[Adopted 7-26-2018 by Ord. No. 18-10]
As used in this part, the following terms shall have the meanings
indicated:
Water obtained from a portable water source of the Commonwealth
such as a hydrant, stream, lake, water well, river, spring or other
source that has not been treated or utilized in commercial or industrial
operations.
Water in that portion of the generally recognized hydrologic
cycle which occupies the pore spaces and fractures of saturated subsurface
materials. Groundwater often supplies wells and springs and is often
withdrawn for domestic, agricultural, municipal, industrial and other
beneficial uses.
An injection well is a device which helps in placing fluids
and hazardous materials including but not limited to petroleum or
petroleum like products and brine underground in porous rock formations
like limestone and sandstone, or below in the shallow soil layer.
The fluids could be wastewater, brine, water, or water mixed with
chemicals.
A lined depression excavation pit or facility situated in
or upon the ground whether natural or artificial used to store fresh
water.
A lined depression excavation pit or facility situated in
or upon the ground, whether natural or artificial, used to store waste
water fluid including, but not limited to brine, fracturing fluid,
produced water, recycled water, impaired water, flowback water, or
any other fluid that does not satisfy the definition of "fresh water."
1.
The minimum site required shall be 10 acres.
2.
Recognizing that the specific location of equipment and facilities
is an important and integral part of oil and gas development, as part
of the planning process, the operator shall locate the temporary and
permanent operations so as to minimize interference with Borough residents,
and future Borough development activities as authorized by the Borough's
Council. Reference is made to the table below which list the minimum
offset distance from the well to the protected structure;
Setback Distances (Minimum) From Protected Structures (Feet)
Residential and Nonresidential Uses
| |
---|---|
Use
|
Setback Distance
(feet)
|
R-1
|
1,700
|
R-2
|
1,500
|
R-3
|
2,800
|
R-4
|
1,500
|
C-1
|
1,000
|
C-2
|
500
|
School
|
2,500
|
Hospital
|
2,500
|
Wetland
|
2,000
|
Gas station
|
1,500
|
Nursing home
|
1,500
|
Day care
|
1,500
|
3.
The site shall have frontage on and direct vehicular access to an
arterial or collector street.
4.
As part of the conditional use application, the applicant shall have
submitted all necessary applications for permits and plan approvals
to the PA DEP. Prior to beginning the drilling site construction,
the applicant shall submit to the Borough a copy of all permits (general
permits, well permits, joint permits, earth disturbance permit, ESCGP-1,
etc) issued by the PA DEP. In addition, the Borough shall be provided
copies of all plans (erosion and sedimentation control, grading, water
management plan, water withdrawal plan, pollution prevention contingency,
alternate waste disposal, etc.) required and approved by the PA DEP.
The Borough Engineer shall be provided with a timeline and activity
schedule and all required permits shall be maintained, commencing
at site construction and continuing throughout the duration of drilling
and production testing (hydraulic fracturing) operation. Any suspension,
or revocation of permits or other penalties by PA DEP shall be reported
to the Borough and shall constitute a violation of Borough zoning
approval and may result in the suspension of zoning approval.
5.
Adjacent public streets shall be adequate to accommodate traffic
volumes and weight limits associated with truck traffic to and from
the site.
6.
The storage, handling, transportation and disposal of hazardous or
potentially hazardous materials Including but not limited to petroleum
or petroleum like products and brine shall be in accordance with all
applicable permits and requirements of the Pennsylvania Department
of Environmental Protection (PA DEP) and the U.S. Environmental Protection
Agency (EPA).
7.
No permanent component of the injection well site shall be closer
than 100 feet from the property line in which the well is located.
8.
A risk assessment report. A report prepared by a professional expert
in that field, that identifies the potential hazards stemming from
the injection well at the proposed site and determines the quantitative
and qualitative risk associated with the identified hazards. The quantitative
risk assessment shall include calculations of two components of risk,
the magnitude of the potential loss, and the probability that the
loss will occur. The report shall include a public health risk assessment
including potential impacts to water supply. This assessment is the
process of characterizing the nature and likelihood of harmful effects
to individuals or populations within one linear mile from the well
site. The report shall also include an assessment of potential seismic
impacts created by the operations of the injection well.
9.
Predrilling, Post-hydraulic fracturing, and baseline water survey
requirements. Prior to drilling and post-hydraulic fracturing, the
operator shall be responsible for testing all existing water supplies
(surface and groundwater) within 1,000 feet of the surface location
of the well. The purpose of testing is to determine the baseline quality
of quantity of the surface water and groundwater in the immediate
vicinity of the proposed well site and to evaluate resultant changes
that may occur or have an impact on the water supply of the site and
surrounding area. If a landowner refuses to allow the operator access
to conduct a survey, the operator shall show evidence of such refusal
in accordance with Pa. Code Title 25, Chapter 78, § 78.52
(f). In addition, prior to drilling, the operator is be required to
drill a test well outside of the limits of the well pad, but no more
than 750 feet from the well location to a depth that intersects all
known or viable aquifers for the purposes of obtaining a baseline
assessment of water quality in the vicinity of the site. The test
well shall be located such that it is park of the hydrologic system
of the drill site. All testing shall adhere to the following:
A.
Predrilling testing results, both from existing water supplies and
from the operator-drilled test well, shall be submitted as part of
the conditional use application.
B.
Post-hydraulic fracturing testing shall be completed no sooner that
one month after hydraulic fracturing activities have ceased and no
later that two months after hydraulic fracturing activities have ceased.
C.
The post-hydraulic fracturing test results, both from existing water
supplies and from the operator-drilled test well, shall be submitted
to the Borough, PA DEP, and residents within 1,000 feet of the surface
location of the well in accordance with Pa. Code Title 25, Chapter
78, § 78.52 "Predrilling or prealteration survey" within
10 days of their receipt.
D.
The operator shall be responsible for all costs associated with drilling
and testing and testing shall be done by an independent state-certified
water testing laboratory agreed upon by the Borough.
E.
Water quantity test. The operator shall hire a consultant (hydrogeologist)
agreed upon by the Borough to conduct water quality testing. The consultant
shall submit a pretesting and a predrilling plan to be approved by
the Borough. The consultant shall test for gallons per minute (gpm)
flow rates, yield, groundwater levels, and other pertinent information
for all viable aquifer zones via drawdown test or other suitable means.
The consultant shall measure and record flow rates in gallons per
minute (gpm) for all surface water sources. Groundwater levels and
other pertinent information via drawdown test or other suitable means
shall be measured from all available wells. Also, GPS coordinate information
shall be recorded for all surface water and groundwater sites. The
results shall be certified by the hydrologist.
F.
Water quality test. Operators shall test for the following list of
parameters for all surface water and groundwater. The list is not
exhaustive and the Borough reserves the right to add additional parameters;
INORGANIC
| ||||
Alkalinity
|
Chloride
|
Conductivity
|
Hardness
|
Oil/grease/bromide
|
Ph
|
Sulfate
|
Total dissolved solids reside - filterable turbidity
| ||
Ethylene glycol
|
Acetone
| |||
TRACE METAL
| ||||
Barium
|
Calcium
|
Iron
|
Magnesium
|
Manganese
|
Potassium
|
Sodium
|
Stontium
|
Aluminum
|
Lithium
|
Selenium
|
Boron
| |||
ORGANIC
| ||||
Ethane
|
Methane
|
Propane
|
Total petroleum hydrocarbons
| |
MICRO-BIOLOGY
| ||||
Total Coliform/E. Coli
| ||||
OTHER
| ||||
Volatile organic compounds
| ||||
Detergent (MBAs)
| ||||
Total organic carbon
| ||||
Nitrate
| ||||
Radionuclides gross alpha, radium
| ||||
Radon
| ||||
Lead
| ||||
Total coliform
| ||||
Bacteria
|
10.
Predrilling and post-hydraulic fracturing soil survey requirements.
Prior to drilling and post-hydraulic fracturing, the operator shall
be responsible for testing soil conditions within the area of the
drill site, but no greater than 500 feet from the surface location
of the well. The purpose of testing is to determine the baseline soil
conditions in the immediate vicinity of the proposed well site and
evaluate resultant changes that may occur or have an impact on the
soils of the site and surrounding area.
A.
Predrilling testing results shall be submitted as part of the conditional
use application.
B.
Post-hydraulic fracturing testing shall be completed no sooner that
one month after hydraulic fracturing activities have ceased and no
later than two months after hydraulic fracturing activities have ceased.
C.
The results shall be submitted to the Borough and PA DEP within 10
days of their receipt.
D.
The operator shall be responsible for all costs associated with sample
collection and testing and testing shall be done by an independent
state-certified testing laboratory agreed upon by the Borough.
E.
Operators shall test for the following list of parameters for soils.
The list is not exhaustive and the Borough reserves the right to add
additional parameters;
INORGANIC
| |||||
Alkalinity
|
Chloride
|
Hardness
|
Oil/Grease/bromide
|
Ph
| |
Sulfate
|
Total dissolved solids
|
Reside filterable
|
Bromide
| ||
TRACE METAL
| |||||
Barium
|
Calcium
|
Iron
|
Magnesium
|
Manganese
|
Potassium
|
Sodium
|
Stontium
|
Aluminum
|
Lithium
|
Selenium
| |
Boron
|
Arsenic
|
Zinc
| |||
MICRO-BIOLOGY
| |||||
Total Coliform/E. Coli
| |||||
OTHER
| |||||
Volatile organic compounds
| |||||
Nitrate
| |||||
Radio-nuclides gross alpha
| |||||
Radium
| |||||
Lead
|
11.
Drip pans must be placed in any location, under equipment, that has
the potential to leak.
12.
All condensate tanks shall be equipped with vapor recovery and/or
vapor destruction units.
13.
All structures including, but not limited to pumping units, storage
tanks, buildings and structures shall be painted a neutral color,
compatible with the surrounding uses. Neutral colors shall include
sand, gray, green and unobtrusive shades of brown, or other neutral
colors, as approved by the Borough Engineer/Zoning Officer.
14.
Processing plants shall be inspected by the fire department prior
to operation. During the active operation at the processing plant,
Borough staff or consultants designated by the Borough Manager shall
have access to the site to determine continuing compliance with the
conditional use approval.
15.
The applicant will reimburse the Borough for all reasonable and direct
professional consultant fees incurred by the Borough related to site
inspection, approval process, or for specialized work called for in
the permit.
16.
The Borough of Sharpsburg reserves the right to impose any other
additional conditions necessary to protect the public health, safety
and general welfare of its residents in order to address any unique
characteristics of a particular processing plant site which are not
otherwise within the jurisdiction of federal and state regulations
in accordance with the Pennsylvania Municipalities Planning Code[1] (PAMPC).
[1]
Editor's Note: See 53 P.S. § 10101 et seq.
17.
Indemnification and express negligence provisions. The operator shall
fully defend, protect and hold harmless Sharpsburg Borough, its departments,
officials, officers, agents, employees and contractors from and against
each and every claim, demand, or cause of action and any and all liability,
damages, obligations, judgments, losses, fines, penalties, costs,
legal and expert fees and expenses incurred in defense of Sharpsburg
Borough, including, without limitation, personal injuries and death
in connection therewith which may be made or asserted by any third
parties on account of, arising out of, or in any way incidental to
or in connection with the performance by the operator.
18.
The facility and/or its operation shall comply with all applicable
permits and requirements of the PA DEP, the United States Environmental
Protections Agency and any other governmental authority having jurisdiction
over its operations and with all federal, state and local laws, ordinances
and regulations promulgated to protect the environment or otherwise
relating to environmental matters. The applicant shall demonstrate
that the compressor stations will not violate the citizens of Sharpsburg
Borough's right to clean air and pure water as set forth in Article
1, Section 27 of the Pennsylvania Constitution (The Environmental
Rights Amendment). The applicant will have the initial burden to demonstrate
that it operation will not affect the health, safety or welfare of
the citizens of Sharpsburg Borough or any other potentially affected
landowner. The application submittal shall include report from qualified
Environmental individuals attesting that the proposed location will
not negatively impact the Borough residents' Environmental Rights
and will include air modeling and hydrogeological studies as potential
pathways that a spill or release of fluid may follow.
19.
Impoundments (being either a water impoundment fresh or a water impoundment,
waste), are subject to:
A.
Impoundments shall be allowed only on the parcel/property where drilling
is occurring as an accessory use.
B.
No off-site impoundments, drill cutting pits/reserve pits shall be
permitted.
C.
Impoundments shall not use surface aerators.
D.
All drill site impoundments shall be secured with a temporary fence
with a secured gate as follows:
(1)
The fence shall be a minimum of six feet in heights and chain
link.
(2)
The fencing shall be in place throughout the drill operation
and until the impoundment is removed.
(3)
The chain link fence shall have a minimum thickness of 11 gauges.
(4)
Impoundments must comply with all state and federal laws in
regard to leak detection and monitoring and must comply with EPA 9090
or any regulation that supersedes it.
(5)
Upon review of the application, Council may, in its discretion,
require air modeling and monitoring of emissions coming off of impoundments.
E.
An impoundment shall not contain any liquid substance generated from
any oil well (s) located on another property. Trucking in of outside
liquid substance for storage in an impoundment is prohibited.
F.
Size limitation. Impoundments are permitted to house up to 1,000,000
gallons of liquid substance.
G.
An impoundment must be completely enclosed within a structure with
solid walls and a roof.
H.
An applicant shall provide to the Borough a preparedness, prevention
and contingency (PPC) plan as defined in the PA DEP document Guidelines
for the Development and Implementation of Environmental Emergency
Response Plans or the most recent applicable guidance document.
I.
An applicant shall provide to the Borough a baseline hydrogeological
study to document background conditions including, but not limited,
to initial water quality testing, water level measurements, available
secondary source information leading to an understanding of groundwater
flow beneath the site and adjacent areas.
This part shall take effect immediately upon passage.