Reservoir Sites
Falling Creek Reservoir
- Site 50
- Verbal Description: Deep hole nearest to the dam of Falling Creek Reservoir
o Latitude: 37.30325
o Longitude: -79.83726
- Site 45
- Verbal Description: Upstream pelagic site nearest to the deep hole of Falling Creek Reservoir
o Latitude: 37.30418
o Longitude: -79.83833
- Site 30
- Verbal Description: Upstream pelagic site in transitional zone of Falling Creek Reservoir
o Latitude: 37.30534
o Longitude: -79.83825
- Site 20
- Verbal Description: Different upstream pelagic site in transitional zone of Falling Creek Reservoir
o Latitude: 37.30769
o Longitude: -79.8371
- Site 99
- Verbal Description: Farthest downstream site on inflow stream to Falling Creek Reservoir.
o Latitude: 37.307613
o Longitude: -79.8360878
- Site 100
- Verbal Description: Inflow stream to Falling Creek Reservoir.
o Latitude: 37.30858
o Longitude: -79.83494
- Site 101
- Verbal Description: Upstream site along inflow to Falling Creek Reservoir.
o Latitude: 37.309653
o Longitude: -79.830467
- Site 102
- Verbal Description: Furthest upstream site on inflow stream to Falling Creek Reservoir.
o Latitude: 37.311678
o Longitude: -79.827357
- Site 200
- Verbal Description: Secondary inflow (wetland) stream to Falling Creek Reservoir.
o Latitude: 37.30943
o Longitude: -79.8361
- Site 01
- Verbal Description: Outflow site at spillway of Falling Creek Reservoir.
o Latitude: 37.30247
o Longitude: -79.83692
Beaverdam Reservoir
- Site 50
- Verbal Description: Deep hole nearest to the dam of Beaverdam Reservoir.
o Latitude: 37.31288
o Longitude: -79.81593
- Site 45
- Verbal Description: Upstream pelagic site nearest to the deep hole of Beaverdam Reservoir
o Latitude: 37.314465
o Longitude: -79.818717
- Site 30
- Verbal Description: Upstream pelagic site in transitional zone of Beaverdam Reservoir.
o Latitude: 37.31921
o Longitude: -79.818226
- Site 20
- Verbal Description: Different upstream pelagic site in transitional zone of Beaverdam Reservoir.
o Latitude: 37.30769
o Longitude: -79.8371
- Site 100
- Verbal Description: Inflow stream to Beaverdam Reservoir.
o Latitude: 37.31957
o Longitude: -79.82437
- Site 200
- Verbal Description: Right arm inflow to Beaverdam Reservoir.
o Latitude: 37.322851
o Longitude: -79.81721
- Site 01
- Verbal Description: Outflow pipe in transitional zone of Beaverdam Reservoir.
o Latitude: 37.314783
o Longitude: -79.820864
Carvins Cove Reservoir
- Site 50
- Verbal Description: Deep hole nearest to the dam of Carvins Cove Reservoir.
o Latitude: 37.369712
o Longitude: -79.957976
- Site 1
- Verbal Description: Site near floating platform at Carvins Cove Reservoir.
o Latitude: 37.3839
o Longitude: -79.9491
- Site 2
- Verbal Description: Near shore site at Carvins Cove Reservoir.
o Latitude: 37.3850
o Longitude: -79.9510
- Site 3
- Verbal Description: Pelagic site upstream of boat launch at Carvins Cove Reservoir.
o Latitude: 37.3922
o Longitude: -79.9488
- Site 4
- Verbal Description: Site near boat launch at Carvins Cove Reservoir.
o Latitude: 37.3845
o Longitude: -79.9471
- Site 5
- Verbal Description: Pelagic site downstream of boat launch at Carvins Cove Reservoir.
o Latitude: 37.3788
o Longitude: -79.9529
Lake Sunapee
- Site 50
- Verbal Description: Site of the Lake Sunapee Protective Association water quality buoy.
o Latitude: 43.391308
o Longitude: -72.058973
- Site 40
- Verbal Description: Deepest site in close proximity to the Lake Sunapee Protective Association water quality buoy
o Latitude: 43.382772
o Longitude: -72.064545
CCC developed and led the reservoir monitoring program 2013-present, and oversaw the collection and analysis of this dataset throughout this time. JHW is the point person for chlorophyll-a data collation and laboratory analysis, QAQC and publishing from 2019 - 2021. ABP led field collection in 2020 and 2021. WMW helped coordinate and supervise chlorophyll-a analysis and processing from 2019-2021. AD and CEB led field prep and post-processing in 2021. MEL was the point person for chl data collection, analysis, and QAQC from 2016–2018. KDH was the point person for chl data collection, analysis, QAQC and publishing from 2014-2015, and JPD was the point person for data collection, analysis, QAQC and publishing for 2013-2014. BRN developed analysis methods, led chemical analyses during COVID 19 (2020-2021), and trained all co-authors on analytical chemistry instruments, analyses, and QAQC best practices.
From 2014 to 2019, multiple whole-ecosystem manipulations were conducted at Falling Creek Reservoir. These manipulations include intermittent operation of hypolimnetic oxygenation and pulsed epilimnetic mixing engineering systems. For a detailed description of the hypolimnetic oxygenation engineered system, see Gerling et al. (2014) and for a detailed description of the epilimnetic mixing engineered system, see Chen et al. (2017). These systems were operated over time from 2014-2018 following Table 1 in Gerling et al. (2016), Table 1 in Munger et al. (2016), and Table 2 in McClure et al. (2018). In 2019, hypolimnetic oxygenation was conducted from June 3-June 17, July 8-July 22, August 5-August 19 and September 2-November 20.
Chen, S., C. Lei, C.C. Carey, P.A. Gantzer, and J.C. Little. 2017. Predicting hypolimnetic oxygenation and epilimnetic mixing in a shallow eutrophic reservoir using a coupled three-dimensional hydrodynamic model. Water Resources Research. 53: 470-484. DOI: 10.1002/2016WR019279
Gerling, A.B., Browne, R.G., Gantzer, P.A., Mobley, M.H., Little, J.C., and C.C. Carey. 2014. First report of the successful operation of a side stream supersaturation hypolimnetic oxygenation system in a eutrophic, shallow reservoir. Water Research. 67: 129-143. doi: 10.1016/j.watres.2014.09.002
Gerling, A.B., Z.W. Munger, J.P. Doubek, K.D. Hamre, P.A. Gantzer, J.C. Little, and C.C. Carey. 2016. Whole-catchment manipulations of internal and external loading reveal the sensitivity of a century-old reservoir to hypoxia. Ecosystems. 19:555-571. DOI: 10.1007/s10021-015-9951-0
McClure, R.P., K.D. Hamre, B.R. Niederlehner, Z.W. Munger, S. Chen, M.E. Lofton, M.E. Schreiber, and C.C. Carey. 2018 Metalimnetic oxygen minima alter the vertical profiles of carbon dioxide and methane in a managed freshwater reservoir. Science of the Total Environment 636: 610-620. DOI: 10.1016/j.scitotenv.2018.04.255
Munger, Z.W., C.C. Carey, A.B. Gerling, K.D. Hamre, J.P. Doubek, S.D. Klepatzki, R.P. McClure, and M.E. Schreiber. 2016. Effectiveness of hypolimnetic oxygenation for preventing accumulation of Fe and Mn in a drinking water reservoir. Water Research. 106: 1-14. DOI: 10.1016/j.watres.2016.09.038.
Lofton, M.E., McClure, R.P., Chen, S., Little, J.C., and C.C. Carey. 2019. Whole-ecosystem experiments reveal varying responses of phytoplankton functional groups to epilimnetic mixing in a eutrophic reservoir. Water. 11, 222; DOI:10.3390/w11020222.
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