Evaluation of Publicly Maintained Bioretention Facilities
Transcript of Evaluation of Publicly Maintained Bioretention Facilities
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A Fairfax County, VA, publication
Prepared for:The Department of Public Works and Environmental Services,
Maintenance and Stormwater Management Division ByThe Northern Virginia Soil &Water Conservation District
Evaluation of Publicly Maintained Bioretention Facilities
Does good maintenance guarantee optimum performance?
Phase I and II studies
April, 2017
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Facts:• In Fairfax County there are close to 130 publicly and 550 privately
maintained bioretention facilities
• Currently 80%-90% of infill lots and 50%-60% of SP and SD plans include bioretention as their main SWM practice
• Bioretention facilities are a widely used and accepted BMP.
Questions:• What if the newly commissioned facilities are not performing as
expected?
• Do we have the right tools to determine the inadequate performance?
• What are the main reasons for inadequate performance?
• Can the current inspection and maintenance guidelines detect these inadequacies?
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Main purpose of this study:
To develop protocols to assess the structural and nonstructural elements that determine the performance of a bioretention facility early in its lifespan.
With the goal of:
Using the findings to create design and construction recommendations that, if implemented, may decrease the frequency and costs of routine maintenance, partial facility repairs and full rehabilitation.
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Inventory of Facilities Evaluated
Evaluation Phase
No. of Facilities Year evaluated Facility Age
Phase I 63 2014 2000-2009
Phase II 27 2015 2010-2014
Phase III 40 2016 2015-2016
• All are publicly maintained (Fairfax County DPWES maintains them)• All built in compliance with SWM requirements for a new development
or redevelopment or in compliance with the County’s MS4 obligations
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The Process
1. Developing an evaluation protocol:
2. Performing the physical surveyI. Ponding area
II. Soil media
1. Infiltration rate
2. Media particle size distribution (sand, silt, clay)
3. Soil media depth
III. Surface area (footprint)
IV. Structural components of the facility
3. Performing plants survey
4. Findings, conclusions, and recommendations
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Evaluation Protocol
Standard Operating Procedures (SOP)STANDARD OPERATING PROCEDURES
FORBIORETENTION EVALUATION
PREPARED FOR:FAIRFAX COUNTY DEPARTMENT OF
PUBLIC WORKS AND ENVIRONMENTAL SERVICES
MAINTENANCE AND STORMWATER MANAGEMENT DIVISION
BY:NORTHERN VIRGINIA SOIL & WATER
CONSERVATION DISTRICT
February 2015
TABLE OF CONTENTSPurpose and ApplicabilitySummary of MethodsDefinitionsHealth and Safety PrecautionsPersonnel QualificationsEquipment and SuppliesProcedural StepsData and Records ManagementAttachmentsAttachment 1: Evaluation FormAttachment 2: Evaluation Tool KitAttachment 3: Infiltration Rate MeasurementAttachment 4: Ponding Area Topographic SurveyAttachment 5: Soil SamplingAttachment 6: Plants SurveyAttachment 7: Typical cross section of a bioretention facility
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Evaluation Protocol
Evaluation Survey Form
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Surface Area (s.ft.) Ponding Depth (ft.)% of original ponding vol.
Soil Media Depth (ft.) Soil Media Composition (%)
Design Actual % Missing Points Design Actual Ave, D Missing % Missing Depth Points Design Actual Ave, D Missing Points Depth 1 Depth 2
. sand silt clay sand silt clay
927.0 730.0 21.3 3.0 1.0 1.9 0.0 0.0 2.5 3.0 0.0 86.0 10.0 4.0
842.0 738.0 12.4 2.0 1.0 1.5 0.0 0.0 2.5 2.6 0.0 80.0 16.0 4.0
BR ID District Age of Facility (Yr.) Inventory Date Date Visited Address City, State, Zip Location Name
BR0299 Braddock 3.64109589 12/17/2010 06/30/14 7825 Heritage Dr Annandale, VA 22003 BRADDOCK ELEMENTARY SCHOOL - 10 CLASSROOM MODULAR ADDITION
BR0300 Braddock 3.64109589 12/17/2010 06/30/14 7825 Heritage Dr Annandale, VA 22003 BRADDOCK ELEMENTARY SCHOOL - 10 CLASSROOM MODULAR ADDITION
Standing water
Cleanout pipeNeed for repair
ErosionTotal
PointsInflow outflow (overflow)
Cleanout pipe
channel sheet pipe Inlet Berm DAslope
s
1.0slope erosion on sides 4.0
2.0
1.0 1.0scouring at open channel 7.0
1.0 1.0See the attached comments 7.0
Evaluation Protocol
Data Organization and Access
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Repair priority rating criteria1345BR
Evaluation Design Actual Missing Points
Ponding depth 0.5 ft. 0.1 ft. 80% 7.5
Infiltration rate 8.0 in/hour 24.0 in/hour - 2
Structural damage 2
Total Points 11.5
Evaluation Protocol
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Physical Survey
• Ponding area
• Soil media
• Soil media depth
• Infiltration rate
• Media particle size distribution (sand, silt, clay)
• Surface area (footprint)
• Structural components of the facility
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Topographic survey of the ponding area
Physical Survey
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Soil media infiltration rate
Date: 07/20/2014
Number of Measurements 4
# Time (min)intervals
(min)Readings (ft)
Rate (in/hour)
1 0 5 0.44 02 5 5 0.42 2.883 10 5 0.38 5.764 15 5 0.32 8.64
I Rate (in/hour) 5.76
% sand 82
% silt 12
% clay 6
%org. matter 2.4Textural Class loamy sand
Physical Survey
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% sand 82
% silt 12
% clay 6
%org. matter 2.4
Textural Class loamy sand
Physical Survey
Soil media depth & particle size
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Physical Survey
Structural Survey
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Survey existing plant population with the intention of finding:• The survival rate of the original
plantings
• Plant species that survived best
• Dominant voluntary plants(weeds, perennials, shrubs,and trees)
Plants Survey
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Compliance with the original design
Ponding depth
% of TotalMissing Ponding
Depth
33% None20% <25%20% 25%-50%13% 50%-75%14% >75%
Findings
Phase I67% of evaluated facilities did not
comply with the original design
Phase II56% of evaluated facilities did not
comply with the original design
% of TotalMissing Ponding
Depth
44% None37% <25%11% 25%-50%4% 50%-75%4% >75%
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Compliance with the original design
Soil media depth
% of TotalMissing Soil Media
Depth
41% None11% <0.5 ft.24% 0.5-1.0 ft.17% 1.0-1.5 ft.8% 1.5-2.0 ft.
Findings
Phase I59% of bioretention did not
comply with design soil media depth
Phase II52% of evaluated facilities did not
comply with the original design
% of TotalMissing Soil Media
Depth
48% None
15% <0.5 ft.
19% 0.5-1.0 ft.
3% 1.0-1.5 ft.
15% 1.5-2.0 ft.
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Compliance with the original designInfiltration rate
* 0.5 in/hour is the minimum acceptable saturated hydraulic conductivity (VA SWM BMP Clearing House)
8.0 in/hour Maximum infiltration rate (Bill Hunt, NC State University, personal communication). 24 facilities comply
Number of Facilities
Rate (inches/hour)
5% (3) <0.5*
40% (27) 0.5-8
15% (9) 8-12
22% (13) 12-20
8% (5) 20-30
10% (6) >30
Findings
Phase I Evaluation Study Phase II Evaluation Study
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Compliance with the original design
Soil media particle size analysis (Phase I)
* Compost
Particle Type MeasurementsVA SWM BMP
Clearing HousePFM
VA SWM Handbook (1999)
Sand 36% to 96 % 85% - 90% 60%-75% 50%
Silt + Clay 2% to 42 % <20% -
Clay 2% to 25% <10% <8% <5%Organic matter 0.5%-22.6% 3%-5% 5%-15%* 20%*
Findings
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Compliance with the original design
Soil media particle size analysis
y = 0.0575x + 9.4158R² = 0.0023
0.0
10.0
20.0
30.0
40.0
50.0
60.0
70.0
80.0
20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0
Sand (%)
Infi
ltra
tio
n R
ate
(in
/ho
ur)
Findings
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y = -0.2618x + 15.941R² = 0.0092
0.0
10.0
20.0
30.0
40.0
50.0
60.0
70.0
80.0
0.0 5.0 10.0 15.0 20.0 25.0 30.0
Infi
ltra
tio
n R
ate
(in
/ho
ur)
Clay (%)
Findings
Compliance with the original design
Soil media particle size analysis
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Compliance with the original design
Soil media particle size analysis (Phase II)
Particle TypeVA SWM BMP
Clearing HousePFM
VA SWM Handbook (1999)
Sand 91.0% 8.8% 0.0%
Clay 91.0% 87.0% 34.0%
Findings
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Findings
Compliance with the original designSoil media particle size analysis
0.0
5.0
10.0
15.0
20.0
25.0
30.0
50.0 60.0 70.0 80.0 90.0 100.0
Infi
ltra
tio
n r
ate
(in
ch/h
ou
r)
Sand content (%)
Infiltration rate/soil media sand content (Phase II)
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Findings
Compliance with the original designSoil media particle size analysis
0.0
5.0
10.0
15.0
20.0
25.0
30.0
0.0 2.5 5.0 7.5 10.0 12.5 15.0 17.5 20.0
Infi
ltra
tio
n r
ate
(in
ch/h
ou
r)
Clay content (%)
Infiltration rate/soil media clay content (Phase II)
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Sand particle size distribution (ASTM-C33)
Findings
Compliance with the original designSoil media particle size analysis
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Findings
Inadequate structural type
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Findings
Damaged structural components
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Findings
The Impact of filter fabric on hydrodynamic performance
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Seepage or continuous base flow into bioretention facility might develop localized wetlands.
Findings
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Facilities that might not qualify as bioretention
Findings
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Facilities that might not qualify as bioretention
Findings
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Lack of compliance is a major construction issue:– Improvement in construction oversight
• Guidelines for construction sequencing and inspection
• Guidelines for preparing the as-built
• Trained construction inspectors
• Documentation (as-built) during construction including guidelines
– Local inspection certification program
Recommendations
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• Restoring missing ponding depth for facilities built prior to new VA SWM plan guidelines might not be required.
• Restoring the soil media depth will be complicated.– More than one foot depth loss might need to be reviewed.
– The BMP credit could be revised.
• High infiltration rate impacts BMP and runoff reduction performance (under drain).– Outflow rate could be adjusted to provide the inflow residency time.
Recommendations
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• Eliminate or divert continuous base flow into the bioretention.
• Although filter fabric did not have a negative impact on vertical flow, 6.0” of pea gravel is a preferred option.
• Within 6 months after construction is complete, survey/evaluate the facility using the SOP developed during this study, and at least every 5 years thereafter.
• Share the results with other DPWES divisions, private industry, other jurisdictions.
Recommendations