With the climate changing, and many areas having seen benefits from outstanding drought preparation, it is surprising that some areas still lack in preparing for droughts. Drought plans for ecosystems and Delta management seem particularly needed. These gaps reflect the greater difficulty and complexity of these problems and perhaps the lack of political will, evolved consensus, and effective organization to manage these problems. Another year of drought might be needed to spur greater preparation.
These are challenging times for water in California, again.
by Jeanette Howard, Kirk Klausmeyer, Laura Read, and Julie Zimmerman
Droughts are extreme, but not necessarily extreme events — at least not in the way we humans usually experience events as discrete, episodic occurrences. Droughts are continuous and exhausting; they can come out of nowhere and take us on a rollercoaster of waiting for precipitation to come, measuring when it does, and hoping it will be enough to keep our rivers flowing for human use and healthy ecosystems. Droughts may feel so extreme that they should be a rare occurrence, but they are a natural part of California climate. And they will become even more frequent – climate change predictions show that extreme events, such as droughts and floods, are becoming more common (Swain et al. 2018).
Droughts are also subjective: in a year like this one, there’s no question that all of California is experiencing a drought. However, many rivers and streams in California experience drought-like conditions almost every year because of human demands for water (Zimmerman et al. 2018) such as in the Sacramento-San Joaquin Delta where the estuary experiences drought-like conditions in most years (Reis et al. 2019). Yet in most rivers in the state, we don’t have enough historical data to know how much water should be available. For example, we often don’t know if a river is running dry because it is the river’s natural condition (a stream with naturally intermittent flow), or if it should always be flowing and is running dry because humans are using too much water at the wrong times.
To effectively and reliably manage water, we need to know (1) how much water needs to be in a river to protect species and ecosystems, (2) how much water is actually in the river, and (3) what is the gap between the two? There is currently a group of scientists from universities, agencies, and NGOs that developed a framework and set of tools to answer the first question for all rivers in California – known as the California Environmental Flows Framework (CEFF). But the second question – how much water is actually in the river – has been a tough nut to crack. Predictions of actual flows would greatly enhance the ability to apply the CEFF framework by enabling the assessment of flow alteration and provide quantitative targets for how much additional water is required instream.
Actual flow measurements are only available at a finite set of point locations across the state – stream gages that are installed and operated by USGS, DWR, or other entities. Work by The Nature Conservancy found that approximately 3,600 stream gages have been active on streams and rivers in California at some point, but only about half of those have been active recently largely due to a lack of funding (see https://gagegap.codefornature.org/). Even with this network of gages, 89% of streams are poorly gaged, which means that for 89% of streams in California we have no information on actual flows and no obvious way to estimate the gap between the river flow that is needed and the flow that is available.
Investments are needed to increase our network of gaged rivers and streams. But rather than measure flow at gages in every stream in the state, it would be more efficient, cost effective, and realistic to predict flows, using a robust and scalable approach. With these predictions, we can develop storylines that tell the tales of these rivers, tracing the hydrologic signatures of a river from its historically unimpaired flows, through transitions brought by alteration (e.g., diversions, dams, land use change), to its current state today and likely state in the future. To write these stories from end-to-end, The Nature Conservancy (TNC-CA) and Upstream Tech have partnered to develop a set of tools that can estimate river flow using dynamic satellite data and machine learning methods. We began by building a model to estimate actual river flow and compared those modeled predictions to stream gage data. Our work in 300 gaged basins across California indicates that the model we’ve developed performs well and can also estimate actual river flow in ungaged basins.
What could be the impact of this model for planning and management in dry years? Consider this example from the Yuba River near Marysville (drainage area = 1,339 mi2 [3,450 km2]):
Using our ‘unimpaired’ flows model, which predicts naturalized streamflow similar to a typical rainfall runoff model, the validation period shows a high bias in the model’s prediction during the spring snow-melt period. The observation record dates back to 1987, so we don’t know the flows here before the reservoirs were built upstream in the basin, but we do know that the signature is altered and that this model is not reflective of impaired flows today.
The challenge ahead of us is to capture this altered behavior such that we can make estimates given the current storyline of the river. The extra challenge: do it with public data sources that have information across many basins so that this approach is scalable and not dependent on difficult to obtain and maintain data (e.g. dam-specific operation plans). Using over 1,000 ‘enhanced basin characteristics’ that were collected from StreamCAT, USGS Gages II, and USGS channel alteration datasets, we enhanced our unimpaired flows model to create an actual flows model. Here’s the result at the same Yuba River site:
The model described the shift from a natural snow-melt signal to a longer and flattened spring peak, reflecting the altered current conditions in the watershed. The real kicker of this site and others like it in our study: this was one of our “test” sites, which in machine learning terminology means that it was hidden from the model during training and treated as ungaged. The model never saw any observations from this site, never saw this time period even at other sites, and stilllearned this behavior shift from the enhanced basin characteristic inputs that we gave it. The Nash-Sutcliffe Efficiency (NSE), a common goodness-of-fit metric in hydrology, improved from -2.7 in the unimpaired model (top plot) to 0.77 in the actual flows model (bottom plot). A perfect NSE is one.
In the next phase, TNC-CA and Upstream Tech are expanding this approach to predict historic daily flows in 350 basins from 2000-2020, further validating modeling of ungaged impaired flows. From there, we’ll work on expanding estimates to ungaged streams across the state.
In dry years better estimates of flow in ungaged streams can provide a lifeline of information for real and near-term operational decisions, curtailments in drought years, assessments of water rights applications, and many other decisions that require information about water availability. For example, this year the operational forecasts largely missed this drought’s severity. A model that can simulate historic daily flows in altered basins across California could be used in the future for forecasting daily and seasonal flows with confidence and be able to answer crucial questions for decision makers such as:
“Will we pass critical habitat thresholds next month?” (Environmental flows planning)
“What is the likelihood that flows will be between X and Y, yielding sufficient water for all users?” (Allocation decisions from daily to three-months out)
“What types of basins need more gages because the hydrology is difficult to model and the data can improve model predictions elsewhere?” (Gage gap analysis and gage prioritization)
As the climate changes, the data and models we use must keep pace. Let’s work together to discover the true stories of our rivers and how they can better shape our future relationship with water as a lifeline for humans and nature.
Jeanette Howard, Ph.D., is the Director of Science for the Water Program for The Nature Conservancy’s California Chapter. Kirk Klausmeyer is the Director of Data Science for The Nature Conservancy’s California Chapter.Laura Read, Ph.D., is a Product Manager of HydroForecast at Upstream Tech. She co-authored this blog, representing the technical work of Alden Keefe Sampson and Mostafa Elkurdy. Julie Zimmerman, Ph.D., is Lead Scientist for The Nature Conservancy’s California Water Program.
California Environmental Flows Working Group (CEFWG). 2020. California Environmental Flows Framework. California Water Quality Monitoring Council Technical Report 37 pp.
Grantham, T. E., J. K. H. Zimmerman, J. K. Carah, and J. K. Howard. 2019. Streamflow modeling tools inform environmental water policy in California. California Agriculture 73(1): 33-39.
Reis, G.J., J.K. Howard, and J.A. Rosenfield. 2019, Clarifying effects of environmental protections on freshwater flows to – and water exports from – the San Francisco Bay Estuary. San Francisco Estuary and Watershed Science 17(1): 1-22.
Swain, D. L., B. Langenbrunner, J. D. Neelin, and A. Hall. 2018. Increasing precipitation volatility in twenty-first-century California. Nature Climate Change 8: 427-433.
Yarnell, S. M., E. D. Stein, J. A. Webb, T, Grantham, R. A. Lusardi, J. Zimmerman, R. A. Peek, B. A. Lane, J. Howard, and S. Sandoval Solis. 2020. A functional flows approach to selecting ecologically relevant flow metrics for environmental flow applications. River Research and Applications 36: 318-324.
Zimmerman, J. K. H., D. M. Carlisle, J. T. May, K. R. Klausmeyer, T. E. Grantham, L. R. Brown, and J. K. Howard. 2018. Patterns and magnitude of flow alteration in California, USA. Freshwater Biology 63: 859-873.
Risk Rating 2.0 has been called the Federal Emergency Management Agency’s (FEMA)’s most significant reform in 50 years. Roughly 77% of customers of the National Flood Insurance Program (NFIP) nationwide will see increases in their premiums, while the other ~23% will see reductions or no change. FEMA will formally introduce Risk Rating 2.0 on October 1, 2021, and most premium increases will kick in on April 1, 2022.
In brief, Risk Rating 2.0 moves the NFIP away from its heavy reliance on in-or-out flood zones, in particular in-or-out of the so-called “100-year floodplain,” and towards an individual assessment of risk for each property (as promoted in this Blog [6/16/2019]). FEMA’s 100-year flood area will not go away – in particular, this will still be the basis for whether a property owner with a federal mortgage must buy flood insurance – but the premiums for each property will be determined based on individual factors that include flood risk from an ensemble of three privately developed flood models.
Recently, FEMA published summaries of NFIP premium changes by state, with details down to individual zip codes. This first glimpse of Risk Rating 2.0 is a limited one; for example it shows only first-year changes (increases are capped at 18%/year) and lumps the most extreme increases or decreases into bins of “greater than $100” per month. Nonetheless, our group took the zip code-level data and “reverse engineered” that information to provide a first look at what policyholders and others interested in flood-risk management can expect from Risk Rating 2.0.
The focus of this review is California. Over the history of the NFIP, California has been a donor state, contributing hundreds of $millions more in flood insurance premiums than it has received in claims (California Water Blog 12/14/2016). Under Risk Rating 2.0, 73.2% of California NFIP policyholders will see premiums increase, and 26.8% will see decreases.
We encourage readers to explore Risk Rating 2.0 premium changes across California using our interactive map of average premium changes by zip code (Link to Interactive Map).
Premium Changes and Patterns across California
Statewide, the majority of Californians with NFIP policies can expect to see premium increases of less than $10 per month (Figure 1; Table 1). That being said, the total amount of premium dollars paid by California policyholders as a whole is actually set to decrease. The overall distribution of premium changes across California is bimodal – a large majority of policyholders will receive small rate increases, but some policyholders will receive larger discounts. Of the >20,000 policies receiving discounts of ≥$20 per month, nearly half are >$70/month. We cannot precisely calculate the total net impact of Risk Rating 2.0 on California because FEMA’s data masks the exact dollar amount of changes at the extreme tails (8 policies with increases >$100 per month and 7421 properties with decreases >$100 per month). For the purposes of this analysis, we conservatively assumed a $100 change for the extreme tails (+/- >$100/month). Using this method, the total change in premiums in the first year of Risk Rating 2.0 is an aggregate decrease of at least $1.4 million per month (= at least $16.76 million per year statewide), or ≥9.9% of total California NFIP premiums (FEMA, 2021b). About half of this estimated total discount discount will go to single-family homes (~165,000 policies), and the other half going to the remaining non-single-family and non-residential NFIP properties (~49,000) in California.
The overall downward shift in premiums is consistent with our earlier findings that NFIP seemed to be overestimating flood risk in California. The state has been hit by more than its share of disasters, but several decades of flood data were not adding up to the flood hazard suggested by NFIP premiums until now. In shifting to a more physical, individualized formula, Risk Rating 2.0 seems to be recognizing this earlier overestimate, although not correcting the formula as much as may be warranted.
This bimodal distribution of premium changes is also interesting when mapped across California (Figure 2). Increases and decreases are scattered across the statewide zip codes, but a few regional patterns emerge. First, the California Central Valley – including the Sacramento Valley north of Sacramento and the San Joaquin Valley to the south – is characterized by average premium decreases. under Risk Rating 2.0 (greens in Fig. 2).
Stakeholders in the Central Valley have long complained that NFIP was overcharging them; for example, pressing the Government Accountability Office in 2014 to study perceived biases against agriculture baked into the NFIP (https://www.gao.gov/products/gao-14-583). In addition, the California Central Valley has broad areas protected by levees, some of which meet the 100-year protection standard, some not.
Figure 3 maps out premium changes in the Sacramento area. Four of California’s top five zip codes with the most NFIP policies are located around Sacramento. Under Risk Rating 2.0, three of those (95833, 95834, and 95835 [Natomas]), will see modest declines in premiums. Conversely, 95831 (the Pocket area) will see premium increases. All four of these are levee-protected areas along the Sacramento River. The US Army Corps of Engineers recently completed significant levee improvements around Natomas, and is commencing improvements to the Pocket area. Until now the NFIP handled levees as all-in or all-out, a practice widely criticized from all sides. Under Risk Rating 2.0, the Corps has supplied FEMA with levee data, but estimates of levee reliability is notoriously difficult to quantify, and the new algorithm for levee protection is currently a black box that needs scrutiny.
Our own zip codes here in Davis illustrate some of the odd shifts under Risk Rating 2.0. The 95616 zip code, including western Davis and the university, will see average decreases of almost $4.00 per month, while 95618 to the east will see increases >$4.00. Both areas lie at similar elevations and are largely outside of FEMA’s mapped 100-year floodplain. The whole area is protected from flooding of the Sacramento River and other tributaries by levees and bypasses. We initially suspected that the private-sector flood models embedded in Risk Rating 2.0 are favoring levee-protected areas, making this change in Davis puzzling, but a lack of transparency in underlying data obscures the mechanisms driving such changes.
Figure 4 shows Risk Rating 2.0 premium changes in the Los Angeles area. Within this region, changes are most pronounced in the foothills and coastal areas in Malibu, the Santa Monica foothills, and the Hollywood Hills, with policyholders in zip code 90265 (Malibu) set for an average discount of >$40/month. This represents the steepest discount for any zip code in California with >1,000 current policies. Elsewhere in L.A., the densely populated San Fernando Valley and main L.A. Basin area, on average, will see modest increases in monthly premiums.
The large premium decreases in Malibu, the Santa Monica foothills, and the Hollywood Hills are surprising. FEMA is heavily marketing Risk Rating 2.0 as “Equity in Action.” Malibu’s median household income is >$150,000 per year (2019), 2.5 to 3 times higher than the $50,000-$60,000 in most San Fernando Valley zip codes.
Risk Rating 2.0 does include one important fix that promotes economic fairness. Under the current NFIP pricing system, premiums are based on the insured value of a structure and not the actual value of that building. And currently, coverage up to $60,000 is charged at a higher rate than coverage above that threshold. FEMA originally did this to encourage policyholders to insure the full value of their structure and contents (up to allowable caps). But the policy is regressive as well as counterintuitive, as high-value structures are also more likely to incur expensive damages. Under Risk Rating 2.0, premiums will be priced based on a structure’s replacement cost.
Beyond the clear fix in premium pricing above, it is unclear how much Risk Rating 2.0 lives up to its “Equity” label, either in intent or in its impact. By all accounts, Risk Rating 2.0 was designed primarily and from the start as a new pricing structure to fix NFIP’s perennial funding shortfall. As the Congressional Research Service put it, “Risk Rating 2.0 will continue the overall policy of phasing out NFIP subsidies.” Fixing the perennial hemorrhaging of NFIP may be a worthy goal, as is making insurance rates that better reflect risk, but rolling out these changes under the banner of “Equity” is disingenuous.
To preliminarily assess the economic equity of Risk Rating 2.0, we compared premium changes across California to median household incomes in the same zip codes (Table 2). There is no clear correlation between neighborhood income level and average premium change. Premium decreases were largest in the lowest-income category (averaging -$9.25/month for neighborhoods with incomes <$50,000). Premium decreases were smallest for middle incomes (averaging -$3.43/month for neighborhoods with incomes $70,000-$80,000). Premium changes in all other income categories, including areas with mean incomes >$100,000, were intermediate, averaging -$6.50/month.
Other questions about Risk Rating 2.0 focus on the modeling and formulas used to calculate risk and premiums. Some details have been provided (e.g., the “Milliman Report,” April 2021), but a lot of Risk Rating 2.0 is a black box. Our research group is trying to obtain better, clearer data to assess questions like how coastal flooding and future climate change are reflected in the new RR2.0 premiums. In the meanwhile, Figure 5 shows zip code-level premium changes for the San Francisco Bay Area. Here, it appears that many low-lying costal areas are set to experience premium increases, while foothill areas are set for significant discounts. Coastal zip codes like 94080 (South San Francisco), 94044 (Pacifica), and 94030 (Millbrae) are will see premium increases in the $5-%7 range, while mountainous, suburban areas like 94605 (Oakland Hills) and 94583 (San Ramon) are set for premium decreases >$20 per month. However patterns in the San Francisco Bay Area appear to run counter to the Los Angeles area: average premiums in low-lying coastal areas of San Francisco going down, versus scattered decreases in Los Angeles. Deconvolving the overlapping hydraulic, climatic, engineering, and actuarial changes embedded in Risk Rating 2.0 will require much more openness and data sharing on the part of FEMA and its partner modeling contractors.
Risk Rating 2.0 is FEMA’s effort to bring about significant reform to the NFIP, with an eye toward incorporating more accurate flood risk information and, purportedly, more equitable premiums proportionate with that risk. Limited pricing data released by FEMA suggest that most California policyholder will see modest increases, whereas a smaller number of policyholders will see larger discounts which bring down the total NFIP bill to California by at least 10%. Mapping these data highlights how these increases and decreases vary widely across the state, and FEMA continues to mask the “extreme tails” of the distribution (changes >$100/month, i.e., >$1200 per year) as well as changes beyond the first year of Risk Rating 2.0. Also importantly, the premium decreases across California are smaller than the documented imbalance between what the state has paid into the NFIP as premiums and what its policyholders have received as payouts over the history of the program (California Water Blog, 12/14/2016).
Answering questions about Risk Rating 2.0, like the one above, requires independent scrutiny of the modeling and assessing assumptions on which the new insurance premiums are based. High on that list of important questions is how data provided to FEMA by the Army Corps of Engineers characterize flood risk behind different levees. “Levee fragility” and “residual risk” behind levees are notoriously difficult to assess and quantify, and slightly different assumptions can mean huge differences in the insurance bills that policyholders are soon to receive.
Starting on October 1 of this year, flood insurance customers eligible for renewal can lock in the new premiums under Risk Rating 2.0. Policyholders should check with their insurance agent whether their bills are slated to go up or down, and if down, by all means they should reset as soon as possible. On April 1, 2022, the new changes will apply to all new and renewing policies.
While the apparent net decrease in California’s flood-insurance premiums is a welcome change, important questions remain about how private-sector flood models and assumptions about local risk (e.g., levee protection) are weighed in Risk Rating 2.0. We call for more transparency and dialog with FEMA, including the sharing of additional information and data at a fine-grained spatial resolution.
Ryan Miller is a Ph.D. student in the Geography Graduate Group at UC Davis, researching flood and fire risks, climate change, and urban planning. Peter Hansen, MA is a geospatial specialist and IT consultant in the College of Behavioral and Social Sciences at CSU, Chico. Nicholas Pinter is the Shlemon Chair in Applied Geosciences in the Department of Earth and Planetary Sciences at UC Davis and is Associate Director, Center for Watershed Sciences.
U.S. Government Accountability Office (GAO), 2014. National Flood Insurance Program: Additional Guidance on Building Requirements to Mitigate Agricultural Structures’ Damage in High-Risk Areas Is Needed. https://www.gao.gov/products/gao-14-583
“Mega-drought” has become a frightful “thing” in public and media discussions. In the past 1,200 years, California had two droughts lasting 120-200 years, “megadroughts” by any standard. Could the state’s water resources continue to supply enough water to drink, grow crops and provide habitat for fish with such an extreme, prolonged drought today?
Clearly, some ecosystems and rural communities would be devastated by such a drought, and it would certainly affect all California residents. But with careful management, California’s economy in many ways could substantially withstand such a severe drought.
The UC Davis Center for Watershed Sciences explored this question a few years ago using computer models. We constructed a drought similar in scale to the two extreme ones found in California’s geological and biological records of the past 1,200 years (Harou, et al. 2010). We created a virtual 72-year-long drought with streamflow at 50 percent of current average rates, with all years being dry, as seen in the paleo-drought record.
We then explored the simulated drought using a computer model of California water management that suggests ways to minimize the economic costs of water scarcity for populations and land use in the year 2020.
Not surprisingly, the model results showed that such an extreme drought would severely burden the agriculture industry and fish and wildlife, and be catastrophic to some ecosystems and rural towns. The greatest impacts would be felt in the Central Valley.
However, if well managed, such a mega-drought would cause surprisingly little damage to California’s economy overall, with a statewide cost of only a few billion dollars a year out of a $2+ trillion-a-year economy.
The key to surviving such a drought lies in adaptive strategies such as water trading and other forms of water reallocation. These strategies would be essential to improving the flexibility of California’s water supply and demand system during such a prolonged drought.
Interestingly, most reservoirs we have today would never (yes, NEVER) fill during a decades-long drought. So expanding surface storage capacity for managing megadroughts would be futile.
California has a very flexible water supply system that can support a large population and economy under extreme adverse circumstances — provided it is well managed.
In adapting to the climate warming and changes that are upon us, the most important thing for California is to be well-organized and led for effective water management. Panic or complacency generally lead to poor decision. Good management of such a complex system will require serious and reasoned analysis and discussions, plus a political will to make reasoned decisions, even when ideal solutions do not exist.
Jay Lund is a professor of civil and environmental engineering and co-director of the Center for Watershed Sciences at UC Davis.
This article originally ran April 12, 2011. Some text has been updated,
by José M. Rodríguez-Flores, Spencer A. Cole, Alexander Guzman, Josué Medellín-Azuara, Jay R. Lund, Daniel A. Sumner
California’s Central Valley is the source of more than $30 billion of farm value. It produces more milk than any state outside California, and dominates national production of dozens of fruits, vegetables, tree nuts and rice. The valley has two main parts: the Sacramento Valley (north) and the San Joaquin Valley (south); each has particular distinguishing agricultural features (such as soil, hydrology, climate, and economy) that have driven how agriculture and water infrastructure have developed. This post reviews the evolution of the major crops and crop categories produced in the Central Valley of California from 1990 to 2019.
Figure 1 shows cropland use in the Sacramento Valley across three decades. Rice acreage has covered about half of the land used for crops in the valley for many decades. The price and yield of rice have been relatively stable in this period, and acreage has temporarily declined mainly during severe drought periods. Figure 1 shows sharp drought declines in rice harvested area, such as in the early 1990s and the 2013-2015 period, which recovers with water availability in wetter years. Three decades ago, other grains were second to rice in land use, but now nut crops mainly walnuts, have more acreage than the grain crops. There has been an upward trend in more profitable tree nut crops such as almonds, pistachios and walnuts since the early 2010s, even during the 2012-2016 drought. These perennial crops have shown technology-driven increases in yields and higher prices in the last ten years, but are somewhat more water intensive (requiring 3 to 4 acre-feet per acre) and allow much less flexibility in water use from year to year.
In the San Joaquin Valley (SJV) almonds, pistachios, and walnuts are currently among the dominant commodities by acreage (Figure 2) and production value. These crops now cover over 50% of total irrigated area in the SJV, where Fresno and Kern counties are the main almond producers. Cotton was the most planted single commodity for during the middle of the 20th century in the southern SJV until its production began a sharp decline in the 1990’s as subsidies were reduced and nut acreage began its rapid expansion. Miscellaneous vegetables, melons, tomatoes, fruit and hay and other field crops make up most remaining crops, with their acreages also declining in the last decade.
The crop mix in the SJV has changed with expected future crop demands, relative prices, production costs, and water conditions. For example, alfalfa acreage declined steadily since 2009 because of lack of growth in the California dairy industry, and low returns relative to tree nuts and some annual crops such as tomatoes. The San Joaquin Valley is now dominated by tree nut crops, that climate-limited ranges which align with California’s Central Valley climate.
Central Valley agriculture is supported by California’s array of intertied water supply infrastructure, including surface and groundwater storage, and conveyance, which provides a delivery system for perennial crops with inflexible water demands over the growing season and from year to year. These factors, along with significant long-term improvements in crop yields for several crops and higher expected prices, have encouraged expansive growth in almonds, pistachios, and walnuts.
In dry periods, cropping decisions are limited by water availability and sometimes increased water costs from transfers or groundwater pumping. Apart from old tree removals, acreages of perennial crops (tree nuts, grapes, and citrus trees) remain roughly constant during droughts due to high upfront costs involved in cultivation and higher revenue per harvested acre or acre-foot of water. Most land use reductions occur in crops with more flexibility and for which net return per unit of water is relatively low such as grain, hay and other field crops.
Almonds, pistachios and walnuts grew substantially even in the 2012-2016 drought due in part to high prices and continued expectations of high future prices which outweighed costs of water limitations and concerns about future water access. With the Groundwater Sustainability Plans (GSPs) required by the 2014 Sustainable Groundwater Management Act, some orchard retirement to cope with water scarcity may become a more frequent drought adaptation tool as GSP mandated cutbacks represent a longterm reality in many sub-regions.. For example, corn grown for silage might be expected fall severely in dry periods, but actually maintained substantial acreage in recent droughts because of its key role in local dairy rations and because it is too expensive per unit of value of haul more than 50 miles or so. Corn acreage provides a useful area to spread cow manure, which is unsuitable to distribute through drip fertigation systems. In contrast, alfalfa, which is also water intensive and typically used as a dry roughage feed crop, saw a downward trend in acreage during droughts (Figure 2) as has been regularly shipped into the San Joaquin Valley from Northern California and other states. Alfalfa hay can also use reduced water in drought years at the expense of fewer cuttings and therefore lower yields per acre.
Historically, cropping decisions differ between the Sacramento Valley, where rice production in the north declines somewhat and in the San Joaquin Calley, where hay, corn silage, grain and cotton decline when water is scarce. While many Groundwater Sustainability Agencies have not yet fully implemented groundwater use limitations, such reductions will be a major part of a portfolio of water management actions to achieve local and regional balances in abstraction and recharge by 2040.
Readers interested in visualizing and downloading DWR data on historical water and cropland use and County Agricultural Commissioners’ Report data on crop prices, land use, crop yield and production value, visit the UC Merced – Water Systems Management Lab website in the agricultural data section: https://wsm.ucmerced.edu/agricultural-data/.
José M. Rodríguez-Flores and Spencer A. Cole are respectively Ph.D. candidate and M.S. student at the Environmental Systems graduate program at UC Merced, Alexander Guzman is a former Junior Research Specialist and Lab Manager of the Water Systems Management Lab at UC Merced, Josué Medellín-Azuara is an associate professor at the Department of Civil and Environmental Engineering at UC Merced, and an associate director at the UC Davis Center for Watershed Sciences, Jay R. Lund is a Professor of Civil and Environmental Engineering at UC Davis, where he is also Co-Director for UC Davis Center for Watershed Sciences, Daniel A. Sumner is the Frank H. Buck Jr. Distinguished Professor in the Department of Agricultural and Resource Economics at UC Davis.
Given the current drought, it’s no surprise that California’s dams are struggling to provide cool water habitats to support native freshwater ecosystems. But what if they were never able to support them under any conditions?
New research shows how current stream management fails to provide the patterns of cool water that California’s native ecosystems need. The challenges stem from two issues: an oversimplification of stream temperature targets and the assumption that dam regulation can replicate desirable cold water patterns.
We analyzed available long-term (> 8 years) daily stream temperature data records for 77 sites throughout California. We then used an algorithm to see whether the sites could be sorted into groups with similar thermal regimes. The sites were sorted based on annual average temperature, annual maximum temperature, and the day when the annual maximum occurred. Aside from these three temperature metrics, no additional information was used to influence how the algorithm grouped the sites.
Results revealed that California’s streams naturally form five distinct classes (Figure 1). Two of the five classes were unique to groundwater springs, whose temperatures are notably constant throughout the year (stable warm and cold). Of the remaining classes, one included only sites not influenced by dam regulation (variable cool), one included sites heavily influenced by dam regulation (stable cool), and the last showed sites whose temperatures were mostly affected by weather (variable warm).
In ecological terms, “cool” and cold” are typically used to describe species that rely on relatively lower temperatures to support optimal growth and survival. These terms are often simplified to mean a specific threshold temperature associated with a species. In the Sacramento River, 56°F is a common target threshold used to sustain salmon. However, our research clearly shows how single temperature metrics like this do not capture the full thermal dynamics of California’s cold-water ecosystems. We must learn to manage towards multiple natural thermal regime endpoints; parallel approaches have greatly improved stream flow management. For example, flow management has transitioned away from single, minimum flow targets to environment flow management that recognizes the importance of diversity in magnitude, frequency, timing, rate of change, and duration of flows. Stream temperature management must make the same change.
When mapped throughout California’s hydrologic regions, the futility of sustaining cold-water ecosystems through regulations is starker (Figure 2). Results show that even when we can heavily manipulate flows or water temperature released from dams, we rarely approach the complexity endemic to natural thermal regimes. Rather than resetting temperature patterns by releasing cooler water than would naturally occur (or warmer, during the winter), dams create an artificial thermal regime that disrupt natural seasonal patterns and create novel thermal habitats – sometimes for tens of miles.
Except for Shasta Dam, no other regulated river showed the kinds of natural temperature patterns that cool- and cold-water ecosystems need. It’s the exception that proves the rule of how poorly dams perform when operated for environmental temperatures. While a few systems may provide opportunities for management of new or novel thermal regimes (which may provide some potential for thermal climate refugia or resilience) these sites are few and far between.
Conservation planning for cold-water species is a risky investment in California. Located at the southern edge of the geographic range of cold-water and anadromous species, California’s freshwater fauna is extraordinarily vulnerable to human-dominated ecosystems. Extinction is likely for most (74%) of California’s native salmonids; though altered or degraded thermal regimes are a major stressor, they are not the only limitations. Bold conservation actions are required to reverse the trend towards extinction.
Ann Willis is a civil engineer and senior researcher at the UC Davis Center for Watershed Science. This research was part of her dissertation on water temperature management and stream conservation. Ryan Peek is an ecologist and senior researcher at the UC Davis Center for Watershed Science. Andrew Rypel is Co-Director of the UC Davis Center for Watershed Sciences and Peter B. Moyle and California Trout Chair in Coldwater Fish Ecology in the Department of Wildlife, Fish & Conservation Biology.
California has more hydrologic variability than any state in the US, meaning that we have more drought and flood years per average year than any other state. This is a problem, but has also meant that we have designed for droughts, which are always testing us.
2021 is the 3rd driest year in more than 100 years of precipitation record. 2020 was the 9th driest year in the precipitation record.
Much warmer temperatures are further reducing streamflows and aquifer recharge, and has lengthened and deepened the wildfire season.
Large reductions are occurring in surface water available for agriculture, especially in the San Joaquin Valley, but also in the Sacramento Valley and smaller river valleys statewide.
Much increased groundwater pumping greatly reduces agricultural impacts, but affects rural wells.
Major forest and aquatic ecosystem impacts are occurring, especially for wildfires and salmon runs, particularly for winter-run salmon downstream of Shasta Dam.
A growing number of small communities and towns are being affected, in addition to more common problems for rural household and community wells. Santa Clara Valley (San Jose area) is the most-affected major urban area, seeking 30% water use reductions.
If next year is also dry, agricultural and environmental impacts will increase and urban impacts will expand.
Warmer temperatures from climate change are worsening droughts, reducing the amount of precipitation that arrives at reservoirs and aquifers, lengthening wildfire seasons, and worsening conditions for cold-water fish species, such as salmon. We need to further adapt water, land, and environmental management for these changes.
Another dry year is likely. Very dry watersheds, very low reservoir levels, falling aquifers, and higher temperatures mean more precipitation is needed to make next year not dry.
Under SGMA, farmers will need to repay additional groundwater pumped during the drought, meaning some reductions in lower-valued crops in wetter years so aquifers can recover to sustain permanent crops in future droughts. Few basins can sustain aquifers with managed aquifer recharge alone; many will need deep reductions in aquifer pumping in wetter years.
Sizable long-term reductions in irrigated area seem unavoidable in parts of the San Joaquin Valley. Urban water conservation statewide is helpful, and still more conservation will help a bit.
A more formal state water accounting system is needed to support tighter surface water right administration, SGMA planning and implementation, and environmental uses. Water right curtailments are likely to become routine in more basins.
Everywhere you go in California, people live in landscapes where non-native species are conspicuous: European grasses turning the hills golden, earthworms tilling our garden soil, exotic trees providing shade, bullfrogs jumping into backyard ponds, starlings making tight maneuvers overhead. In this blog, I want to describe the language of our relationships with non-natives and the nature of those relationships as biological phenomena, using fishes and other aquatic organisms as examples. Reconciling our relationships with non-native species requires a vocabulary that reflects our attitudes towards them and their management.
In a recent WaterBlog, Stompe et al. (https://californiawaterblog.com/2021/07/04/home-is-where-the-habitat-is/) argued that non-native fishes thrive in California because we have created habitats much like the ones to which they were native. These habitats, alas, are mostly quite different from the ones to which our native fishes are adapted. To some extent, native and non-native fishes can form coalitions (novel ecosystems) where the resources available are divided up among the species, much as it supposedly is in undisturbed habitats (e.g. Aguilar-Medrano et al. 2019). But, in general, non-native fishes are replacing natives as habitats change, mostly as we have changed them. How do we live with this change but still save native fishes? Let’s start with language.
I use non-native as the general, seemingly neutral, term for species from elsewhere that have extended their range into California, thanks to being brought here by people. Most are introduced species, another neutral term.
The word exotic is a somewhat positive term, bringing to mind exotic people and places, as well as nature specials on television. Today, it is most often applied to fish and plants in the aquarium trade.
Non-indigenous is the term often used by government agencies because it is neutral, hard to pronounce, and can be bureaucratically abbreviated to NID species.
Invasive is the term for non-native species that are harmful and/or spreading. Unfortunately, it is widely applied to all non-native species, even though many are not demonstrably harmful.
Naturalized can be used to describe non-native species that were introduced so long ago they have adapted to California’s distinctive environment and are integrated into the biotic communities. Fish examples include striped bass, American shad, and common carp.
Alien is a negative term for non-native species, enhanced by science fiction movies. The worst thing you can call a non-native species is alien invader. This term fits realistically the northern pike, highly predatory species, on which California was willing to spend millions of dollars to eradicate before it spread widely, devouring native fishes.
The diversity of words we use to describe non-native species reflects the ambiguity in our attitudes towards them. This partly reflects the diverse symbiotic relationships that we humans have with other species, especially non-native species. Symbiosis in its simplest sense means ‘living together’ and usually includes mutualism, commensalism, parasitism, competition, and predation.
The symbiotic relationship looked upon most favorably is mutualism, where both species benefit from a relationship. Most sport fishes brought into California by agencies could be considered as mutualists, when people benefit from the fishery and the fish benefit from having their range expanded, important in the game of long-term evolution and survival. Of course, as human attitudes change and protection of native species from non-native species becomes a priority, the relationship between humans and non-native fish becomes more complicated.
For some species, the relationship with people is commensalism, where one species benefits but the other species neither benefits nor is harmed. An example is the shimofuri goby, a small fish with a life cycle that permits it to be carried across oceans in the ballast water of ships. It became established in the Delta in the 1980s and is now a common species, enjoying life amongst the rip-rap and trash, feeding primarily on non-native invertebrates that are not eaten by other fishes. This benign relationship with people may change if it manages to invade (which it probably will) estuaries in southern California where it can compete with/prey on the endangered tidewater goby.
A poorly understood (for California fish) symbiotic relationship is parasitism, including disease, where the parasite benefits from the relationship but the host is harmed. For example, whirling disease, scourge of both hatchery and wild populations of rainbow trout, is native to Europe and was brought to North America in trout from Europe. It has forced some California trout hatcheries to shut down with considerable impact on recreational fisheries.
Competition and predation are often not listed as forms of symbiosis but they are interspecies interactions of great consequence. Humans, for example, compete with freshwater fish for water (a resource in short supply), with the fish usually losing, regardless of native vs non-native status, unless people choose to back away from the relationship. Likewise, people are the biggest predators on fishes, via fisheries, management of which can favor non-native species (e.g. largemouth bass) over native fishes (e.g. Sacramento pikeminnow).
Regardless of the initial reason people and non-native species wind up living together, the relationship often becomes complicated. The Mississippi silverside was introduced into Clear Lake for an assumed mutualistic relationship, to control pestiferous gnat populations, which it did. It also became abundant in the process, an expected result of the relationship. But what was not expected was that silversides were carried from the lake, down Cache Creek and into the Delta, where they likely prey on the eggs and larvae of native fishes, such as delta smelt. They also serve as prey themselves for native birds like herons and egrets. They are now abundant in reservoirs in southern California, with unknown effects.
All these types of interactions between people (a non-native species) and fish show that understanding the biology of each species and our relationships with them is important. Like it or not, we humans need to have this understanding for living symbiotically with non-native species so we don’t have to consider ourselves at war with them.
Living with non-native species.
The widespread colonization of highly altered freshwater environments by non-native species is resulting in increased biotic homogenization. This is especially true in California and the American west because of intense development of water for people has resulted in massive changes to our waterways. A few natives can survive in new habitats such as reservoirs, but most cannot. Our inability to stop the juggernaut of habitat change and non-native species demonstrates “…we are losing the battle against extinction…and against the seizure of aquatic ecosystems by alien invaders (Moyle 2021, p 70)”. To take this militaristic analogy further, one of the best ways to save native fishes seems to be through creation of a system of fortresses, aquatic preserves that are bulwarks against species invasions. For non-native fishes, a triage system for management can be recognized: eradication, control, acceptance.
Eradication should be the main option for new arrivals that have a limited enough distribution that eradication is possible (e.g., Northern pike in Lake Davis). It is also a good option for populations of non-natives confined to treatable areas, such as brook trout in Sierra Nevada lakes where eradication via gill nets is possible, one lake at a time. This strategy is important to restore native amphibians and invertebrates to the lakes.
Control can be an alternative where complete eradication is not possible. This approach has been used to create stream refuges for golden trout in California: a barrier is first built and then non-native trout eliminated above the barrier using a degradable fish poison. Golden trout are then re-introduced. Such control of non-natives is rarely permanent, however. In regulated streams, some control over non-native species can result from a tightly managed flow regime that favors native fishes.
Acceptance of non-native fishes is hard for those of us engaged in native fish conservation, but reality dictates that there is often little choice. This does not mean they should not be managed at all, but instead managed in ways that minimize negative impacts on native species. It is not worth spending time and energy on ‘saving’ native fishes where environments are so severely altered that native species will not persist whether or not non-native species are present (e.g. most reservoirs). On the other hand, where major positive environmental change is likely, as through dam removal, its effects on both native and non-native fishes will need to be considered. Sometimes environmental restoration to favor native species will instead favor non-natives (e.g., Williamshen et al. 2021).
An approach that I think is helpful in resolving the native vs non-native fish dilemma is reconciliation ecology. Reconciliation ecology is defined as “the science of inventing, establishing, and maintaining new habitats to conserve species diversity in places where people live work and play” (Rosenzweig 2003, p 7). This concept acknowledges that people dominate most ecosystems today, which means we determine what species they will contain as time goes on. Many, if not most, ecosystems can support both native and non-native species. If we understand the role of non-native species, we are more likely to also keep native species as significant parts of California’s unique ecosystems.
This blog is based, in part, on Moyle (2020).
Aguilar-Medrano, R., J. R. Durand, V.H. Cruz-Escalona and P.B. Moyle. 2019. Fish functional groups in the San Francisco Estuary: understanding new fish assemblages in a highly altered estuarine ecosystem. Estuarine, Coastal and Shelf Science 227106331 https://doi.org/10.1016/j.ecss.2019.106331
Moyle, P.B., 2020. Living with aliens: nonnative fishes in the American Southwest. Pages 69-78 In D.L. Propst, J.E. Williams, K.R. Bestgen, and C.W. Hoagstrom, eds., Standing Between Life and Extinction: Ethics and Ecology of Conserving Aquatic Species in North American Deserts. Chicago: University of Chicago Press.
Moyle, P. B., P. K. Crain, K. Whitener, and J. F. Mount. 2003. Alien fishes in natural streams: fish distribution, assemblage structure, and conservation in the Cosumnes River, California, USA. Environmental Biology of Fishes 68: 143-162.
Rosenzweig, M.L., 2003. Win-win Ecology: How the Earth’s Species Can Survive in the Midst of Human Enterprise. Oxford University Press on Demand.
Williamshen, B.O., T.A. O’Rear, M. K. Riley, P.B. Moyle, J. R. Durand. 2021. Tidal restoration of a managed wetland in California favors non-native fishes. Restoration
Ecology. Society for Ecological Restoration. doi: 10.1111/rec.13392 12 pages
Peter Moyle is Distinguished Professor Emeritus at the Center for Watershed Sciences, UC Davis.
This is a slightly-edited re-posting from May 5, 2019.
Figure 1. 1861-62 flood in Sacramento.
A review of 170 years of water-related successes in California suggests that most successes can be traced directly to past mistakes. California’s highly variable climate has made it a crucible for innovations in water technology and policy. Similar water imperatives have led to advances in water management in other parts of the world. A close look at California’s water model suggests that “far-sighted incrementalism” is a path to progress. Given the complexity of water management systems, better scientific information and new policy tools must be developed coherently and collaboratively over time. A history of learning from previous failures can guide progress towards stable, secure, and resilient water systems worldwide. This includes learning from other regions and other “water models” – the one option clearly superior to innovating in response to your own mistakes is learning from the errors of others.
Average runoff in California is about 100 km3/yr, but our ecosystems and parts of our economy have been water-limited for decades. Part of the state’s challenge comes from the variability of its climate. Average years are unusual, and instead long droughts are punctuated by years of heavy rain or snowmelt and flooding. Nonetheless, the state has managed to thrive, with 40 million people, agricultural production exceeding $45 billion/year, and the world’s sixth largest economy. California’s droughts and floods and tension between economic growth and environmental protection have pushed it to develop a diverse toolkit for managing water.
The toolkit consists of an integrated system of infrastructure, laws, institutions, and economic tools. This system, the ”California water model,” has evolved from the first Spanish settlement, through the gold mining era, the ascendancy of agriculture and major cities, to the recent broad mix of objectives that includes strong environmental protection. California has steadily adapted its water management by making mistakes and then learning from those mistakes. In 2017, for example, California avoided major flooding despite the winter being one of the wettest on record and major spillway failures. This was partly due to luck. Reservoirs began low from a drought and winter storms were widely spaced. And most flood infrastructure, particularly the flood bypasses, functioned well. California’s water model offers broad lessons for water managers, particularly in arid regions.
Water in California is framed by the state’s Mediterranean climate. Summers are long and dry and most precipitation comes during the winter. Historically, much of the water supply comes from mountain snowmelt (the state’s largest surface reservoir), reservoirs, and groundwater. In addition to this seasonality, wet years often follow droughts, and vice versa, high variability accentuated by climate change. This near-perpetual alternating water crisis forces Californians to find innovative solutions. Whereas other US states and other countries may have decades to settle into a false sense of security, California’s hydrologic extremes accelerate innovation.
In 2017, California emerged from a severe five-year drought. The drought’s effects on agriculture were limited because past droughts had led to more flexible water markets, and farmers greatly expanding groundwater pumping. Although the state lost about a third of its water supply, agricultural revenue losses were only 3%, and only about 6% of the land was fallowed. This was in part because producers of lower-value crops sold or transferred their water to producers of higher value crops such as fruit, nuts, and vegetables and to urban water users. The expanded groundwater pumping raised the visibility and impacts of long-term groundwater problems, which in turn led to passage of California’s Sustainable Groundwater Management Act, which will regulate groundwater in the future.
At the other extreme, California also has long history of damaging floods, and flood risk remains widespread today. Winter storms of 1861-62, turned much of the Central Valley into an inland sea, and frequent levee breaches through the 19th and 20th centuries resulted in high costs to landowners and to the state. In less variable regions, the decades between major floods lead to a “hydro-illogical cycle” in meaningful steps avoid flood damage are forgotten in intervals between disasters. Early on in California, repeated flooding led to construction of Yolo and Sutter Bypasses, which remain a world model for basin-scale flood management. A costly 1986 levee failure (and national headlines from New Orleans in 2005) sparked new legislation and investment that has upgraded many California levees from some of the worst in the nation to some of the best. Repeated flood disasters have kicked the state in the right direction, although much work always remains. The near-disaster at Oroville Dam in February of 2017, where two spillway failures led to major evacuations, sparked scrutiny and investment at Oroville Dam and for aging water infrastructure across California. Other regions with large dams, or contemplating new dams, should include Oroville’s lessons in their textbook.
Figure 2. Unchecked groundwater overdraft has brought ground-surface subsidence. California’s San Joaquin Valley’s severe subsidence over the past century, continues locally today. Photo courtesy of Michelle Sneed, US Geological Survey.
Despite successes, California’s water management faces continued challenges. High on this list, protecting endemic aquatic species remains a vexing challenge. Despite legal protections under federal and state regulations, California’s native fishes are in rapid decline, with 80% of species on paths towards extinction. California will need to expand its toolkit – such as by accepting “reconciliation ecology” as a new model for maintaining natural diversity in the face of human pressures and a changing climate.
A prerequisite for providing and maintaining healthy aquatic ecosystems and adequate supplies of clean water is “far-sighted incrementalism” among water managers and political leaders. Incrementalism involves addressing seemingly intractable problems by small forward-looking steps. “Far-sighted,” at least in California, has involved forward-thinking planning among scientists, managers, and leaders during and after each water-related crisis. The common response after a damaging flood is reactive – repair the levee breach and rebuild floodplain neighborhoods. Far-sighted leaders see opportunities in such a crisis to move the system forward, usually incrementally, in a longer-term strategic direction (usually too controversial or difficult to achieve in one step). California must continue to support organized and independent learning from and adapting to disasters and extremes.
Lessons for managing water in a thirsty world
By 2050, an additional 2.3 billion people worldwide will face severe water stress, especially in Africa and southern and central Asia. Already, 2.1 billion people worldwide lack access to safe drinking water. Three out of four jobs worldwide depend upon access to water and water-related services. Water-limited regions and populations must prepare for changes in water management, addressing existing and emerging weaknesses and learning from mistakes, if possible from other areas, without repeating those errors.
Water management successes often rest on past failures – failures from which scientists, managers, and leaders learn and adapt. This is especially true for California, where hydrologic variability frequently tests water systems and water policy. As the world, especially the arid to semiarid world, looks for water solutions, the failures and lessons from California’s turbulent history can provide guidance for future global water resilience.
Nicholas Pinter, Jay Lund, and Peter Moyle are faculty in the Departments of Earth and Planetary Sciences, Civil and Environmental Engineering, and Wildlife, Fish, and Conservation Biology (respectively) and work together at the Center for Watershed Sciences at the University of California, Davis. Email: email@example.com; firstname.lastname@example.org; email@example.com
Auerswald, K, P. Moyle, S.P.Seibert, and J. Geist. 2019. HESS Opinions: Socio-economic and ecological trade-offs of flood management – benefits of a transdisciplinary approach. Hydrology and Earth System Sciences 23: 1035-1044. https://www.hydrol-earth-syst-sci.net/23/1035/2019/ Open access.
Dettinger MD, Ralph FM, Das T, Neiman PJ, & Cayan DR. 2011. Atmospheric rivers, floods and the water resources of California. Water, 3: 445-478.
Grantham, T.E., R. Figueroa, and N. Prat, 2013. Water management in mediterranean river basins: a comparison of management frameworks, physical impacts, and ecological responses. Hydrobiologia, 719: 451–482.
WHO & UNICEF World Health Organization and the United Nations Children’s Fund, 2017. Progress on drinking water, sanitation and hygiene: 2017 update and SDG baselines. Geneva: World Health Organization (WHO) and the United Nations Children’s Fund (UNICEF).