Title: Centralized Impoundments for Storage of Wastewaters
1Centralized Impoundments for Storage of
Wastewaters
2Centralized Impoundments for Storage of
Wastewaters
- Service multiple well sites
- Regulated part of the well site
- Generally large capacity (10-15 million gallons)
3Standards For Wastewater Impoundments
- Structural Standards
- Liner Systems
- Quality Assurance/Quality Control
- Leak Detection
- Action Leakage Rates
- Groundwater Monitoring
4Distance Restrictions
- In the 100-year floodplain of waters of this
Commonwealth. - In or within 100 feet of a wetland.
- Within 200 feet from an occupied dwelling
- Within 100 feet of a perennial stream.
- Within 200 feet of a private water source.
- Within 1,000 feet upgradient, and within 300 feet
downgradient, of a public water source
5Embankment Design Criteria
- Maximum Particle Size 6
- Bottom must be at least 20 above seasonal high
groundwater table - Must meet specific soil type and compaction
standards - Minimum embankment top width of 12 is required
- Minimum inside outside side slopes of 3H1V are
required - Permanent vegetative ground covering must be
established upon completion of dam construction. - 2 of lined freeboard must be maintained at all
times.
6Embankment Construction
- Soils to be used for dam embankment construction
must be classified in accordance with ASTMD-2487.
A minimum of three samples must be classified. - Soils acceptable for dam embankment construction
are limited to GC, GM, SC, SM, CL or ML. - Soils must contain a minimum of 20 of Plus No.
200 sieve materials.
7Gradation Sheet
GC- Clayey gravels GM- Silty gravels SC- Clayey
sands SM- Silty sands CL- Inorganic clays low
to medium plasticity ML- Inorganic silts
and fine sand, slight plasticity
8Site Preparation
- Foundation of dam embankment must be stripped and
grubbed to a depth of two feet prior to any
placement compaction of earthfill. - Any springs encountered in the foundation area
should be drained to the outside/downstream toe
of the embankment with a drain section two foot
by two foot in dimension consisting of PennDOT
Type A sand, compacted by hand tamper. No
geotextiles to be used around sand. The last
three feet of this drain at the
outside/downstream slope should be AASHTO 8
material. - 20 Separation must be maintained.
9Compaction
- All compaction for embankments must be done with
a sheepsfoot or pad roller. - Loose lift thickness must be 9 or less.
- A minimum of 5 passes of the compaction equipment
over the entire surface of each lift is required. - Compaction to visible non-movement of the
embankment material is required.
10Soil Placement and Compaction
11 Pad Rollers
12Embankment Top Width Minimum 12
13Take a closer look..
14Failure to properly compact movement of the
embankment material
15Failure to maintain 2 feet of lined freeboard
16Centralized Impoundment Liner Components
- Sub-base
- Geo-textile Ventilation Layer
- Secondary Liner
- Leak Detection System
- Primary Liner
17Failed liners (two separate locations)
18Failed liner
19Sub-base 6 Compacted Clay Particle Size lt0.75
1
3
Minimum Slope 3H1V
2 Slope
Leak Detection Trench
20Sub-base Requirements
- Must cover bottom and sides
- Minimum thickness of 6
- Compacted to 90 standard proctor
- Coefficient of permeability lt 1 x 10-6 cm/s
- Compaction and permeability testing must be
conducted once per 2,500 ft2 - Hard, uniform, smooth and free of debris, rock
fragments, plant materials and other foreign
material. - Free of coarse rock fragments greater than 0.75
in diameter.
21Like This
Not Like This
22Do not utilize organic matter in a subbase
23The Decomposition of organic matter produces gas
and results in the potential for the liner to
burst or rupture!
24Geotextile Fabric
2 Slope
Leak Detection Pipe Perforated, 4
Diameter Schedule 80 Minimum 2 Slope Minimum
Clean Stone
25Geotextile
- The sub-base shall be covered with non-woven
geotextile fabric to cushion the secondary liner
and allow for adequate venting between the
secondary liner and sub-base to prevent
entrapment of gases beneath the liner system.
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29Secondary Liner Geo-Synthetic Membrane Thickness
40 mil
Anchor Trench
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31Secondary Liner Requirements
- Must cover bottom and sides
- Minimum thickness of 40 mil synthetic
geo-membrane - Coefficient of permeability lt 1 x 10-7 cm/s
- Liner compatibility shall satisfy EPA Method
9090, Compatibility Test for Wastes and Membrane
Liners - Installed in accordance with QA/QC plan
32Leak Detection kgt1 x 10-2
33Leak Detection System Requirements
- Coefficient of permeability of 1.0 x 10-2 cm/sec
or greater - Uses a perforated piping system capable of
detecting and intercepting liquid within the leak
detection zone and conveying the liquid to a
collection sump. - The collection sump shall be equipped with a sump
pump with an automatic switch. - Discharge from the sump pump shall be directed
back into the impoundment or other suitable
containment. - The pump and sump shall be of sufficient size and
capacity to convey any leak that may occur
without a discharge. - The leak detection zone and sump shall be
designed to allow the operator to monitor and
record leakage rates. - The leak detection zone shall have a minimum
bottom slope of 2. - Contain non-carbonate stones or aggregate with no
sharp edges. - The operator shall monitor the leak detection
zone weekly to determine whether liquid is
flowing from the zone.
34Leak Detection Piping System Requirements
- The slope, size and spacing of the piping system
shall assure that liquids drain from the leak
detection zone. - The pipes shall be installed primarily
perpendicular to the flow and shall have a
minimum post-settlement grade of at least 2. - The minimum diameter of the perforated pipe shall
be 4 inches with a wall thickness of Schedule-80
or greater.
35Primary Liner Geo-Synthetic Membrane Thickness
40 mil
36Primary Liner Requirements
- Must cover bottom and sides
- Minimum thickness of 40 mil synthetic
geo-membrane - Coefficient of permeability lt 1 x 10-7 cm/s
- Liner compatibility shall satisfy EPA Method
9090, Compatibility Test for Wastes and Membrane
Liners - Installed in accordance with QA/QC plan
37Action Leakage Rates
Fluid Height (ft) ALR (gallons/acre/day)
h 10 340
10 lt h 15 420
15 lt h 20 490
20 lt h 25 550
25 lt h 30 610
h gt 30 case by case
Allowable leakage rates shall be determined based
upon the maximum depth of the impounded fluid as
specified in the table below. The area shall be
calculated as the area of the liner in contact
with the impounded fluid.
In the event that the flow rate of leakage
through the primary liner, as collected in the
leak detection sump, exceeds the value above for
a given fluid depth, the impoundment shall be
drained to the extent necessary and the leak or
leaks shall be located and repaired
38Groundwater Monitoring
- Minimum of 1 monitoring well located up-gradient
and 3 down-gradient - Must be within 200 feet of the impoundment and at
least 100 feet closer than the nearest drinking
water well - Quarterly monitoring for (as a minimum)
- Total dissolved solids
- Chloride
- Sulfates
- pH
- Specific conductance
39Monitoring Well Construction
- The minimum casing diameter shall be 4 inches
unless otherwise approved by the Department in
writing. - The well shall be equipped with a factory-made
screen designed to maximize open area and
minimize entrance velocities and allow rapid
sample recovery. - The well shall be filter-packed with chemically
inert clean quartz sand, silica or glass beads.
The material shall be well rounded and
dimensionally stable. - The casing shall be clearly visible and protrude
at least 1 foot above the ground. - The annular space above the sampling depth shall
be sealed to prevent contamination of samples and
the groundwater.
40Monitoring Well Casings
- Must Be of sufficient strength to protect the
well from damage by heavy equipment and
vandalism. - Must Be installed for at least the upper 10 feet
of the monitoring well, as measured from the well
cap, with a maximum stick up of 3 feet. - Be grouted and placed with a concrete collar at
least 3 feet deep to hold it firmly in position. - Be numbered for identification with a label
capable of withstanding field conditions and
painted in a highly visible color. - Have a locked cap.
- Be made of steel or another material of
equivalent strength
41Typical Monitoring Well
screen
42Engineer Certification
- Design plans for centralized impoundments must be
developed and sealed by a registered professional
engineer in Pennsylvania. - The design engineer shall provide oversight for
all aspects of construction to ensure that
construction is completed in accordance with the
design and quality assurance and quality control
plan.
43Engineer Certification
- Upon completion, a facility completion and final
certification report must be submitted to the
Department. The report must be completed and
sealed by the licensed professional engineer who
provided oversight for construction and contain
the following items - A statement that the engineer provided oversight
for all aspects of construction and that the
impoundment was constructed as designed and in
accordance with these requirements and the
quality assurance and quality control plan - Soils classification testing results for the
embankments - Soil compaction testing results for the sub-base
- As-built drawings noting any deviation from the
original plans submitted to the Department - Quarry tickets for drain material
- Quality assurance and quality control test
results - Color photographs
- The impoundment shall not be filled until the
facility completion and final certification
report is received and approved by the Department.
44Contact Information
- Joseph Adams, P.E. Environmental Engineer
- Bureau of Oil and Gas Management
- Department of Environmental ProtectionRachel
Carson State Office Building400 Market Street
Harrisburg, PA 17101Phone 717.772.2199
josepadams_at_state.pa.us