Pits
At a drilling site pits are used to store water, contain
drilling fluids and cuttings or to hold other liquid substances such as brine
or oil. Sites we’ve examined have all had at least one pit, that for drilling
fluids and cuttings. These pits may also have held used fracture fluids
(flowback). The only sites that probably didn’t have a pit were those dating
from the 1940s.
Unless an examination is made of a number of Discharge Monitoring Reports filed
with the state we have no way of knowing what percentage of pits may possibly
have held flowback (category 1 pits do not contain flowback). Because of that
we have to assume all pits contain some flowback.
Regulation of pits and what they can hold is distributed over three platforms
in West Virginia: code of state regulations (35 CSR 4.16.4), Erosion and Sedimentation
Control Field Manual (II.B.2 and III.A) and General Water Pollution
Control Permit (G2, G10 and G15). This is typical
for this state where regulatory control is dispersed and lacks any form of
quantification. For example, freeboard is required by the code of state
regulations (35 CSR 4.16.4c), but no amount of required freeboard is given,
such as 2 feet. Other absences include no limitation of placement in respect to
ground or surface water. A driller, in essence, can put a pit anywhere, even
where common sense would dictate differently.
We’ve created a webpage that has the three
regulatory platforms’ texts together in one spot.
Problems with the state’s regulations occur in these areas: no limitation of
pit location in respect to ground water; no limitation of placement of pit on
site (fill area) or near surface water; no specifications for proper liner and
installation/welding; no technique for proper encapsulation of solid waste and
cover requirements; and finally, no placement of permanent marker and filing a
deed notice to comply with Federal Housing Administration requirements for
future builders and homeowners. Except for possibly the last item, the state’s
policies do not protect the environment or the health and welfare of its
citizens.
Ground Water
While the state’s regulations make offhand requirements to protect the state’s
waters, there is no minimum distance between the bottom of the pit and ground
water. The Argonne National Laboratory recommends a minimum of 5 feet between
the bottom of the pit and seasonal high water level. British Columbia requires
a minimum of 1 meter. New Mexico in its recently updated regulations requires
the distance be at least 50 feet. We believe the state should adopt the Argonne
National Laboratory’s recommendation at a minimum. The distance should be much
more in sandy soils.
Pit Location
The pit needs to be placed in firm soil. Sandy soils are not appropriate
without amendment of some sort according to the Railroad Commission of Texas.
Fill soils are inappropriate and pits in fill soils need special written permission
in British Columbia. Placing a pit on the edge of the pad by the fill slope is
not recommended by the Erosion and Sedimentation Control Field Manual but we
believe this is quite common. With pits increasing dramatically in size, the
state needs to regulate or somehow control the use of fill soils.
The pit needs to have the site constructed so that rain or other water is
directed away from the pit (with berm and/or ditch). The General Water
Pollution Control Permit actually sanctions the directing of stormwater into
the pit (G15). Overflow of the pit because of improper stormwater drainage
causes contamination of soils, ground and surface water. The freeboard needs to
be a stated amount (New Mexico and Arkansas require 2 feet freeboard).
The location of a pit near a body of surface water should be regulated. New
Mexico requires a distance of 300 feet from a river (other setbacks are
regulated in New Mexico, such as 500 feet from a domestic water source). In
Texas, water wells within 1 mile of a pit need to be recorded in the permit, as
does the depth of the shallowest freshwater for those wells. Arkansas has
similar requirements in its permit for landspraying.
Pit Liners
Pit liners are optional for this state but I believe are commonly used. Liners
should always be required. The state has no specifications for liners which are
available in a variety of materials and thicknesses. The state also has no
requirements for locations of seams (up and down slopes, not laterally, for
instance) or installation (type and depth of anchor trench). We believe that
New Mexico’s regulations could easily be adapted.
Burial and Cover
Before burial, the solids at the bottom of the pit are encapsulated (though
West Virginia doesn’t require encapsulation; open liners and contents can be
buried shallowly). Basically, encapsulation means the pit liner’s edges are
folded over the solids preventing their escape. Cover over the burial cell is
important since enough depth is required to prevent plant roots from disturbing
the liner’s integrity. The Argonne National Laboratory recommends at least 3
feet of cover. We believe that more is required where the reclaimed surface
will eventually revert to forest. Soil cover needs to be graded so that the
surface doesn’t allow the ponding of water. We believe the Argonne National
Laboratory’s recommendations should be incorporated in the state’s regulations.
Permanent Marker
There needs to be a way to record the exact location of each pit in the state.
In New Mexico this is done through a deed notice associated with the surface
owner’s property deed. New Mexico also requires a permanent marker much like
that required in this state for plugged wells — a steel monument 3 feet above
the ground’s surface. British Columbia requires a separate pit permit and
registration for each pit and the pit number(s) posted at the drill site
(Arkansas has similar requirements). New Mexico’s regulations were written so
as to not disadvantage surface owners at the present or in the future because
of Federal Housing Administration requirements. This state needs to do the
same.
In a future post we’ll present our recommendations for pits adapted from our
comments for Raymond City #17.
Sources:
Argonne National Laboratory. Fact Sheet – Onsite Burial (Pits, Landfills). Drilling Waste Management, web page accessed 20
September 2008.
Arkansas. 2008. Authorization to
Construct, Operate and Close the Pits Associated with Oil and Gas Well
Exploration. Arkansas Department of
Environmental Quality, Permit No. 00000-WG-P.
British Columbia Oil and Gas Commission. n.d. British Columbia Oil and
Gas Handbook, Chapter 10, Drilling Waste Management. n.p.: British Columbia Oil and Gas Commission.
Department of Housing and Urban Development. 1999. Changes to Handbook
4150.2, Valuation Analysis for Single Family One- to Four-Unit Dwellings. n.p.: Department of Housing and Urban Development. Chapter
2: Site Analysis, 2.2.E.
New Mexico. 2008. New Mexico Code and State
Rules for Oil and Gas. New
Mexico Energy, Minerals and Natural Resources Department, Oil Conservation
Division.
New Mexico. Highlights of the
“Pit Rule” — 19.15.17 NMAC.
Santa Fe, NM: New Mexico Energy, Minerals and Natural Resources Department, Oil
Conservation Division.
Railroad Commission of Texas. Surface Waste Management
Manual, Chapter 4, Pits. Railroad
Commission of Texas website, accessed 8 December 2008.
April 28, 2009