Authored By:
Edward Ring, Director, Water and Energy Policy
California Policy Center
18002 Irvine Blvd., Suite 108
Tustin, California 92780
&
Marc Joffe , Visiting Fellow
California Policy Center
On Behalf Of:
Board of Directors
Mesa Water District
949.631.1205
1965 Placentia Ave.
Costa Mesa, California 92627
The United States Drought Monitor (USDM), designed as a weekly assessment of drought conditions, is produced by federal and academic partners with its primary contact being the National Drought Mitigation Center at the University of Nebraska-Lincoln. The USDM designates areas in drought by intensity, classified into categories—from “None” (no drought) to “Exceptional Drought” (D4) based on a percentile methodology intended to reflect historical frequencies (e.g., D0-D4 expected 30% of the time).
This report examines the USDM’s reports from 2000–2025, focusing on California and Orange County, where USDM drought categorizations are routinely used as part of the justification to trigger water conservation mandates, restrict development of new water supplies, and justify broad regulatory responses.
Given the high stakes of such decisions, we conducted an independent review of USDM reports from 2000 to 2025, with a focus on statewide trends and more localized impacts in Orange County. Our key findings are as follows:
Our analysis of USDM records for the period 2000–2025 shows that drought categories (D0–D4) were designated to California over 60% of the time—roughly double the frequency implied by the USDM’s own percentile-based methodology. This inflation is not isolated to California; national data also reveal significant over-categorization. This discrepancy suggests potential methodological or institutional bias in the USDM’s “convergence of evidence” approach.
We conducted an independent analysis using a century of climate records from dozens of California-based monitoring stations. Variables included precipitation, snowpack, temperature, relative humidity, dew point, and vapor pressure deficit (a computed value). The post-2000 climate data show no substantial drying trend compared to prior 25-year periods. This undermines the notion that California has entered a new, dramatically drier era with sharply heightened drought frequency.
Water storage data for major California reservoirs show modest declines in some areas and relative stability in others. Variations appear to be more closely linked to population growth, land-use changes, and water management decisions rather than to changes in natural water availability. This further calls into question the assumption that USDM categories accurately reflect real-world water scarcity.
Using a statistical model calibrated against historical climate and drought data, we estimate that the actual increase in drought frequency for California between 2000 and 2025 is approximately 0.83%, far below the observed increase reflected in USDM reports. This further supports the conclusion that the USDM has consistently overstated drought conditions.
In addition to the other findings that call into question USDM methods, the USDM drought classifications are based on “dryness” and do not account for water availability, based on water storage trends. This critical variable is of equal, if not greater, consequence when assessing water stress and when determining water policy priorities.
To ensure future drought policy in California is based on sound science and objective data, our key recommendations are as follows:
The USDM methodology must use transparent inputs and clearly defined calculations to ensure that drought categorizations are independently reproducible and verifiable.
Rename the USDM to reflect its actual function as a “Dryness Rating” (or similarly named metric), clarifying that it does not directly measure water scarcity.
Rename the USDM categories as “Dryness” levels (rather than “Drought” levels)—such as “Moderately,” “Severely,” “Extremely,” or “Exceptionally” Dry—clarifying that the metric does not directly measure water scarcity.
Actual drought assessments should prioritize stored water levels and supply-demand balances, rather than relying solely on “dryness” indicators.
Policymakers should avoid using USDM categorizations to trigger regulation unless the methodology becomes fully transparent and automated, and it is shown to correlate meaningfully with actual water shortages.
In responding to genuine drought events, the focus should shift from water conservation mandates to expanding supply through, for example, large-scale desalination, wastewater recycling, and runoff harvesting in coastal regions, along with a statewide effort to increase reservoir and aquifer recharge capacity.
Our findings raise serious concerns about the USDM’s accuracy and its outsized role in shaping California’s water policy. While drought preparedness remains essential, an overreliance on the mislabeled and apparently inflated USDM categorizations may lead to unnecessary water restrictions, economic inefficiencies, and missed opportunities to invest in long-term water resilience. A more balanced, data-driven approach is needed—one that reflects actual water availability and encourages investments in diverse water supply infrastructure instead of reactive rationing.
The United States Drought Monitor (USDM) is a weekly map that depicts drought conditions in the United States and its territories, released every Thursday. Jointly produced by the National Drought Mitigation Center at the University of Nebraska-Lincoln, the National Oceanic and Atmospheric Administration (NOAA), and the U.S. Department of Agriculture (USDA), it serves as a snapshot of current drought intensity based on a blend of scientific data and expert input. The categorizations range from “None” (no drought) to “Abnormally Dry” (D0) and four categories of drought: “Moderate” (D1), “Severe” (D2), “Extreme” (D3), and “Exceptional” (D4) .
These categories inform disaster response, resource allocation, and policy measures. At the federal level, the USDM categorizations primarily trigger eligibility for disaster relief and financial assistance programs rather than mandatory water conservation measures. In California, the USDM plays a significant role in informing drought emergency declarations by the governor, which in turn enable mandatory water conservation measures. The state references USDM maps to assess drought intensity, with categorizations like D3 or D4 often contributing to proclamations that trigger regulatory water conservation actions.
For example, during the 2014–2017 drought, Governor Jerry Brown declared a statewide emergency when much of California reached D4, leading to mandatory 25% water use reductions for urban water suppliers. In 2021, Governor Gavin Newsom expanded a drought emergency to all counties amid persistent D2–D4 conditions, directing the State Water Resources Control Board (SWRCB) to adopt emergency regulations prohibiting allegedly wasteful practices like “overwatering” lawns.
These measures are not automatically triggered by specific USDM thresholds but are enacted through executive orders and SWRCB regulations when USDM designations indicate intense moisture deficits. Local water utilities and city water providers may impose tiered restrictions (e.g., limiting outdoor watering to certain days) based on state directives, with penalties for non-compliance. The California Public Utilities Commission also uses USDM maps to monitor and enforce conservation in regulated water systems.
For the State of California, the USDM’s weekly report has designated drought status 61% of the time since its inception in 2000 (this includes the DO “Abnormally Dry” category). For Orange County in Southern California, the USDM has designated drought status in 62% of all weekly reports. The significance of designating a near permanent drought status to the state and many of its most populous counties is reflected in ongoing and escalating imposition of what are turning into permanent restrictions on water consumption and is now reflected in legislation that will restrict residential indoor water use statewide to 42 gallons per person per day by 2030.
These mandatory restrictions on water use, in turn, are reflected in less industry investment in new sources of water supplies. They create a disincentive for water agencies to develop reliable and diverse sources of water because they place arbitrary caps on how much total water an agency can deliver to its customers. Instead, they create an incentive for the state and water agencies to declare water emergencies in order to access disaster relief funds. In short, they flip on its head the natural mission of a water agency, which is to invest in the means to deliver abundant and affordable water to their customers.
With so much at stake, it is fitting to assess the process used by the researchers responsible for producing the USDM’s weekly report. This report will therefore investigate and attempt to answer the following questions:
1. How does the USDM define and designate drought categories, and are the USDM drought categorizations consistent with their own methodology?
We assess what the discrepancies are between the USDM’s theoretical percentile-based methodology and designated drought categorizations from 2000–2025. To do this, we compare the USDM’s weekly reports that designate drought status based on historical percentages per category, and measure to what extent those categorizations are consistent with the USDM’s stated methodology. We then calculate how that distorts the amount of time the USDM has declared California to be in some stage of a drought categorization.
2. Has California’s climate changed enough to justify more frequent drought declarations?
To answer this, we review climate and hydrologic data to see whether the 2000s have been extraordinarily dry, and we estimate what the drought categorization frequencies should be in comparison to 20th century data. This review relies on available source data from California-based stations that have historically reported on key climate variables—rainfall, snowpack, temperature, relative humidity, and dew point—to evaluate what trends can be objectively observed when comparing the quarter-century periods 1925-1949, 1950-1974, 1975-1999, and 2000-2024. We also use this data to determine whether, and to what extent, climate conditions have become drier in the 21st century and we estimate the degree to which drier conditions overall might reasonably affect the USDM’s drought assessments.
3. Do water storage and hydrology support USDM drought declarations?
We suggest a more practical set of criteria for the USDM to assess drought conditions in California. In particular, we review the hydrologic conditions, i.e., the availability of stored water for use by California’s urban water agencies. We compare storage data over the past century and observe trends. We then suggest (a) an alternative method to report drought conditions that puts greater emphasis on measuring how much water is banked in reservoir and aquifer storage, and (b) propose a more appropriate name for the USDM report, one that reflects its emphasis on immediate climate conditions and does not imply by its name that water scarcity exists when in fact stored water is available in abundance.
It is important to emphasize that there are inherent difficulties in making these assessments with absolute certainty. USDM personnel, while generous with their time and data, were not themselves aware of precisely how their procedure ascribes weight to the multiple sets of data they incorporate into their weekly drought assessments. At the same time, our own survey of data for the State of California and Orange County took into account every source of raw station reports available, but we had to discard data sets that were missing significant percentages of reports over time because including incomplete reports would not allow us to accurately estimate overall trends.
Moreover, even with a vast pool of data to compile, we contend with the question of which stations are most indicative of overall statewide climate conditions, and which are potentially unrepresentative. We also have to acknowledge that data can vary based not on changes in climate, but on changes in policy. In particular, we recognize that the average amount of water stored in reservoirs does not necessarily indicate the volume of runoff but, rather, can also be affected by new policies that, for example, require releases to maintain higher summertime flows in the Sacramento-San Joaquin Delta.
With these caveats, we nonetheless believe this report will demonstrate that (a) the USDM has overstated the intensity of drought in California and Orange County, and (b) a more valuable tool for reporting drought conditions would be one that emphasizes the amount of stored water available to urban water agencies, and to what degree that signifies water supply security or insecurity for their customers.
The goal of this report is to alter the accepted perception of how accurate the USDM reports “drought” conditions both by revealing the complexity and potential subjectivity of methods, by questioning whether the methods are reliably consistent with the data used by the USDM, and by assessing to what extent objective historical data indicate whether the frequency and intensity of drought conditions in the most recent quarter century are alarmingly different from those same conditions in the previous century.
A final goal of this report is to propose a method of measuring drought to reflect actual water availability, with the hope that this emphasis will restore an incentive to develop more water availability and storage, instead of more water rationing.
The USDM employs a “convergence of evidence” methodology, integrating multiple quantitative indicators with qualitative inputs from local experts and impact reports to designate drought categories. The methodology cannot be replicated by a computer algorithm and thus could be subject to human bias.
The USDM categories are tied to percentile ranges of historical data. As Mark Svoboda and his co-authors explained in a 2002 journal article describing the system:
“As a guideline, the system uses a percentile approach in determining the thresholds for each severity level, and all data used in drought severity determinations are considered with reference to their historical frequency of occurrence for the location and time of year in question.”
Given this statement, we assume that drought categories were created based on a review of climate data from the 20th century, given the lack of availability of United States data from previous centuries.
The theoretical categories and their percentile ranges are as follows:
It appears that the USDM has been altering its characterization of these percentile values in recent years. In their 2002 journal article, Svoboda, et. al., stated that “Each category is associated with its percentile chance of happening in any given year out of 100 yr.”
In the version of the Drought Classification diagram published on the USDM’s website in 2019, it labeled these values as “Objective Drought Indicator Blends (Percentiles)”. Today, the same web page labels these numbers as “Example Percentile Range for Most Indicators” (emphasis added).
Analysis of USDM data from 2000 to 2025 reveals that the actual frequency of drought category designation deviates from the theoretical percentiles – derived as a baseline using climate data from the 20th century – as outlined in the methodology. The following charts, derived from data downloads from the USDM website, illustrate these discrepancies across national, California, Orange County, and Newport Bay regions. In these charts, the left column (labeled “Theoretical”) reflects the percentiles stated in the USDM methodology and listed in the previous section. The Designated (2000-2025) column reflects the percentages of D0-D4 categorizations designated by the USDM from its inception through early September 2025.
National Drought Category Distribution (2000–2025)
The first chart compares theoretical vs. designated drought category frequencies for the United States and Puerto Rico from January 2000 through early September 2025. The table shows that D0-D4 categorizations (“Abnormally Dry” through “Exceptional Drought’) are designated much more frequently (43.53%) than suggested by the USDM methodology (30.00%).
California Drought Category Distribution (2000–2025)
Next, we show the same comparison just for areas within California. The deviation between theoretical and designated drought categorization is even greater than it is for the whole United States, with some dryness/drought categorization (D0-D4) designated more than twice as often (60.65% v. 30.00%) than the methodology would suggest.
Orange County Drought Category Distribution (2000–2025)
Within Orange County, CA, the deviation is slightly more pronounced than it is statewide (61.97% v. 30.00%).
Newport Bay Drought Category Distribution (2000–2025)
Finally, drought category frequencies within the Mesa Water District (Mesa Water®) service area for the Newport Bay Hydrologic Unit Code (HUC) deviate even more, with 62.59% of observations involving a DO-D4 categorization compared to the 30.00% proportion suggested by the published methodology.
Summarizing the Drought Category Frequencies
The following table summarizes the relative frequencies graphed in the preceding sections. In all four cases, designated USDM drought categorizations from 2000-2025 indicate more intense drought conditions than the methodology (“Theoretical” column) suggests. The deviation is especially notable in California and its local subdivisions we have analyzed.
| Category | Theoretical | National Designated | California Designated | Orange County Designated | Newport Bay Designated |
| None | 70.00% | 56.47% | 39.35% | 38.03% | 37.41% |
| D0 | 10.00% | 17.39% | 15.46% | 13.37%. | 14.19% |
| D1 | 10.00% | 11.35% | 15.32% | 15.64% | 15.54% |
| D2 | 5.00% | 8.41% | 15.42% | 17.96% | 17.80% |
| D3 | 3.00% | 4.83% | 9.02% | 7.72% | 5.36% |
| D4 | 2.00% | 1.55% | 5.43% | 7.26% | 9.69% |
The conclusion indicated by the USDM reports is not subtle. The USDM indicates California as being drought-free (“None”) barely half as often in the most recent 25 years compared to the previous century. Similarly, in the categorizations of “Severe Drought” in California, the USDM shows a remarkable increase. For example, the incidence of years when the USDM reports D4 (“Exceptional Drought”) shows an increase from 2% in the 20th century baseline to over 5% in the 21st century to-date.
In the next section we will evaluate source data over the past 100 years to determine if such a dramatic shift in climate between this century and the previous one can be independently verified.
If the climate has, in fact, become drier than in the 21st Century, some deviation from the theoretical percentiles may be justified. So next, we review various long time-series of California climate data to assess whether such a trend can be identified and, if present, how strong it may be. We consider precipitation, snow depth, temperature, relative humidity, dew point, and vapor pressure deficits.
Precipitation Data
The Applied Climate Information System (ACIS), developed by the NOAA Regional Climate Centers (RCCs), has long histories of daily weather summaries. Unfortunately, many older weather stations have either stopped reporting or have considerable gaps in their data.
We found 39 California weather stations that had “almost complete data” for the 100 years between 1925 and 2024. By “almost complete” we mean having data for at least 90% of the months during the 100-year period. 25-year averages for these 39 stations are as follows:
One of these 39 stations is Newport Beach Harbor in Mesa Water’s service area, so we report its averages separately.
Snowpack
Some weather stations have a long-time series of snow depths, but unfortunately data prior to World War 2 is relatively sparse. Consequently, we can only provide data for three 25-year periods in this section.
The USDA Natural Resources Conservation Service’s National Water and Climate Center collects monthly snowpack data from thousands of weather stations globally. We found 65 California stations in its data set that consistently reported monthly snow depth data since 1950. In the following chart, we report average snow depths for these 65 stations as of April 1st of each year.
Temperature, Relative Humidity, Dew Point, and Vapor Pressure Deficit
The Iowa Environmental Mesonet (IEM) has long time series of temperature, relative humidity, and dew point data for thousands of weather stations around the country. We found 51 California weather stations which frequently reported this data on an hourly basis for the 75 calendar years after January 1, 1950, and present 25-year averages below (data are reported in degrees Fahrenheit).
There is relatively little variability in the temperatures across the three periods, with a difference of 0.55° Fahrenheit between the first and last periods. It is also worth noting that the average of the first two temperature bars (60.83°) is virtually the same as the final bar (60.86°).
Some of the variability may be attributable to the Urban Heat Island (UHI) effect as more land was paved over. We identified 13 stations of the 51 that were especially prone to UHI by interrogating the Grok and Gemini large language models. After removing observations from these 13 stations we obtained averages for the remaining 38 stations in the data set, obtaining the following results.
This reduced the gap between the first and last observations to just 0.33° Fahrenheit, and the overall pre-2000 average is higher than the 2000-2024 average. Our findings raise questions about the intensity of anthropogenic global warming over the past half century.
Next, we present dew point averages for the full set of 51 stations, once again using hourly observations. The dew point is the temperature at which the air would be fully saturated under current conditions. In other words, it is the temperature at which the relative humidity would be 100%.
Next we report average relative humidity for the three stations over the same time, once again using hourly observations.
Finally, we show a calculated figure often used in drought analysis. The Vapor Pressure Deficit (VPD) is the difference between the Actual Vapor Pressure and Saturation Vapor Pressure and is normally measured in kiloPascals (kPa).
For each hourly weather station observation, we calculated VPD from the observed temperature and relative humidity and then computed averages across the 51 stations.
We see little variance over the 75-year time period.
More locally, we found average temperature data on ACIS for the Newport Beach Harbor weather station, and can report 100 years of data from the daily summaries available on that data set.
Although this station shows a steady and pronounced temperature increase, it is worth repeating that the statewide averages did not show significant temperature change.
Based on 75-100 years of source data, there is limited evidence that droughts in California are more intense in this century. The statewide annual rainfall average from 2000-2024 is indeed lower, at 17.6 inches, than the most recent previous quarter century from 1975-1999 of 20.1 inches, but is only marginally lower than the two quarter centuries before that: 18.7 inches from 1950-1974, and 18.2 inches from 1925-1949. This hardly constitutes a precipitous drop in average rainfall.
While average snow depth does show a statistically meaningful drop from a high of 58.3 inches in 1950-1974 vs. 47.6 inches in 2000-2024, we lack data for earlier periods, and cannot account for other variables including the impact of greatly increasing forest density in recent decades that causes snow to collect in the canopy and evaporate. Furthermore, additional raw data, in particular temperature, dew point, and vapor pressure deficit, are virtually unchanged in the period for which we have data, 1950 through 2024.
Overall, while source data may indicate a minor drying trend between this century and the last one, as our evaluation will further demonstrate, it is incremental at most, and not at all remarkable or significant.
The California Data Exchange Center (CDEC) managed by the California Department of Water Resources (DWR) has long histories of hydrology data. In the following charts, we include storage (in acre feet) for the three major state water project reservoirs. Monthly data for all three are available from October 1968 to present (Folsom Lake goes back to 1955).
The first chart shows the full-time series of storage data for the three facilities.
Lacking a full 75 years of data, we compare full year averages of observations from before the USDM was published and thereafter.
It is possible that the drop in storage could be explained, in part, by increased outflows required by the state’s increasing population. But CDEC does not have enough historic inflow and outflow data to confirm or contradict this assumption.
Aside from state water projects dams, there are three sizable water storage facilities that have at least 75 years of data: Lake Mohave, Lake Almanor, and Pardee (although Lake Mohave is not located in California, it is part of the Colorado River system which supplies water to the state). We found a few missing observations and interpolated them from previous and following month data. These three reservoirs show less volatility and no tendency toward reduced storage over an extended time.
The CDEC data does not include historical data for reservoirs in Orange County. The nearest facilities to Orange County in the CDEC database are Castaic Lake and Pyramid Lake in Los Angeles County and Lake Perris in Riverside County. Storage data goes back only to 1974 and is displayed in the graphs below (as with the last charts, a few missing entries were interpolated). Average storage across the three dams fell by less than 4% between the 25 years through 1999 and the most recent 25 years.
What is evident from reservoir data is that three of the biggest dams that are part of the state water project indeed show lower levels this century compared to the 2nd half of the 20th century. But it is impossible to detach these findings from policies. Precipitation has not declined appreciably, but water management at the state level has changed dramatically.
San Luis, for example, is a major off-stream reservoir that is filled up and drained in accordance with regulations set by the California DWR. Over the past two decades, the amount of water that can be stored and moved to the reservoir has been restricted due to new levels of endangered fish protection in the Sacramento-San Joaquin Delta. Additionally, since 2007, San Luis has also been left below capacity for the past several years due to ongoing work to seismically retrofit the dam. Work is not projected to be complete on San Luis until 2027.
Similarly, Lake Oroville, the largest reservoir in the State Water Project system, starting in 2017, was left at barely 40% of its full capacity for over two years in order to complete repairs on its spillway.
Finally, the California DWR has deliberately mandated lower levels in reservoirs in recent decades in order to leave more space available to protect against what the state perceives to be growing flood risk. This is predicated on a perception that the climate is shifting toward more extreme rainfall necessitating more available reservoir capacity, but this decision making is also driven by concern over the condition of the state’s dams as exemplified in the 2017 spillway failure at Lake Oroville, as well as the decreasing capacity of the state’s reservoirs due to accumulated silt.
We contend that these factors – dramatic shifts in policy with respect to managing flood risk and protecting fish, and storage drawdowns to facilitate maintenance work – are the primary drivers of less water storage in California’s major reservoirs. Absent these factors, we find that unremarkable changes in overall precipitation cannot explain somewhat lower average storage. Hydrological drought, such as it is, results from changes in policy, not climate change.
Thus far, we have seen that the USDM is designating drought categorizations—including intense drought categories—much more frequently than its stated methodology suggests. This could be explained by greater dryness than expected when the methodology was developed. But given the very large departure, changing climate conditions may not be a sufficient explanation. In this section, we discuss the results of a quantitative model that compared pre-2000 and post-2000 climate observations to determine how much of an increase in USDM drought categorization is empirically justified.
In this section, we focus on the distribution of drought categories for California as a whole, taking advantage of the data presented in this report’s “Comparisons of Pre-2000 and Post-2000 Climate Data” section. Aside from averages, we calculated other descriptive statistics for the data sets we collected. We then loaded those statistics into large language models (Grok) and asked it to calculate an empirically justified distribution of post-2000 drought categories.
The indented text below is the explanation Grok generated to explain its approach to calculating this empirically supported distribution of D0-D4 categories:
Imagine the USDM as a teacher grading weather conditions on a curve set by pre-2000 data. If today’s weather is much drier than that old standard, it gets a “drought” grade more often. Our method updates the expected grades (frequencies) for California by comparing recent weather (2000–2024) to the old curve, using four key variables: rainfall (less rain = drier), snowpack (less snow = drier), temperature (hotter = drier), and vapor pressure deficit (higher = drier air, more evaporation). These are core to how the USDM assesses drought, as it blends precipitation, evaporation, and related factors.
Here’s how we do it, step by step, in plain terms:
This method is like checking how often a student would score an A, B, or C on an old test using their new study habits. It keeps the USDM’s rules but adjusts for California’s new climate reality, such as less rain or hotter days.
The following chart compares the drought frequencies Grok calculated (“modeled”) with the frequencies described in USDM documentation (“theoretical”) with those designated by the USDM since 2000.
Because conditions have been drier in the 2000s (i.e., less rainfall) the model agrees that there should be some increase in dryness and drought designations. But the increase suggested by the model (0.83%) across all categories is well below the 30.65% departure we have observed.
We performed similar analysis with Google’s Gemini, and that model also calculated a far more modest increase in drought categorizations than those published by the USDM since 2000.
Because conditions have been drier in the 2000s (i.e., less rainfall) the model agrees that there should be some increase in dryness and drought designations. But the increase suggested by the model (0.83%) across all categories is well below the 30.65% departure we have observed.
We performed similar analysis with Google’s Gemini, and that model also calculated a far more modest increase in drought categorizations than those published by the USDM since 2000.
Edward Ring is the director of water and energy policy for the California Policy Center, which he co-founded in 2013 and served as its first president. His work has appeared in the Los Angeles Times, the Wall Street Journal, National Review, City Journal, and other media outlets. Ring’s undergraduate degree is in Political Science from UC Davis, and he has an MBA in Finance from USC. Ring is the author of several books, including “Fixing California – Abundance, Pragmatism, Optimism” (2021), “The Abundance Choice – Our Fight for More Water in California” (2022), and “Solutions – Innovative Public Policy for California” (2024).
Marc Joffe is President of the Contra Costa Taxpayers Association and a California Policy Center visiting fellow. After a long career in the financial industry, including a senior director role at Moody’s Analytics, he transitioned to policy research at CPC and the Reason Foundation. Joffe’s research focuses on government finance and state policy issues. Marc earned an MBA from New York University and an MPA from San Francisco State University.
About the District
Founded on January 1, 1960, and governed by a publicly elected, five-member Board of Directors, Mesa Water is an independent special district that provides water service to 110,000 residents in an 18-square-mile service area that includes most of Costa Mesa, a portion of Newport Beach, and John Wayne Airport. Mesa Water provides 100 percent local reliable groundwater to its customers due to the Mesa Water Reliability Facility.