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Surface and
Near-Subsurface Hydrocarbon Migration Patterns, Mechanisms and
Seepage
Rates
Associated with a Macroseep
By
V.T. Jones, III, Exploration Technologies, Inc., D.F. Becker, Geoscientific Consulting Partners, D.D. Coleman, Isotech Laboratories, Inc., T.H. Anderson, University of Pittsburgh, P.A. Witherspoon, University of California, and G.A. Robbins, University of Connecticut
Previous assessments within a planned development area revealed methane macroseeps emanating from a natural wetland containing marsh deposits, Gas bubbles rising from an adjacent creek that crosses the property initially indicated the presence of methane gas emissions, Gas measurements made in five deep wells at multiple depths. extending down to the 50 feet adjacent to the creek confirmed the presence of gas in deeper sediments underlying the site. The methane was initially interpreted as biogenic, and non-hazardous although a natural gas storage reservoir lies within 3000 feet of the area where the methane seeps occur. An invcstigation was bcgun to address concern about possible leakage from the gas storage reservoir.
A soil gas survey, consisting of over 800 sites placed on a 100 foot grid
spacing was completed over the site, defining an area of anomalous
seepage
.
Within the area of seeps, methane concentration in some samples is as high as
100%. At each site gas was cxtractcd from a four-foot deep soil gas probe
and analyzed for methane through butanes, carbon dioxide, and hydrogen sulfide.
Selected soil gas samples were also analyzed for carbon and hydrogen isotopes.
The distribution of the methane seeps was used to locate areas where deeper
monitor wells might be installed in order to assess input from deeper sources.
It was anticipated that mapping the presence of gas anomalies within an
extensive gravel aquifer that completely underlies the site at a depth of
approximately 50 feet could: 1) define gas sources located at intermediate depth
below the marsh deposits and 2) provide a three dimensional picture of the
natural gas
seepage
in the area.
Using the soil gas maps as a guide, 42 monitor wells were installed in the gravel aquifer. Both free and dissolved gases were collected from each of these wells using water displacement, with at least one sample collected from each of the five to seven well-volumes of water pumped from each of the wells. The well gases were analyzed for their methane through butane and carbon dioxide contents. The hydrocarbon data from the monitor wells collected and analyzed by this method provide reliable control points from which distribution of the light hydrocarbons within the aquifer may be estimated. Areas containing methane concentrations in the aquifer ranged from zero to 100%, with the quantity of free gases increasing significantly within the areas containing the higher methane levels. Carbon isotopes for methane, ethane, and carbon dioxide and hydrogen isotopes for methane were analyzed for all monitor wells, although only one sample from each well was analyzed. An excellent correlation between both composition and isotopic ratios was found between the soil gas seeps at four feet and the dissolved and free gases in the gravel aquifer at 50 feet. Gas collected from seeps and wells is derived from thermogenic sources.
Gases from nine deep wells within lhc storage field were collcctcd and analyzed for their chemical and isotopic compositions for comparison with the near-surface and deeper ground water aquifer gases. Comparison of the chemical and isotopic data indicates that the surface gas seeps and 50-foot gravel aquifer gases are not related to the gases injected into the adjacent gas storage field. The shallow gas is nearly identical to production gases from a field about 4.5 miles to the southeast. This field has produced over 23 BCF of dry gas from the Pico Forrnation_ A non-productive well drilled adjacent to the secpagc anomaly blcw out in 1930 while drilling at 1830 feet in the Pico Formation and flowed at the rate of 5 MMcfpd for a few hours. A 3-D seismic study indicates the presence of disrupted strata, possibly associated with a fractured slump0 block that appears to provide the vertical pathways for the observed macroseeps.
Using the soil gas contour maps as a guide, numerous additional macroseeps
were located on land, where gas seeps are typically difficult to find. Measured
seepage
rates range upwards from about 1 ml/minute to as much as 9 liters/minute
of gas into the atmosphere. This variation in
seepage
rates, coupled with the
extensive data base from the aquifer below the oxidation zone, provides a unique
opportunity to study, and document near-surface alteration effects on soil
gases.
The
seepage
gases contain mainly methane and are very dry. However, ethane
through butanes are sufficiently abundant for chemical trace analysis, and there
is adequate ethane for carbon isotopes analysis on selected samples Although,
the ethane is quite degraded within the 50 foot deep gravel aquifer, it exhibits
only a small variation in the ethane carbon isotope within the aquifer, ranging
from -18 to -2l parts per mil. Very near the surface. ethane carbon isotope
values as low as -13.5 per mil have been documented at four feet, suggesting
additional near-surface degradation related to the shallow depth. This type of
degradation effect has also been documented for methane, where the methane
carbon isotopes have been altered to values that appear to be more mature than
they are in the underlying aquifer. These oxidation-related changes could easily
be misinterpreted as being more mature than they really are without the
additional supporting data.
In areas having very high advective
seepage
rates, both the methane and the
ethane have chemical and isotopic values that are identical to those measured in
the gravel aquifer. However, in areas having moderate
seepage
rates, where
oxygen probably diffuses into the shallow subsurface, both methane and ethane
isotopes have been documented to have carbon isotopes values that do not
represent their true source, and/or maturity that is normally associated with
isotope interpretations, Thus the carbon isotope data may be easily
misinterpreted. In such samples, only the chemical composition; i.e., presence
of ethane, propane, and butanes proves the presence of a thermogenic source.
Hydrogen sulfide does not occur in the gases vented directly from the gravel aquifer. It is, however, often present in the larger soil gas anomalies. The source for hydrogen sulfide appears to be natural, organic rich soils, and its areal distribution at the surface correlates almost entirely with rich seeps of methane gas, which apparently act as a carrier.
Figure Captions