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Evaluating the Hydrologic Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA

Atkins Engineering SNC-Lavalin, Raleigh, NC 27609, USA
Department of Food, Agricultural, and Biological Engineering, Ohio State University, Columbus, OH 43210, USA
Department of Biological and Agricultural Engineering, North Carolina State University, Raleigh, NC 27695, USA
North Carolina Department of Transportation, Raleigh, NC 27610, USA
AECOM, Morrisville, NC 27560, USA
Department of Coastal and Marine Systems Science, Coastal Carolina University, Conway, SC 29528, USA
Author to whom correspondence should be addressed.
Water 2019, 11(6), 1291;
Received: 6 May 2019 / Revised: 9 June 2019 / Accepted: 17 June 2019 / Published: 20 June 2019


Bioswales are a promising stormwater control measure (SCM) for roadway runoff management, but few studies have assessed performance on a field scale. A bioswale is a vegetated channel with underlying engineered media and a perforated underdrain to promote improved hydrologic and water quality treatment. A bioswale with a rip-rap lined forebay was constructed along state highway NC 211 in Bolivia, North Carolina, USA, and monitored for 12 months. Thirty-seven of the 39 monitored rain events exfiltrated into underlying soils, resulting in no appreciable overflow or underdrain volume. The bioswale completely exfiltrated a storm event of 86.1 mm. The one event to have underdrain-only flow was 4.8 mm. The largest and third-largest rainfall depth events (82.6 and 146 mm, respectively) had a large percentage (85%) of volume exfiltrated, but also had appreciable overflow and underdrain volumes exiting the bioswale, resulting in no peak flow mitigation. Overall, this bioswale design was able to capture and manage storms larger than the design storm (38 mm), showing the positive hydrologic performance that can be achieved by this bioswale. The high treatment capabilities were likely due to the high infiltration rate of the media and the underlying soil, longer forebay underlain with media, gravel detention layer with an underdrain, and shallow slope.

1. Introduction

The United Nations predicts that by 2050, 66% of the world’s population will be living in urban areas [1]. This increase in urban population will cause an increase in impervious cover resulting from urban sprawl. An increase in impervious cover can have detrimental environmental effects [2,3,4,5,6]. Changes in land cover likely alter storm hydrographs, resulting in increased runoff volumes, peak flows, and a decreased time to peak flow [7,8,9], causing an increased occurrence of flooding [10]. The continued urbanization and consequent negative hydrologic impacts highlight the need for stormwater control measures.
Low impact development (LID) is a design philosophy to manage stormwater near its source [11]. The overarching goal of LID is to develop land in such a way that the developed land’s hydrologic condition mimics those of pre-development conditions as closely as possible [12,13]. Stormwater control measures (SCMs) are employed to achieve LID principles through practices that convey, infiltrate, and treat runoff [14,15].
One commonly installed SCM is a bioretention cell (BRC), which is a sand-based practice amended with fractions of silt and clay (fines) and organic matter [16]. Hydrologically, the high sand content supports a high infiltration rate that serves to reduce runoff volume and control outflow peak flows [16]. Previous bioretention studies have reported 24–99% peak flow rate reductions [17,18,19,20,21,22,23] and 20–98% volume reduction [20,24,25].
Another common SCM is a dry swale, which is a vegetated channel for stormwater conveyance [26,27]. Dry swales have reported mean volume reduction from 11 to 75% [13,15,28,29,30,31,32,33]. Swale peak flow rate reductions have been reported from 10 to 74%, with detention provided by infiltration or check dams improving this mitigation [31,34,35].
A bioswale combines the conveyance of a dry swale with the infiltration capabilities of bioretention media [36]. The grassed surface conveys stormwater runoff and can reduce runoff rates due to vegetation roughness [37]. Beneath the vegetation is an engineered soil media, generally with a high sand content to promote infiltration and benefit volume and peak flow rate mitigation [38]. A bioswale generally employs a perforated underdrain below the media. While the performance of swales and bioretention cells has been relatively well studied, there is a lack of data on the performance of bioswales. Initial research on bioswales has demonstrated the potential for stormwater runoff volume reduction [39,40,41]. This research implemented a bioswale in the Coastal Plains of North Carolina and monitored the hydrologic capabilities for a range of rainfall depths when placed over sandy soil.

2. Materials and Methods

2.1. Site Descritption

2.1.1. Watershed Characteristics

The studied bioswale was built in Brunswick County in Bolivia, North Carolina (NC), USA (34°0′16.2972” N, 78°15′38.7792” W). Runoff from this location drains into the Lockwoods Folly River. The Lockwoods Folly River is on the USEPA 303(d) list of impaired waters because of fecal coliform [42]. Brunswick County was reported as the 31st fastest-growing county in the United States from 2010 to 2016 [43].
The bioswale was installed in a right-of-way along state highway NC 211, near the US 17 intersection. NC 211 is a two-lane road with good condition asphalt wearing course. The catchment drainage area was 0.74 ha, with 44% impervious cover. Pervious cover was existing grassed shoulders, which had a 4:1 horizontal distance:vertical distance (H:V) slope with good condition vegetation and underlying sandy soils. Stormwater runoff from the lane adjacent to the bioswale discharged onto the grassed shoulder, which could allow for initial infiltration. Runoff then flowed into the rip-rap lined forebay and bioswale (Figure 1).

2.1.2. Bioswale Design

The bioswale SCM included a 10.7 m, Class A rip-rap (5.1 to 15.2 cm diameter stone [44]) lined forebay draining into the bioswale. The bioswale had a total length of 42 m, width of 1.2 m, and depth of 0.9 m. The initial 23.8 m of the bioswale trench and its trapezoidal base were filled with high-flow media (Figure 2). The remaining trench base was filled with 0.3 m of ASTM standard #57 washed stone (2.3 to 38 mm stone size [45]), designed to serve as detention through internal water storage, which studies have shown to improve runoff reduction within BRCs through the promotion of inter-event exfiltration [35,46]. An 18 m long perforated underdrain (0.2 m diameter) was placed in the middle of this stone layer. A 5 cm choking layer of pea gravel covered with a fiberglass mesh screen was used to ensure that no media mobilized to the underdrain. The remaining 0.45 m of trench depth was filled with high-flow media (Table 1) and covered with a thin-cut centipede (Eremochloa ophiuroides) sod. The surface of the bioswale was a triangular in shape with 4:1 H:V side slopes (Figure 3 and Table 2). Previously published research on the water quality performance of this bioswale includes a full description of the bioswale construction and additional profiles [47].
The total bioswale storage was 36.9 m3, with 22.7 m3 of media porosity storage and 14.2 m3 of surface storage. These calculations are conservative since they assume no water is leaving the SCM by exfiltration during a storm event. This calculation is similar to that of the bioretention abstraction volume (BAV) originally postulated by Davis et al. (2012b) [32]. The bioswale’s overflow and underdrain flows were discharged into the existing outlet drain structure (Figure 4). The upslope chamber of the outlet structure held the underdrain monitoring equipment, while the downslope chamber had overflow monitoring equipment to prevent mixing of the two outflow sources for monitoring purposes (Figure 3 and Figure 4). A watertight wooden structure was built over the underdrain monitoring vault, creating a de facto 0.15 m tall check dam for surface storage in the bioswale.

2.2. Hydrologic Data Collection

An on-site tipping-bucket rain gauge continuously recorded rainfall, with readings taken at 2 minute intervals. The inlet peak flow rate was calculated based on measured rainfall intensity, using the rational method [48] (Equation (1)):
Q = k C i A
where Q is the peak flow rate (L s−1), k is the English to metric units conversion (0.00278), C is the composite runoff coefficient, i is the 5 minute peak rainfall intensity (mm h−1), and A is the drainage area (ha). Based on site characteristics, a composite runoff coefficient of 0.486 was obtained using C = 0.95 for asphalt (0.32 ha) and C = 0.125 for grass on a sandy soil with average slope (0.42 ha).
The inflow volume was calculated using the discrete curve number method [48] (Equation (2)):
Q * = ( P 0.2 S ) 2 ( P + 0.8 S ) ;   S = 1000 C N 10
where Q* is the runoff depth (mm), P is the rainfall depth (mm), S is the maximum retention after rainfall begins (mm), and CN is the curve number. Q* and the corresponding runoff volume were calculated separately for each land use (pervious and impervious) and combined to obtain the total storm runoff for each event. Curve numbers of 39 and 98 were used for the pervious areas and impervious road, respectively.
The underdrain and overflow monitoring structures included purpose-built weirs. Each weir had a HOBO U20 [49] pressure transducer to monitor the flow depth over the weir plate (Figure 5), which was then utilized to calculate the overflow and underdrain volumes and flow rates. Since the transducers were non-vented, another U20 logger was installed by the rain gauge to measure on-site atmospheric pressure. All measurements were taken on at 2 min intervals. The pressures at each monitoring point were offset by atmospheric pressure to determine flow depth. HOBOware [49] was used to convert the pressure to a corresponding flow depth, which was then used to calculate flow rates and volumes using the same equations as Teledyne ISCO samplers (Equations (3)–(5)).
The flow depth over each corresponding weir was calculated to a flow rate using the following equations for underdrain flow (60° V-notch, Equation (3)) and overflow (90° V-notch, Equation (4)):
Q = 796.7 × H 2.5
Q = 1380 × H 2.5
where Q is the flow rate in L s−1 and H is the flow depth in m.
The volume passing over each weir was determined using the flow rate data and the measurement interval of 2 min (Equation (5)).
V = Q × t
where V is the corresponding volume (L), Q is the corresponding flow rate (L s−1), and t is the time step of the 120 s (2 min) measurement interval. The total volume was the summation of the individual 2 minute steps across the underdrain flow and overflow durations.
A small, 0.9 m depth well, the same depth of the bioswale, was installed just downstream of the forebay, before the start of the underdrain. A HOBO U20 transducer was used to measure the stage of water within the bioswale media and to monitor the rate of water recession after storms (i.e., the drawdown rate) due to exfiltration.
Monitoring data (rainfall and runoff hydrology) were collected over a 1 year period (25 February 2014 through 26 February 2015).

2.3. Data Analysis

A rain gauge was used to determine total rainfall depth. Individual storms had an antecedent dry period (ADP) of 6 hours or greater. Once separated into individual events, 5 minute peak rainfall intensity, rainfall duration, and ADP were determined for each of the 71 observed rainfall events over the 1 year monitoring period. Rainfall depth totaled 1085 mm during this time, well below the 1547 mm annual average precipitation from 1971 to 2000 recorded in Wilmington, NC, located 43 km away [50]. However, roughly one-half of the studied year (177 days) did not have complete rainfall data due to equipment failures.
Hydrologic data from the underdrain and overflow bubbler modules were analyzed for the presence (or absence) and quantity of flow during each storm event. Detectable flow was initiated when the water level exceeded the invert of the weir. Thus, rainfall depth could be related to the size of the storm that (1) generated detectable underdrain flow and/or (2) generated detectable overflow to occur. Of the 71 storms with inflow data, 39 events had paired HOBO underdrain and overflow data.
Using the HOBO data, the following were calculated: total inlet volume, overflow volume, underdrain volume, inlet peak flow rate, overflow peak flow rate, underdrain peak flow rate, percent of inlet volume exfiltrated, and peak flow rate reductions. The exfiltrated volume, the difference between the inflow volume and the total outflow (overflow plus underdrain) (Equation (6)), represents the water which left the bioswale network into the in situ soil, assuming no loss via evaporation over the observational timescale.
V e x f i l t r a t e d = V i n f l o w V o v e r f l o w V u n d e r d r a i n .
Peak flow rate reductions were calculated using Equation (7):
P e a k   f l o w   r a t e   r e d u c t i o n = ( I n l e t   p e a k   f l o w   r a t e O u t f l o w   p e a k   f l o w   r a t e I n l e t   p e a k   f l o w   r a t e ) × 100 % .
Wilcoxon signed rank non-parametric tests were utilized to determine if either the peak flow rate reductions or the percent of inflow exfiltrated to the underlying soil were statistically significant. All statistical analyses were completed using R software (v. 3.4.3, R Core Team, 2013) using a 95% significant criterion (α = 0.05).

2.4. Analysis for Bioswale Degradation

Over time, a bioswale has the potential for clogging due to sediment build-up, which can decrease its infiltration rate and hydrologic function. The ratio of overflow volume to underdrain volume was calculated for each storm event as a potential measure of degradation. A Kendall’s tau non-parametric test was utilized to compare the storm event number to the ratio. If surface clogging occurred, it was hypothesized that the ratio would increase with time.

3. Results and Discussion

3.1. Storm Event Characteristics

Thirty-nine storm events were analyzed for appreciable overflow and/or underdrain volumes (Table 3). Thirty-six events (>92% of events) were completely infiltrated, meaning they did not have appreciable overflow or underdrain volume. The volume from these events passed through the high-flow media and fabric, exfiltrating into the sandy underlying soils. The median storm size for completely infiltrated events was 5.6 mm of rainfall (range: 1–86.1 mm). The overflow or underdrain volume was considered to be appreciable if it was equal to or greater than 1% of the total inflow volume and greater than 0.25 watershed mm of rainfall to eliminate “incidental” outflows. Three events had appreciable underdrain volume. The median depth for these events was 82.6 mm (range: 4.8–146 mm). Of these three events, one had underdrain-only flow, leaving two events with appreciable underdrain and overflow. The one event with underdrain-only was 4.8 mm. The median storm size for the two events with appreciable outflow was 114 mm (range: 82.6–146 mm).
Based on the watershed characteristics and the bioswale design, the system could be expected to capture and treat up to a 13.7 mm storm [48]. This depth is representative of a storm that fills the surface storage and fully utilizes the porosity of the media. All events within this rainfall depth were captured by the bioswale, with only one having appreciable underdrain volume (Table 3), showing that the design completely captured design storms, as well as exfiltrating much larger events (up to 86.1 mm). While this large storm of 86.1 mm is much greater than the expected capture volume, precipitation from this event occurred for an extended duration (19 hours), allowing the runoff time to infiltrate the media and exfiltrate to the underlying soil.
Of the 39 storm events, peak flow mitigation occurred for 37 events (Table 4). For the largest and third-largest events (82.6 and 146 mm), no peak flow mitigation occurred. These are the same two events reported in Table 3 as having overflow. The smaller event was 82.6 mm with a peak intensity of 93 mm h−1, duration of 19.3 h, and ADP of 3.76 days. The larger event was 146 mm with a peak intensity of 120 mm h−1, duration of 34.1 h, and ADP of 0.84 days.
A statistically significant (α = 0.05) exfiltrated volume was reported only for the category containing all inflow events (Table 5). All other categories had large percentages of exfiltrated volumes, but due to the small sample size, statistics were not conducted.
Graphical analysis of the distribution of overflow, underdrain, and exfiltrated water supports that the majority of volume mitigation occurred through exfiltration (Figure 6). While overflow composed over one-half of outflow for the overflow events and underdrain flow was appreciable for three events, this volume was noticeably lower than the cumulative rainfall and exfiltration. In total, 99% of inflow was filtered by the soil media, providing water quality treatment [47].
The six storms with the highest 5 minute rainfall intensities recorded ranged from 73.2 to 120.4 mm h−1, with two events having an intensity of 73.2 mm h−1 (Table 6). Of these six events, only the highest and fourth-highest intensity events resulted in appreciable outflow volume, both overflow and underdrain, with just over one-half of the outflow leaving as overflow. These two events had no peak flow reduction from the overflow, underdrain, or combined outflow. The other four high-intensity events completely exfiltrated all inflow volume.
The five storms with the largest rainfall depths ranged from 146 mm to 48.3 mm (Table 7). Only two of these events had appreciable outflow, with more than one-half leaving as overflow. These two events (events 6 and 60) were the same two high-intensity events that resulted in outflow. The two events with overflow were the only events to occur in both the highest rainfall depths and intensities. While these events exfiltrated a large percentage of volume, as noted, neither decreased peak flows. This could be caused by the bioswale being fully saturated, resulting in ponding on the surface and any additional overflow volume not being subject to flow mitigation from the vegetation [51].
This bioswale was able to completely infiltrate four of the six highest intensity events and three of the five largest rainfall depth events. While the exact in situ soil infiltration rate was not determined, these results show the positive volume and flow rate mitigation capabilities of this bioswale. Volume mitigation is likely due to several design features including the high infiltration rate of the media and the underlying sandy soil. The plunge pool was underlain with the high-flow media, allowing all ponded water to infiltrate the bioswale. The underdrain was only present in the second half of the bioswale, allowing for more media volume for storage, infiltration, and increased base surface area for exfiltration. The bioswale had a shallow slope (0.5%), likely decreasing the overflow rate and increasing hydraulic retention time for increased infiltration. The gravel layer below the underdrain allowed for the conveyance of infiltrated volume out of the bioswale, aiding in outflow volume mitigation. Additionally, the 0.05 m gravel layer below the underdrain provided detention for inter-event exfiltration.

3.2. Internal Water Level

Monitoring well data were utilized to determine several characteristics including the maximum stage of water in the bioswale during a storm and the resulting drawdown rate. Kendall’s tau tests were run to determine any statistically significant interactions in relation to the internal water level in the bioswale. Positive associations were found between rainfall depth and the following: maximum stage of ponded water in the bioswale, length of time to the peak well stage, and internal water drawdown rate.
Analysis of the peak internal water level compared to rain depth showed that the interval water level plateaued around 1.07 m (Figure 7). The average depth of the bioswale was 0.9 m. Thus, a depth within the well greater than 0.9 m equated to ponding along the bioswale surface. There were several events (n = 12) of ponding on the bioswale surface and complete saturation of the media. The smallest rainfall depth to result in surface ponding was 11.4 mm. The monitoring well was near the upstream end of the bioswale, so ponding at this location was not always representative of overflow, as runoff infiltrates along the bioswale length. Additionally, there was a de facto check dam at the end of the bioswale, allowing for surface ponding. Only two instances of ponding resulted in appreciable overflow, because surface ponding exceeded the storage volume and infiltration capacity. The average drawdown rate was approximately 0.04 ft min−1.

4. Conclusions

The bioswale had positive volumetric and flow rate mitigation for the 39 events during the 12 month study period (February 2014–February 2015). The bioswale eliminated overflow from 37 of these 39 storm events, including an event of 86.1 mm. Events with significant overflow were the largest and third-largest rainfall depth events with depths of 146 mm and 82.6 mm, respectively. Statistical analysis did not show significant decreases in infiltration capabilities of the bioswale over time. Thus, within this study period there was likely little clogging or degradation of the system. Based on the storage available in the media and on the bioswale surface, a storm up to 13.7 mm could be expected to be fully stored by the bioswale. The bioswale was able to exfiltrate storms much larger than this design event. For example, the 86.1 mm event was likely able to achieve full exfiltration due to the long rainfall duration of 19 hours, where intra-event exfiltration into the sandy underlying soil was key.
Monitoring of the internal water level highlighted that ponding occurred on the bioswale surface for the majority of events, with the ponded volume completely infiltrating along the bioswale length for all but two events. This highlighted the capabilities of the bioswale to achieve a high percentage of exfiltrated volume, even in cases where the media was fully saturated and had surface ponding.
This bioswale nearly eliminated outflow volume and had exemplary peak flow mitigation. While this is only one bioswale, this research highlights that bioswale design and function should continue to be examined to allow for the creation of optimal design standards for enhanced hydrologic mitigation. Several design features contributed to positive hydrologic treatment. The high infiltration rate of the media and underlying soil, longer forebay underlain with high-flow media, gravel detention layer with an underdrain in the second half of the bioswale length, and shallow slope allowed large events to be completely captured by the bioswale.

Author Contributions

Author contributions are as follows: conceptualization, M.S.L., A.D., R.J.W., B.L., and W.F.H.; methodology, M.S.L., A.D., R.J.W., B.L., and W.F.H.; software, R.A.P.; validation, R.A.P.; formal analysis, R.A.P.; investigation, R.J.W. and R.A.P.; resources, M.S.L., A.D., R.J.W., B.L., W.F.H., and S.L.; data curation, R.A.P.; writing—original draft preparation, R.A.P.; writing—review and editing, W.F.H., R.J.W., M.S.L., A.D., B.L., K.N., and S.L.; visualization, R.A.P.; supervision, W.F.H.; project administration, M.S.L., A.D., and B.L.; funding acquisition, M.S.L., A.D., and B.L.


This research was funded by the North Carolina Department of Transportation (NCDOT), Grant 2016-18, and the National Science Foundation (NSF), Grant DGE-1252376.


Field equipment installation was performed by Shawn Kennedy (NCSU BAE) and field data collection was performed by Jeff Barley (CCU’s Environmental Quality Lab).

Conflicts of Interest

The authors declare no conflict of interest. The sponsors of the project paid for the design and construction of the bioswale. The sponsors also reviewed the manuscript prior to submission, but otherwise had no function in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.


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Figure 1. Watershed, grassed shoulder, and rip-rap channel and forebay [47].
Figure 1. Watershed, grassed shoulder, and rip-rap channel and forebay [47].
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Figure 2. Horizontal cross-section of the first 23.8 m of the bioswale.
Figure 2. Horizontal cross-section of the first 23.8 m of the bioswale.
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Figure 3. Bioswale longitudinal cross-section [47].
Figure 3. Bioswale longitudinal cross-section [47].
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Figure 4. Outlet structure with closed portion for underdrain flow [47].
Figure 4. Outlet structure with closed portion for underdrain flow [47].
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Figure 5. Underdrain outlet weir and associated HOBO logger [47].
Figure 5. Underdrain outlet weir and associated HOBO logger [47].
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Figure 6. Distribution of rainfall into overflow, underdrain, and exfiltration.
Figure 6. Distribution of rainfall into overflow, underdrain, and exfiltration.
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Figure 7. Positive association (α = 0.05) between the rainfall depth and the peak bioswale internal water level. Events above the black line (surface) represent surface ponding.
Figure 7. Positive association (α = 0.05) between the rainfall depth and the peak bioswale internal water level. Events above the black line (surface) represent surface ponding.
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Table 1. High-flow media characteristics.
Table 1. High-flow media characteristics.
Hydraulic conductivity (Ksat)2540 mm h−1
Moisture content30–50%
Passing 2.0 mm sieve95–100%
Passing 1.0 mm sieve>80%
Sand—very coarse40–45%
Table 2. Bioswale design characteristics [47].
Table 2. Bioswale design characteristics [47].
Rip-rap channel length6 m
Rip-rap channel slope3%
Plunge pool length4.7 m
Plunge pool depth0.15 m
Underdrain length18.3 m
Underdrain diameter0.2 m
Media depth0.45–0.9 m
Total length42 m
Surface geometryTriangular
Surface side slopes4:1
Media void storage22.7 m3
Surface storage14.2 m3
Table 3. Fate of inflow based on HOBO data.
Table 3. Fate of inflow based on HOBO data.
Event TypeNumber of EventsMedian
Inflow a395.617.80.76–146
Completely infiltrated365.612.71.0–86.1
Underdrain-only flow14.84.84.8
a—Inflow events with complete HOBO monitoring equipment data for all monitoring points (inflow, overflow, underdrain).
Table 4. Mean volume and flow for each storm event scenario.
Table 4. Mean volume and flow for each storm event scenario.
Event TypeInlet
Peak Flow Rate
(L s−1)
Total Inlet Volume (L)Overflow Peak Flow
(L s−1)
Total Overflow Volume (L)Underdrain Peak Flow
(L s−1)
Total Underdrain Volume
Overflow Peak Flow Rate Reduction
Underdrain Peak Flow Rate Reduction
All inflow events
(n = 39)
Completely infiltrated
(n = 36)
Underdrain-only flow
(n = 1)
(n = 2)
* NA—not applicable; NR—no reduction.
Table 5. Mean fate of inflow volume and outlet volume of the 39 events.
Table 5. Mean fate of inflow volume and outlet volume of the 39 events.
Event TypeOutflow VolumeInflow Volume Exfiltrated
Underdrain (%)
All inflow events (n = 39)188299
Completely infiltrated (n = 36)00100
Underdrain-only flow (n = 1)010099
Overflow (n = 2)584285
Table 6. Hydrologic performance of the largest peak 5 minute rainfall intensity events.
Table 6. Hydrologic performance of the largest peak 5 minute rainfall intensity events.
EventPeak 5 min Intensity (mm/h)Rainfall Depth
Rainfall Duration
Antecedent Dry Period (ADP)
Over of Outflow
Under of Outflow
% ExfiltratedOverflow Peak Flow Rate Reduction
Underdrain Peak Flow Rate Reduction
Combined Peak Flow Rate Reduction
* Intensities for comparison: 1 year-5 min event = 159 mm h−1; 1 year-24 h = 4 mm h−1.
Table 7. Hydrologic performance of largest overall rainfall depth events.
Table 7. Hydrologic performance of largest overall rainfall depth events.
EventRainfall Depth (mm)Peak 5 min Intensity
Rainfall Duration (h)ADP
Over of Outflow
Under of
% ExfiltratedOverflow Peak Flow Rate Reduction
Underdrain Peak Flow Rate Reduction
Combined Peak Flow Rate Reduction
* Intensities for comparison: 1 year-5 min event = 159 mm h−1; 1 year-24 h = 4 mm h−1.

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Purvis, R.A.; Winston, R.J.; Hunt, W.F.; Lipscomb, B.; Narayanaswamy, K.; McDaniel, A.; Lauffer, M.S.; Libes, S. Evaluating the Hydrologic Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA. Water 2019, 11, 1291.

AMA Style

Purvis RA, Winston RJ, Hunt WF, Lipscomb B, Narayanaswamy K, McDaniel A, Lauffer MS, Libes S. Evaluating the Hydrologic Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA. Water. 2019; 11(6):1291.

Chicago/Turabian Style

Purvis, Rebecca A., Ryan J. Winston, William F. Hunt, Brian Lipscomb, Karthik Narayanaswamy, Andrew McDaniel, Matthew S. Lauffer, and Susan Libes. 2019. "Evaluating the Hydrologic Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA" Water 11, no. 6: 1291.

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