Abstract:Reliable estimation of freshwater inflow to the ocean from large tidal rivers is vital for water resources management and climate analyses. Discharge gauging stations are typically located beyond the tidal intrusion reach, such that inputs and losses occurring closer to the ocean are not included. Here, we develop a method of estimating river discharge using multiple gauges and time‐dependent tidal statistics determined via wavelet analysis. The Multiple‐gauge Tidal Discharge Estimate (MTDE) method is develope… Show more
“…Therefore, the collapse of the M6 overtide in Boston Harbor likely reflects the greater average depth of the system caused both by channel deepening and by the significant loss of subtidal and intertidal habitat (Figure ). Interestingly, the M4 overtide slightly increased over time (Figure b), possibly indicating an increase in the (small) tidally averaged flow (e.g., river discharge or the return flow caused by tidal Stokes drift—see, e.g., Moftakhari et al, ) but also potentially caused by a decrease in damping of the overtide produced on the continental shelf (e.g., as occurs in the Ems Estuary; see Chernetsky et al, ). The divergence in the M4 and M6 overtide trends is an interesting challenge for a future numerical or analytical model to reproduce and explain.…”
Using newly‐discovered archival measurements, we construct an instrumental record of water levels and storm tides in Boston (MA) since 1825. After ascertaining the 19th century datum and correcting for a 0–0.03 m bias in the modern tide‐gauge record, we show that local, decadally‐averaged relative sea level (RSL) rose by 0.28 ± 0.05 m since 1826, with an acceleration of 0.023 ± 0.009 mm/yr2. Tide range decreased by 5.5% between 1830 and 1910, due in large part to dredging and filling of Boston Harbor, and trended slightly upward thereafter. An evaluation of storm events since 1825 suggests that trends in flood risk are driven by RSL rise, with a small contribution by tidal trends. Sea‐level rise also interacts with the 18.6 year nodal cycle in tide amplitudes to produce decadal fluctuations in hazard. Conditional sampling of the 1825–2018 record shows that storm tides with a 0.01–0.5 annual probability (100 and 2 year events) are 0.1–0.2 m larger during periods with above‐average tidal amplitudes. Similarly, the once‐in‐25 year event during elevated tidal forcing becomes a once‐in‐100 year event during periods of reduced tides. A plurality of historic flood events—including floods in 1851, 1978, and 2018—occurred near the peak of the tidal nodal cycle. Projections to the year 2100 suggest that decadal fluctuations in tide characteristics will interact with relative sea‐level rise to produce a fluctuating hazard over time, with periods of relative stationarity (e.g., the 2020s) bracketed by relatively abrupt increases in flood hazard (the early 2030s).
“…Therefore, the collapse of the M6 overtide in Boston Harbor likely reflects the greater average depth of the system caused both by channel deepening and by the significant loss of subtidal and intertidal habitat (Figure ). Interestingly, the M4 overtide slightly increased over time (Figure b), possibly indicating an increase in the (small) tidally averaged flow (e.g., river discharge or the return flow caused by tidal Stokes drift—see, e.g., Moftakhari et al, ) but also potentially caused by a decrease in damping of the overtide produced on the continental shelf (e.g., as occurs in the Ems Estuary; see Chernetsky et al, ). The divergence in the M4 and M6 overtide trends is an interesting challenge for a future numerical or analytical model to reproduce and explain.…”
Using newly‐discovered archival measurements, we construct an instrumental record of water levels and storm tides in Boston (MA) since 1825. After ascertaining the 19th century datum and correcting for a 0–0.03 m bias in the modern tide‐gauge record, we show that local, decadally‐averaged relative sea level (RSL) rose by 0.28 ± 0.05 m since 1826, with an acceleration of 0.023 ± 0.009 mm/yr2. Tide range decreased by 5.5% between 1830 and 1910, due in large part to dredging and filling of Boston Harbor, and trended slightly upward thereafter. An evaluation of storm events since 1825 suggests that trends in flood risk are driven by RSL rise, with a small contribution by tidal trends. Sea‐level rise also interacts with the 18.6 year nodal cycle in tide amplitudes to produce decadal fluctuations in hazard. Conditional sampling of the 1825–2018 record shows that storm tides with a 0.01–0.5 annual probability (100 and 2 year events) are 0.1–0.2 m larger during periods with above‐average tidal amplitudes. Similarly, the once‐in‐25 year event during elevated tidal forcing becomes a once‐in‐100 year event during periods of reduced tides. A plurality of historic flood events—including floods in 1851, 1978, and 2018—occurred near the peak of the tidal nodal cycle. Projections to the year 2100 suggest that decadal fluctuations in tide characteristics will interact with relative sea‐level rise to produce a fluctuating hazard over time, with periods of relative stationarity (e.g., the 2020s) bracketed by relatively abrupt increases in flood hazard (the early 2030s).
“…However, as river flow increases, there is a subsequent decrease in D6 generation [ Parker , ]. Alternately, a strong Stokes drift return flow could mimic river flow and produce D4 [ Moftakhari et al ., ]. To test whether this mechanism produced D4 in the Gironde, the Stokes drift transport was approximated in one dimension as (following Moftakhari et al .…”
Section: Discussionmentioning
confidence: 99%
“…To test whether this mechanism produced D4 in the Gironde, the Stokes drift transport was approximated in one dimension as (following Moftakhari et al . [] adapted from Longuet‐Higgins []). Here Q stokes is the Lagrangian Stokes drift, is the D2 tidal velocity amplitude, is the D2 tidal height amplitude, is the phase of the tidal velocity, and is the phase of the tidal height.…”
Transverse variations of tidal and subtidal flow were investigated in a macrotidal and convergent estuary. This was accomplished by combining data analysis of current velocities and water density with numerical modeling at the mid‐reaches of the Gironde Estuary (France). Nonlinear mechanisms responsible for overtide generation and hence subtidal flows were found to vary across the estuary and from neap to spring tides. Subtidal flows were driven by a combination of internal asymmetry, tidal advective accelerations, nonlinear effects of water level variations, quadratic friction, and river discharge. The quarter‐diurnal overtide band (D4) in the flow was generated by internal asymmetry and tidal advective accelerations during neap tide. The ratio of quarter‐diurnal to squared semidiurnal bands (D4/D22) was largest (>0.3) in sections of the channel showing subtidal outflow. River discharge increased from neap to spring tides causing a subsequent increase of seaward subtidal currents. During spring tide, D4 was generated by tidal advective accelerations and quadratic friction combined with river discharge, rather than by internal asymmetry. The sixth‐diurnal overtide (D6) in the flow was comparable to D4 for both neap and spring tides. Largest D6/D23 ratios were found in the shallowest cross‐channel locations during both neap and spring tides.
“…Various methods are available to estimate the discharge curve [9][10][11][12]. Since a continuous measurement of stream stage was obtained using the electronically recording level loggers, another method was available to obtain an estimate of the discharge curve.…”
Section: Refinements To the Stream Flow Discharge Curvementioning
The effluent discharge from wastewater treatment plants can permeate through the ground and become a major source of contaminant to ecosystems and water bodies. These toxic contaminants can transport and find a way to the ocean via underground streams harming the aquatic life and promoting algal blooms. This paper presents meteorological and hydrological data collection and analysis to better understand the characteristics of the effluent discharge from the wastewater treatment plant and receiving water in Toguan watershed on the Island of Guam so as to support future regulatory discussions regarding modification of permit conditions and/or water quality standards to achieve compliance. Hydrological data such as rainfall, turbidity and stream level were collected over a period of two years. Crossflow measurements for two stations, one downstream, the other upstream of the effluent discharge point were collected biweekly , except at times of very low flow or dangerously high storm runoff in the stream. To better understand the behavior of the Toguan River sub-watersheds, aerial photos were taken from a single-engine Cessna aircraft. By analyzing the collected hydrological data, the relationships among the stream level, volume discharge and rainfall, were developed. The manually collected crossflow data allowed for the calculation of a rating curve for the Toguan River. This effort was somewhat hampered by prolonged drought conditions during roughly half of the period of data collection that severely limited the amount of crossflow measurements taken at high stage heights. The continuous measurement of stream level and rainfall allowed for a more comprehensive analysis of the relationship between the stage height and rainfall. Finally, a complimentary stream stage height short-term prediction scheme was developed using a routing model, and refinements to the stream flow discharge curve using a simple model for open channel flow is also presented. A further benefit of the study was the establishment of a baseline for the hydrologic conditions of the Toguan watershed which can be used to assess changes related to any future improvements to the wastewater treatment plant operations or other significant developments within this watershed.
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