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“The mechanisms by which the Marcellus gas shale sequesters residual treatment water (RTW)”



                                            Terry Engelder
                                       Department of Geosciences
                                    The Pennsylvania State University
                                       University Park, PA 16801


body The international rush to produce gas within shale by horizontal drilling and massive slickwater
hydraulic fracturing (i.e., fracking) has prompted concerns that fracking may harm global health (1).
Concerns involving water quality arise because as much as 2 x 10 4 m3 of water-based fluid is injected into
gas shale to open fractures near each horizontal well (Table 1). Prior to injection, water is treated to
prevent bacterial growth, to prevent scaling of steel pipes, to aid in rapid flow, to prevent swelling of the
clay minerals in the shale, and to carry sand which props fractures open. Once fractures within the gas
shale are opened, the treatment water reacts with constituents of the shale to gather up salt, some metals,
and a few radionuclides. During the lifetime of a gas-shale well less than half of the treatment water is
recovered as flowback or later production brine (2). While recovered treatment water is easily managed,
residual treatment water (RTW) slips beyond the control of engineers. Presently, the fate of this RTW,
more than 104 m3 per horizontal well, is uncertain. The question is whether the RTW might someday
appear in groundwater (3).

The report by Warner et al. in this issue of PNAS (3) focuses on the migration of natural brine as a proxy
for migration of RTW. Warner et al. conclude that the Type D waters mark cross formational pathways
where high Br/Cl, low 87Sr/86Sr, high Sr/Ca brines have migrated from the deep formations in the past.
They do not state when this cross formation brine migration took place, but imply (by mentioning it’s
methane richness and it’s prevalence in valleys where present-day escape is more likely because of a
freshwater sweep from highland infiltration) that the natural migration is ongoing today. By referring to
the source repeatedly as the “Marcellus” they suggest that leakage is from the Marcellus. They suggest
the pathways of natural gas leakage might be areas of higher risk for leakage of RTW. The implication is
that the Marcellus is leaking now, naturally without any human assistance, and that if water-based fluid is
injected into these cross-formational pathways, that leakage, which is already ‘contaminating’ the aquifers
with salt, could be made much worse.

In the Appalachian Basin high Br/Cl brines are residuals from extensive evaporation and halite
precipitation of seawater (4). One of two geologically reasonable sources is residual pore fluids in the
Silurian Salina salt. These residual brines were almost certainly squeezed out by salt deformation during
the Alleghanian orogeny some 270-260 million years ago (5). These brines likely contaminated the
Marcellus and the Upper Devonian section at that time by mixing into a deep regional flow system
originating in the high Alleghanian uplands to the SE.

Using a typical electric log from the Marcellus, it is clear that the volume of free water within the
Marcellus is so small it cannot support ongoing contamination of the shallow aquifers with high Br/Cl
brine as observed by Warner et al. (3) even assuming it is leaking (Figure 1). If fully saturated and
completely mixed into treatment water, the natural free water could bring the salinity of flowback up to ≈
105 ppm (Table 1). The volume of the capillary bound water is also more than sufficient to increase the
salinity of the treatment water as observed. The Marcellus water chemistry reported in Warner et al. (3) is
most likely found in treatment water salinized in situ and is, therefore to be distinguished from natural
brines produced by oil and gas wells from the Medina, Tuscarora, and Oriskany sandstones (6).

The Marcellus has plenty of joints as a consequence of gas generation and expulsion (7). These joints
have a very low innate water-filled φ largely because early gas became saturated in water and the free
water was carried off during expulsion, leaving behind stratabound salt (Blauch, 2009). This process
progresses to the point that residual brine in the Marcellus evolved beyond halite precipitation (Figure
1). Thus the Marcellus, and other gas-generating shales become relatively dry and the residual brine
they contain will tend toward the high Br/Cl variety.

Why are the Marcellus and other gas shales such a good seals? The strata surrounding the Marcellus and
similar gas filled shales contains water, and so capillary seals will form at their margins (8). These
capillary seals form automatically in the presence of a porous media with variations in porosity and two
fluids. They are virtually indestructible, and for this reason trap gas in basins virtually forever. In the
case of the Marcellus they have trapped in the gas for at least 200 million years (this being the end of the
period when it was generated).

Several observations serve as evidence that fluids are not leaking from the Marcellus today. The
Marcellus is the seal over very large Oriskany gas fields in NY and PA holding an initial pressure head of
> 0.7 psi.ft (9). Shut-in tests within the Marcellus show gas pressure > 0.85 psi/ft (proprietary). Joints
containing water tend to heal in the form of veins. Common Marcellus joints are gas charged and
unhealed (6). The Marcellus carries a low water saturation (< 10%). High gas pressure indicates that,
even if fractures within the Marcellus are interconnected, they are sealed by a capillary-bound water. Yes,
the gas in the Marcellus today is highly over pressured, but this does not mean gas is leaking out; it is
firmly trapped by capillary seals. If it was leaking even a very very little, it would now be all gone. 200
million years (the end of active gas generation with the onset of exhumation) is a long time to leak.

There is no doubt that deep basin brine passed through the Marcellus during Alleghanian tectonics as
witness by Marcellus veins with 26 wt % equivalent NaCl fluid inclusions (10). Certainly, it is reasonable
to suppose that the free water in the Marcellus has the same salinity. The most likely place for deep basin
brines to have passed through the Marcellus and its Upper Devonian overburden is in the more heavily
fractured core of anticlines where more faults are found (11). However, many of these faults are low
angle and likely to be smeared with clay fault gouge, a low permeability seal rock.

While 104 m3 of RTW may seem like a large volume, the reservoir volume that is stimulated by hydraulic
fracturing is much larger (Table 1). If imbibed pervasively in the stimulated reservoir volume, the RTW
could be absorbed by a porosity (φ) of roughly 0.06%. Spontaneous imbibition is a form of wicking made
possible by a high capillary pressure within the water-wet matrix of very fine grained rocks like gas shale.
Imbibition is limited to a zone near fracture walls where water invasion can be 3 cm in an experimental
time frame of three days in nanoDarcy permeability shales (2). If fracture spacing is as low as 1 m only 5
cm of matrix penetration by imbibition will sequester the entire charge of RTW in a shale φ of 0.6%. If
RTW is caught in the tip regions of fractures, less imbibition is necessary for total sequestration. RTW
sequestered by a combination of imbibition and flow to joint-tip regions is of no further concern to global
health particularly when mantled by a capillary seal (8).

ACKNOWLEDGMENTS. My work on gas shale has carried on for more than 30 years with support
from both government (presently DOE/RPSEA) and industry (presently PSU-ABBSG).



References:

    1. Howarth RW, Ingraffea A, Engelder T (2011) Natural Gas: Should fracking stop? Nature
       471:271-275.

    2. Pagels M, Willberg D, Edelman E (2011) Chemo-mechanical effects of induced fluid invasion
       into ultralow permeability rocks: AGU Fall Meeting 2011, San Francisco, Poster H21B-1091.

    3. Warner NR, et al. (2012) Geochemical evidence for possible natural migration of Marcellus
       Formation brine to shallow aquifers in Pennsylvania: Proc. Natl. Acad. Sci. USA XXX:ZZZ.

    4. Dresel P, Rose AW (2010) Chemistry and origin of oil and gas well brines in western
       Pennsylvania: Pennsylvania Geological Survey. in 4th series Open-File Report OFOG 10–01.0
       (Pennsylvania Department of Conservation and Natural Resources), p 48.

    5. Davis DM, Engelder T (1985) The role of salt in fold-and-thrust belts Tectonophysics 119: 67-88.

    6. Engelder T, Lash, GG, Uzcategui RS (2009) Joint sets that enhance production from Middle and
       Upper Devonian gas shales of the Appalachian Basin American Association of Petroleum
       Geologists Bulletin 93:857-889.

    7. Haluszczak LO, Rose AW, Kump LR (2012) Geochemical evaluation of flowback and production
       waters from Marcellus gas wells in Pennsylvania (submitted).

    8. Cathles, L. M., 2004, Hydrocarbon generation, migration, and venting in a portion of the offshore
       Louisiana Gulf of Mexico Basin, The Leading Edge, August, 7 p.

    9. Fettke CR (1953) Oil and gas developments in Pennsylvania in 1952 Commonwealth of
       Pennsylvania, Dept. of Internal Affairs, Topographic and Geologic Survey 30 p.

    10. Evans MA (1995) Fluid inclusions in veins from the Middle Devonian Shales: A record of
        deformation conditions and fluid evolution in the Appalachian Plateau Geological Society of
        America Bulletin 107:327-339.

    11. Scanlin MA, Engelder T (2003) The basement versus the no-basement hypothesis for folding
        within the Appalachian Plateau Detachment Sheet American Journal of Science 303:519-563.
Figure 1. A proprietary Schlumberger ELAN (Elemental Log Analysis) showing that the Marcellus is a
quartz/clay mudstone with limestone stringers (left tract). At 6505’ kerogen and the gas filled porosity in
the kerogen constitute 30% of the volume of the rock. Most of the water in the rock is clay-bound. The
rest of the water in the Marcellus is either capillary-bound or free (left tract – white). Moved hydrocarbon
is the volume of hydrocarbon per unit volume of rock that have been displaced by invasion of drilling
mud (left tract - orange). Total porosity in the Marcellus (φ) includes 2% and 5% clay-bound water which
does react with residual treatment water (right tract – white). The maximum effective φ at 15% in the
Marcellus is gas charged and this φ is found in oil-wet kerogen where gas saturation approaches 100%
(right tract – red). A much smaller fraction of the effective φ is water filled and only portion of the
effective φ contains free water subject to Darcy flow (right tract – blue). Capillary-bound water is evenly
distributed through the 150’ section of the Marcellus (right tract – gray).



Table 1.

  Volume of Marcellus tapped              15.3x106 m3     =(83 acres)(4047 m2/acre)(150 ft)(0.3048 m/ft)
  Volume of treatment water               2x104 m3        =5.3 million gallons
  Volume of capillary-bound water         1-2x105 m3      =(1% - 2% porosity)(15.3x106 m3)
  Vol. of free water that could leak      8,160 m3        =(8 ft/150 ft)(1% porosity)(15.3x106 m3)
  Volume filled with gas                  1.2x106 m3      =(≈8% porosity)(15.3x106 m3)
Terry Engelder Letter to PNAS Objecting to Publication of Duke Study on Brine Migration

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Terry Engelder Letter to PNAS Objecting to Publication of Duke Study on Brine Migration

  • 1. “The mechanisms by which the Marcellus gas shale sequesters residual treatment water (RTW)” Terry Engelder Department of Geosciences The Pennsylvania State University University Park, PA 16801 body The international rush to produce gas within shale by horizontal drilling and massive slickwater hydraulic fracturing (i.e., fracking) has prompted concerns that fracking may harm global health (1). Concerns involving water quality arise because as much as 2 x 10 4 m3 of water-based fluid is injected into gas shale to open fractures near each horizontal well (Table 1). Prior to injection, water is treated to prevent bacterial growth, to prevent scaling of steel pipes, to aid in rapid flow, to prevent swelling of the clay minerals in the shale, and to carry sand which props fractures open. Once fractures within the gas shale are opened, the treatment water reacts with constituents of the shale to gather up salt, some metals, and a few radionuclides. During the lifetime of a gas-shale well less than half of the treatment water is recovered as flowback or later production brine (2). While recovered treatment water is easily managed, residual treatment water (RTW) slips beyond the control of engineers. Presently, the fate of this RTW, more than 104 m3 per horizontal well, is uncertain. The question is whether the RTW might someday appear in groundwater (3). The report by Warner et al. in this issue of PNAS (3) focuses on the migration of natural brine as a proxy for migration of RTW. Warner et al. conclude that the Type D waters mark cross formational pathways where high Br/Cl, low 87Sr/86Sr, high Sr/Ca brines have migrated from the deep formations in the past. They do not state when this cross formation brine migration took place, but imply (by mentioning it’s methane richness and it’s prevalence in valleys where present-day escape is more likely because of a freshwater sweep from highland infiltration) that the natural migration is ongoing today. By referring to the source repeatedly as the “Marcellus” they suggest that leakage is from the Marcellus. They suggest the pathways of natural gas leakage might be areas of higher risk for leakage of RTW. The implication is that the Marcellus is leaking now, naturally without any human assistance, and that if water-based fluid is injected into these cross-formational pathways, that leakage, which is already ‘contaminating’ the aquifers with salt, could be made much worse. In the Appalachian Basin high Br/Cl brines are residuals from extensive evaporation and halite precipitation of seawater (4). One of two geologically reasonable sources is residual pore fluids in the Silurian Salina salt. These residual brines were almost certainly squeezed out by salt deformation during the Alleghanian orogeny some 270-260 million years ago (5). These brines likely contaminated the Marcellus and the Upper Devonian section at that time by mixing into a deep regional flow system originating in the high Alleghanian uplands to the SE. Using a typical electric log from the Marcellus, it is clear that the volume of free water within the Marcellus is so small it cannot support ongoing contamination of the shallow aquifers with high Br/Cl brine as observed by Warner et al. (3) even assuming it is leaking (Figure 1). If fully saturated and completely mixed into treatment water, the natural free water could bring the salinity of flowback up to ≈
  • 2. 105 ppm (Table 1). The volume of the capillary bound water is also more than sufficient to increase the salinity of the treatment water as observed. The Marcellus water chemistry reported in Warner et al. (3) is most likely found in treatment water salinized in situ and is, therefore to be distinguished from natural brines produced by oil and gas wells from the Medina, Tuscarora, and Oriskany sandstones (6). The Marcellus has plenty of joints as a consequence of gas generation and expulsion (7). These joints have a very low innate water-filled φ largely because early gas became saturated in water and the free water was carried off during expulsion, leaving behind stratabound salt (Blauch, 2009). This process progresses to the point that residual brine in the Marcellus evolved beyond halite precipitation (Figure 1). Thus the Marcellus, and other gas-generating shales become relatively dry and the residual brine they contain will tend toward the high Br/Cl variety. Why are the Marcellus and other gas shales such a good seals? The strata surrounding the Marcellus and similar gas filled shales contains water, and so capillary seals will form at their margins (8). These capillary seals form automatically in the presence of a porous media with variations in porosity and two fluids. They are virtually indestructible, and for this reason trap gas in basins virtually forever. In the case of the Marcellus they have trapped in the gas for at least 200 million years (this being the end of the period when it was generated). Several observations serve as evidence that fluids are not leaking from the Marcellus today. The Marcellus is the seal over very large Oriskany gas fields in NY and PA holding an initial pressure head of > 0.7 psi.ft (9). Shut-in tests within the Marcellus show gas pressure > 0.85 psi/ft (proprietary). Joints containing water tend to heal in the form of veins. Common Marcellus joints are gas charged and unhealed (6). The Marcellus carries a low water saturation (< 10%). High gas pressure indicates that, even if fractures within the Marcellus are interconnected, they are sealed by a capillary-bound water. Yes, the gas in the Marcellus today is highly over pressured, but this does not mean gas is leaking out; it is firmly trapped by capillary seals. If it was leaking even a very very little, it would now be all gone. 200 million years (the end of active gas generation with the onset of exhumation) is a long time to leak. There is no doubt that deep basin brine passed through the Marcellus during Alleghanian tectonics as witness by Marcellus veins with 26 wt % equivalent NaCl fluid inclusions (10). Certainly, it is reasonable to suppose that the free water in the Marcellus has the same salinity. The most likely place for deep basin brines to have passed through the Marcellus and its Upper Devonian overburden is in the more heavily fractured core of anticlines where more faults are found (11). However, many of these faults are low angle and likely to be smeared with clay fault gouge, a low permeability seal rock. While 104 m3 of RTW may seem like a large volume, the reservoir volume that is stimulated by hydraulic fracturing is much larger (Table 1). If imbibed pervasively in the stimulated reservoir volume, the RTW could be absorbed by a porosity (φ) of roughly 0.06%. Spontaneous imbibition is a form of wicking made possible by a high capillary pressure within the water-wet matrix of very fine grained rocks like gas shale. Imbibition is limited to a zone near fracture walls where water invasion can be 3 cm in an experimental time frame of three days in nanoDarcy permeability shales (2). If fracture spacing is as low as 1 m only 5 cm of matrix penetration by imbibition will sequester the entire charge of RTW in a shale φ of 0.6%. If RTW is caught in the tip regions of fractures, less imbibition is necessary for total sequestration. RTW
  • 3. sequestered by a combination of imbibition and flow to joint-tip regions is of no further concern to global health particularly when mantled by a capillary seal (8). ACKNOWLEDGMENTS. My work on gas shale has carried on for more than 30 years with support from both government (presently DOE/RPSEA) and industry (presently PSU-ABBSG). References: 1. Howarth RW, Ingraffea A, Engelder T (2011) Natural Gas: Should fracking stop? Nature 471:271-275. 2. Pagels M, Willberg D, Edelman E (2011) Chemo-mechanical effects of induced fluid invasion into ultralow permeability rocks: AGU Fall Meeting 2011, San Francisco, Poster H21B-1091. 3. Warner NR, et al. (2012) Geochemical evidence for possible natural migration of Marcellus Formation brine to shallow aquifers in Pennsylvania: Proc. Natl. Acad. Sci. USA XXX:ZZZ. 4. Dresel P, Rose AW (2010) Chemistry and origin of oil and gas well brines in western Pennsylvania: Pennsylvania Geological Survey. in 4th series Open-File Report OFOG 10–01.0 (Pennsylvania Department of Conservation and Natural Resources), p 48. 5. Davis DM, Engelder T (1985) The role of salt in fold-and-thrust belts Tectonophysics 119: 67-88. 6. Engelder T, Lash, GG, Uzcategui RS (2009) Joint sets that enhance production from Middle and Upper Devonian gas shales of the Appalachian Basin American Association of Petroleum Geologists Bulletin 93:857-889. 7. Haluszczak LO, Rose AW, Kump LR (2012) Geochemical evaluation of flowback and production waters from Marcellus gas wells in Pennsylvania (submitted). 8. Cathles, L. M., 2004, Hydrocarbon generation, migration, and venting in a portion of the offshore Louisiana Gulf of Mexico Basin, The Leading Edge, August, 7 p. 9. Fettke CR (1953) Oil and gas developments in Pennsylvania in 1952 Commonwealth of Pennsylvania, Dept. of Internal Affairs, Topographic and Geologic Survey 30 p. 10. Evans MA (1995) Fluid inclusions in veins from the Middle Devonian Shales: A record of deformation conditions and fluid evolution in the Appalachian Plateau Geological Society of America Bulletin 107:327-339. 11. Scanlin MA, Engelder T (2003) The basement versus the no-basement hypothesis for folding within the Appalachian Plateau Detachment Sheet American Journal of Science 303:519-563.
  • 4. Figure 1. A proprietary Schlumberger ELAN (Elemental Log Analysis) showing that the Marcellus is a quartz/clay mudstone with limestone stringers (left tract). At 6505’ kerogen and the gas filled porosity in the kerogen constitute 30% of the volume of the rock. Most of the water in the rock is clay-bound. The rest of the water in the Marcellus is either capillary-bound or free (left tract – white). Moved hydrocarbon is the volume of hydrocarbon per unit volume of rock that have been displaced by invasion of drilling mud (left tract - orange). Total porosity in the Marcellus (φ) includes 2% and 5% clay-bound water which does react with residual treatment water (right tract – white). The maximum effective φ at 15% in the Marcellus is gas charged and this φ is found in oil-wet kerogen where gas saturation approaches 100% (right tract – red). A much smaller fraction of the effective φ is water filled and only portion of the effective φ contains free water subject to Darcy flow (right tract – blue). Capillary-bound water is evenly distributed through the 150’ section of the Marcellus (right tract – gray). Table 1. Volume of Marcellus tapped 15.3x106 m3 =(83 acres)(4047 m2/acre)(150 ft)(0.3048 m/ft) Volume of treatment water 2x104 m3 =5.3 million gallons Volume of capillary-bound water 1-2x105 m3 =(1% - 2% porosity)(15.3x106 m3) Vol. of free water that could leak 8,160 m3 =(8 ft/150 ft)(1% porosity)(15.3x106 m3) Volume filled with gas 1.2x106 m3 =(≈8% porosity)(15.3x106 m3)