Real-time Estimates of Hypoxic Water Volume

Chesapeake Bay

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Quick Summary

Scientists estimate the amount of hypoxia in the Chesapeake Bay using a metric called the "hypoxic volume," which is the volume of water in the Bay with a dissolved oxygen concentration less than 2 milligrams per liter (mg/L). This volume represents an approximate size of the Dead Zone in the Bay. In the spring, the size of the summer dead zone is forecast based on the amount of nutrients supplied to the Bay. Once or twice a month, boats are used to collect observations and estimate the hypoxic volume. However, both these methods provide very infrequent estimates of hypoxic volume.

The Chesapeake Bay Environmental Forecast System estimates the hypoxic volume every day. The daily hypoxic volume forecasts are used to calculate the total annual hypoxic volume throughout the year. This metric provides a single number that represents the severity of hypoxia in a given year. The model was used to estimate hypoxic volume for each day from 1985 through 2023 for comparison with 2024. These daily estimates are based on complex computer models that continue to be improved; therefore, past estimates may be updated as improvements are made to the models.

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2024 Dead Zone Size

The amount of hypoxia in the Bay is expected to increase from spring into summer and then decrease as summer progresses into fall, with hypoxia starting sometime in May. Check back to see how the size of the dead zone increases seasonally and how daily weather changes the amount of hypoxia. Notable weather that may impact the amount of hypoxia are very windy days or periods of very calm wind. The image below will be continually updated throughout 2024 based on the daily forecast model.

In summer 2024 the amount of hypoxia consistently increased to a moderate value over the month of May and was higher than in the past 4 years at the end of May. Modeled hypoxia then increased quickly in the beginning of June to a level not often seen in early June. Hypoxia remained relatively severe throughout June; both for the month of June and relative to the past 4 years. The CBEFS team is investigating what conditions may have caused the increase to a large amount of hypoxia in early June. So far, hypoxia in summer 2024 is more severe than in the past 4 years.

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Hypoxic Volume (HV) Metrics for Recent Years for Comparison to 2024 Forecast
Year Maximum Daily HV [km3] Average Summer HV [km3] Hypoxic Duration [days] Total Annual HV [km3 days]
Historical 5.2 to 15.6 2.3 to 7.9 77 to 119 323 to 1,030
2020 10.7 (13%) 5.0 (6%) 101 623 ± 81
2021 8.4 (10%) 5.0 (6%) 143 720 ± 94
2022 10.4 (13%) 5.4 (7%) 114 673 ± 87
2023 4.3 (5%) 2.4 (3%) 113 336 ± 44

Notes: 1 km3 equals about 400,000 Olympic-sized swimming pools of water. Percents (%) represent the percent of the Bay that was hypoxic based on the volume of the Bay and tidal tributaries in the forecast model. Historical values are based on a 39-year simulation and represent the normal range in conditions between 1985 to 2023 (median ± one standard deviation).

  • Maximum Daily Hypoxic Volume (km3): The maximum volume of Chesapeake Bay water experiencing hypoxic conditions on any given day
  • Average Summer Hypoxic Volume (km3): The average volume of hypoxic water from June through September
  • Hypoxic Duration (days): The number of days in a given year between the first and last day of hypoxic conditions exceeding 2 km3 in volume
  • Total Annual Hypoxic Volume (km3 days): The total amount of hypoxia in the Bay for a given year, calculated by summing the hypoxic volume on each day. Uncertainty in total annual hypoxic volume estimates from cruise-based observed data has been estimated at 13% (Bever et al. 2018, Table 4). The 13% was adopted here as a general estimate of the uncertainty of the total annual hypoxic volume for each year, represented by the plus and minus (±) value.
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Historical Hypoxic Volumes

The table below provides yearly metrics of model-estimated hypoxic volumes and the duration of hypoxia from 1985 through 2023. These metrics of hypoxia were derived using daily hypoxic volumes from long model simulations. The daily hypoxic volume and total annual hypoxic volume were calculated from the daily-averaged 3D model output following Bever et al. (2018). The duration of hypoxia was calculated from the daily estimates of hypoxic volume following Bever et al. (2013). The average summer hypoxic volume is the average volume of hypoxic water on each day from June through September. These yearly metrics of the severity of hypoxia in Chesapeake Bay are thus based on computer models that continue to be improved; therefore past estimates, such as those in the below table, may be updated as improvements to the model are made.

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Year Maximum Daily HV [km3] Average Summer HV [km3] Hypoxic Duration [days] Total Annual HV [km3 days]
1985 6.7 (8%) 3.6 (4%) 119 541 ± 70
1986 9.6 (12%) 5.0 (6%) 95 688 ± 89
1987 11.5 (14%) 5.1 (6%) 85 633 ± 82
1988 8.3 (10%) 3.9 (5%) 79 484 ± 63
1989 13.1 (16%) 6.8 (8%) 108 835 ± 109
1990 11.4 (14%) 5.3 (6%) 113 678 ± 88
1991 12.2 (15%) 5.2 (6%) 107 785 ± 102
1992 5.7 (7%) 2.2 (3%) 61 272 ± 35
1993 21.6 (26%) 11.1 (14%) 117 1,413 ± 184
1994 20.1 (25%) 9.5 (12%) 96 1,157 ± 150
1995 6.1 (7%) 2.7 (3%) 81 348 ± 45
1996 16.9 (21%) 9.0 (11%) 114 1,123 ± 146
1997 15.3 (19%) 6.8 (8%) 107 879 ± 114
1998 17.9 (22%) 9.7 (12%) 101 1,208 ± 157
1999 3.6 (4%) 1.5 (2%) 59 192 ± 25
2000 12.9 (16%) 5.3 (6%) 99 697 ± 91
2001 5.3 (6%) 2.7 (3%) 89 350 ± 46
2002 3.8 (5%) 1.3 (2%) 48 162 ± 21
2003 21.6 (26%) 10.7 (13%) 98 1,323 ± 172
2004 16.6 (20%) 9.0 (11%) 136 1,274 ± 166
2005 15.9 (19%) 8.6 (10%) 97 1,063 ± 138
2006 10.7 (13%) 4.8 (6%) 97 621 ± 81
2007 9.9 (12%) 5.3 (6%) 97 676 ± 88
2008 15.4 (19%) 7.2 (9%) 88 885 ± 115
2009 8.1 (10%) 4.4 (5%) 94 547 ± 71
2010 12.6 (15%) 6.2 (8%) 108 861 ± 112
2011 17.7 (22%) 8.8 (11%) 113 1,091 ± 142
2012 8.6 (10%) 4.5 (5%) 107 657 ± 85
2013 7.6 (9%) 3.6 (4%) 91 444 ± 58
2014 12.1 (15%) 6.4 (8%) 101 785 ± 102
2015 6.0 (7%) 2.8 (3%) 71 350 ± 46
2016 7.0 (9%) 3.2 (4%) 80 394 ± 51
2017 5.0 (6%) 1.9 (2%) 71 238 ± 31
2018 10.0 (12%) 4.8 (6%) 100 593 ± 77
2019 20.2 (25%) 11.6 (14%) 154 1,688 ± 219
2020 10.7 (13%) 5.0 (6%) 101 623 ± 81
2021 8.4 (10%) 5.0 (6%) 143 720 ± 94
2022 10.4 (13%) 5.4 (7%) 114 673 ± 87
2023 4.3 (5%) 2.4 (3%) 113 336 ± 44

  

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2024 Model-Data Comparison (Model Accuracy)

The Maryland Department of Natural Resources and Old Dominion University periodically collect dissolved-oxygen data from the water surface to the seabed as part of the long-term Water Quality Monitoring Program. We use these data to calculate an estimate of the hypoxic volume, which we compare with the hypoxic volume estimated using the model. The data-based and model-based estimates of hypoxic volume will not be the same because different methods are used for each. However, we expect they should be similar and follow a similar seasonal pattern. The image and text below compare the model-based and data-based hypoxic volumes; we periodically update the data-based hypoxic volumes through the summer as more data become available. The black lines above and below the gray dots show the uncertainty in the data-based estimate of hypoxic volume. The blue lines are hourly model-based hypoxic volumes calculated over the duration of the data collection cruises and in a similar manner to how the data-based hypoxic volumes are calculated. 

Both the model-based and the data-based hypoxic volumes show hypoxia starting in early-May, with the model-based and data-based estimates of hypoxic volume matching very well in mid-May. The estimates of hypoxic volume are higher than the historical average in mid-May. Model-based and data-based estimates of hypoxic volume then increased into June Continue to check back to see how hypoxia progresses throughout the remainder of the summer.

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Synopsis of 2023 Dead Zone Size

Hypoxia in summer 2023 really began in mid-May, increased to a moderate level, and then leveled off. Hypoxia remained at low to moderate levels throughout June, July, August, and September. The spring-time nutrient supply to the Bay was relatively low which may have contributed to the low amount of hypoxia. In 2023, hypoxia was uncharacteristically small from June until ending in late-September. The quick end in hypoxia resulted from temperatures cooling and stronger winds from the passing of Tropical Storm Ophelia, both of which act to limit the amount of hypoxia in the Bay. Overall, the duration of hypoxia in summer 2023 was normal, and the total annual amount of hypoxia and the maximum daily amount of hypoxia were quite low, representing a very good year for hypoxic conditions in the Bay.

 2023_NV_realtime

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Summary of 2023 Model to Data Comparison (Model Accuracy)

The Maryland Department of Natural Resources and Old Dominion University periodically collect dissolved-oxygen data from the water surface to the seabed as part of the long-term Water Quality Monitoring Program. We use these data to calculate an estimate of the hypoxic volume, which we compare with the hypoxic volume estimated using the model. The data-based and model-based estimates of hypoxic volume will not be the same because different methods are used for each. However, we expect they should be similar and follow a similar seasonal pattern. The image and text below compare the model-based and data-based hypoxic volumes; we periodically update the data-based hypoxic volumes through the summer as more data become available. The black lines above and below the gray dots show the uncertainty in the data-based estimate of hypoxic volume.

Both the model-based and the data-based hypoxic volumes show hypoxia starting in mid-May. The model-based and data-based estimates for June both show relatively low amounts of hypoxia. Although, the data-based estimate is noticeably lower than the model-based estimate. Both the model-based and data-based estimates for July suggest a low to moderate amount of hypoxia, continuing the trend of 2023 being a relatively mild year for hypoxia in the Bay. Continue to check back to see how hypoxia progresses throughout the remainder of the summer.

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