25 research outputs found
第2章 1-4-4-3. 河川の富栄養化に伴う河川の各種窒素プールの窒素同位体比の変動
Spearman correlation among all nutrients. (DOC 32Â kb
Age Dating Oil and Gas Wastewater Spills Using Radium Isotopes and Their Decay Products in Impacted Soil and Sediment
Spills
from oil and gas operations can contaminate water resources,
sediment, and soil, but in many cases, information about spill sources
and environmental impacts is not available. Here we present age dating
methods to estimate the time since the accumulation of radium in impacted
soils and sediments from oil and gas wastewater spills. The retention
of unsupported <sup>226</sup>Ra and <sup>228</sup>Ra from spill water
to soil and sediment and the ingrowth of Ra progeny result in three
independent age dating methods using the <sup>228</sup>Th/<sup>228</sup>Ra, <sup>210</sup>Pb/<sup>226</sup>Ra, and <sup>228</sup>Ra/<sup>226</sup>Ra activity ratios. We tested the <sup>228</sup>Th/<sup>228</sup>Ra method on spill sites in North Dakota and West Virginia,
where the dates of the spills are known. The <sup>228</sup>Th/<sup>228</sup>Ra method yields ages similar to the documented spill ages
and can reveal the initial <sup>228</sup>Ra/<sup>226</sup>Ra ratios
of the spill waters, validating the notion that Ra isotopes and their
decay products in contaminated soils and sediments can reveal the
ages and origins of spills
Water Footprint of Hydraulic Fracturing
We
evaluated the overall water footprint of hydraulic fracturing
of unconventional shale gas and oil throughout the United States based
on integrated data from multiple database sources. We show that between
2005 and 2014, unconventional shale gas and oil extraction used 708
billion liters and 232 billion liters of water, respectively. From
2012 to 2014, the annual water use rates were 116 billion liters per
year for shale gas and 66 billion liters per year for unconventional
oil. Integrated data from 6 to 10 years of operation yielded 803 billion
liters of combined flowback and produced water from unconventional
shale gas and oil formations. While the hydraulic fracturing revolution
has increased water use and wastewater production in the United States,
its water use and produced water intensity is lower than other energy
extraction methods and represents only a fraction of total industrial
water use nationwide
Evidence for Coal Ash Ponds Leaking in the Southeastern United States
Coal combustion
residuals (CCRs), the largest industrial waste
in the United States, are mainly stored in surface impoundments and
landfills. Here, we examine the geochemistry of seeps and surface
water from seven sites and shallow groundwater from 15 sites in five
states (Tennessee, Kentucky, Georgia, Virginia, and North Carolina)
to evaluate possible leaking from coal ash ponds. The assessment for
groundwater impacts at the
14 sites in North Carolina was based on state-archived monitoring
well data. Boron and strontium exceeded background values of 100 and
150 μg/L, respectively, at all sites, and the high concentrations
were associated with low δ<sup>11</sup>B (−9‰
to +8‰) and radiogenic <sup>87</sup>Sr/<sup>86</sup>Sr
(0.7070 to 0.7120) isotopic fingerprints that are characteristic of
coal ash at all but one site. Concentrations of CCR contaminants,
including SO<sub>4</sub>, Ca, Mn, Fe, Se, As, Mo, and V above background
levels, were also identified at all sites, but contamination levels
above drinking water and ecological standards were observed in 10
out of 24 samples of impacted surface water. Out of 165 monitoring
wells, 65 were impacted with high B levels and 49 had high CCR-contaminant
levels. Distinct isotope fingerprints, combined with elevated levels
of CCR tracers, provide strong evidence for the leaking of coal ash ponds to adjacent surface water and shallow groundwater. Given the
large number of coal ash impoundments throughout the United States,
the systematic evidence for leaking of coal ash ponds shown in this
study highlights potential environmental risks from unlined coal ash ponds
Naturally Occurring Radioactive Materials in Uranium-Rich Coals and Associated Coal Combustion Residues from China
Most coals in China
have uranium concentrations up to 3 ppm, yet
several coal deposits are known to be enriched in uranium. Naturally
occurring radioactive materials (NORM) in these U-rich coals and associated
coal combustion residues (CCRs) have not been well characterized.
Here we measure NORM (Th, U, <sup>228</sup>Ra, <sup>226</sup>Ra, and <sup>210</sup>Pb) in coals from eight U-rich coal deposits in China and
the associated CCRs from one of these deposits. We compared NORM in
these U-rich coals and associated CCRs to CCRs collected from the
Beijing area and natural loess sediments from northeastern China.
We found elevated U concentrations (up to 476 ppm) that correspond
to low <sup>232</sup>Th/<sup>238</sup>U and <sup>228</sup>Ra/<sup>226</sup>Ra activity ratios (≪1) in the coal samples. <sup>226</sup>Ra and <sup>228</sup>Ra activities correlate with <sup>238</sup>U and <sup>232</sup>Th activities, respectively, and <sup>226</sup>Ra activities correlate well with <sup>210</sup>Pb activities across
all coal samples. We used measured NORM activities and ash yields
in coals to model the activities of CCRs from all U-rich coals analyzed
in this study. The activities of measured and modeled CCRs derived
from U-rich coals exceed the standards for radiation in building materials,
particularly for CCRs originating from coals with U > 10 ppm. Since
beneficial use of high-U Chinese CCRs in building materials is not
a suitable option, careful consideration needs to be taken to limit
potential air and water contamination upon disposal of U- and Ra-rich
CCRs
Sources of Radium Accumulation in Stream Sediments near Disposal Sites in Pennsylvania: Implications for Disposal of Conventional Oil and Gas Wastewater
In
Pennsylvania, Appalachian oil and gas wastewaters (OGW) are
permitted for release to surface waters after some treatment by centralized
waste treatment (CWT) facilities. While this practice was largely
discontinued in 2011 for unconventional Marcellus OGW at facilities
permitted to release high salinity effluents, it continues for conventional
OGW. This study aimed to evaluate the environmental implications of
the policy allowing the disposal of conventional OGW. We collected
stream sediments from three disposal sites receiving treated OGW between
2014 and 2017 and measured <sup>228</sup>Ra, <sup>226</sup>Ra, and
their decay products, <sup>228</sup>Th and <sup>210</sup>Pb, respectively.
We consistently found elevated activities of <sup>228</sup>Ra and <sup>226</sup>Ra in stream sediments in the vicinity of the outfall (total
Ra = 90–25,000 Bq/kg) compared to upstream sediments (20–80
Bq/kg). In 2015 and 2017, <sup>228</sup>Th/<sup>228</sup>Ra activity
ratios in sediments from two disposal sites were relatively low (0.2–0.7),
indicating that a portion of the Ra has accumulated in the sediments
in recent (<3) years, when no unconventional Marcellus OGW was
reportedly discharged. <sup>228</sup>Ra/<sup>226</sup>Ra activity
ratios were also higher than what would be expected solely from disposal
of low <sup>228</sup>Ra/<sup>226</sup>Ra Marcellus OGW. Based on these
variations, we concluded that recent disposal of treated conventional
OGW is the source of high Ra in stream sediments at CWT facility disposal
sites. Consequently, policies pertaining to the disposal of only unconventional
fluids are not adequate in preventing radioactive contamination in
sediments at disposal sites, and the permission to release treated
Ra-rich conventional OGW through CWT facilities should be reconsidered
Radium and Barium Removal through Blending Hydraulic Fracturing Fluids with Acid Mine Drainage
Wastewaters
generated during hydraulic fracturing of the Marcellus
Shale typically contain high concentrations of salts, naturally occurring
radioactive material (NORM), and metals, such as barium, that pose
environmental and public health risks upon inadequate treatment and
disposal. In addition, fresh water scarcity in dry regions or during
periods of drought could limit shale gas development. This paper explores
the possibility of using alternative water sources and their impact
on NORM levels through blending acid mine drainage (AMD) effluent
with recycled hydraulic fracturing flowback fluids (HFFFs). We conducted
a series of laboratory experiments in which the chemistry and NORM
of different mix proportions of AMD and HFFF were examined after reacting
for 48 h. The experimental data combined with geochemical modeling
and X-ray diffraction analysis suggest that several ions, including
sulfate, iron, barium, strontium, and a large portion of radium (60–100%),
precipitated into newly formed solids composed mainly of Sr barite
within the first ∼10 h of mixing. The results imply that blending
AMD and HFFF could be an effective management practice for both remediation
of the high NORM in the Marcellus HFFF wastewater and beneficial utilization
of AMD that is currently contaminating waterways in northeastern U.S.A
Impacts of Shale Gas Wastewater Disposal on Water Quality in Western Pennsylvania
The
safe disposal of liquid wastes associated with oil and gas
production in the United States is a major challenge given their large
volumes and typically high levels of contaminants. In Pennsylvania,
oil and gas wastewater is sometimes treated at brine treatment facilities
and discharged to local streams. This study examined the water quality
and isotopic compositions of discharged effluents, surface waters,
and stream sediments associated with a treatment facility site in
western Pennsylvania. The elevated levels of chloride and bromide,
combined with the strontium, radium, oxygen, and hydrogen isotopic
compositions of the effluents reflect the composition of Marcellus
Shale produced waters. The discharge of the effluent from the treatment
facility increased downstream concentrations of chloride and bromide
above background levels. Barium and radium were substantially (>90%)
reduced in the treated effluents compared to concentrations in Marcellus
Shale produced waters. Nonetheless, <sup>226</sup>Ra levels in stream
sediments (544–8759 Bq/kg) at the point of discharge were ∼200
times greater than upstream and background sediments (22–44
Bq/kg) and above radioactive waste disposal threshold regulations,
posing potential environmental risks of radium bioaccumulation in
localized areas of shale gas wastewater disposal
A Critical Review of the Risks to Water Resources from Unconventional Shale Gas Development and Hydraulic Fracturing in the United States
The rapid rise of
shale gas development through horizontal drilling
and high volume hydraulic fracturing has expanded the extraction of
hydrocarbon resources in the U.S. The rise of shale gas development
has triggered an intense public debate regarding the potential environmental
and human health effects from hydraulic fracturing. This paper provides
a critical review of the potential risks that shale gas operations
pose to water resources, with an emphasis on case studies mostly from
the U.S. Four potential risks for water resources are identified:
(1) the contamination of shallow aquifers with fugitive hydrocarbon
gases (i.e., stray gas contamination), which can also potentially
lead to the salinization of shallow groundwater through leaking natural
gas wells and subsurface flow; (2) the contamination of surface water
and shallow groundwater from spills, leaks, and/or the disposal of
inadequately treated shale gas wastewater; (3) the accumulation of
toxic and radioactive elements in soil or stream sediments near disposal
or spill sites; and (4) the overextraction of water resources for
high-volume hydraulic fracturing that could induce water shortages
or conflicts with other water users, particularly in water-scarce
areas. Analysis of published data (through January 2014) reveals evidence
for stray gas contamination, surface water impacts in areas of intensive
shale gas development, and the accumulation of radium isotopes in
some disposal and spill sites. The direct contamination of shallow
groundwater from hydraulic fracturing fluids and deep formation waters
by hydraulic fracturing itself, however, remains controversial
Enhanced Formation of Disinfection Byproducts in Shale Gas Wastewater-Impacted Drinking Water Supplies
The disposal and leaks of hydraulic
fracturing wastewater (HFW)
to the environment pose human health risks. Since HFW is typically
characterized by elevated salinity, concerns have been raised whether
the high bromide and iodide in HFW may promote the formation of disinfection
byproducts (DBPs) and alter their speciation to more toxic brominated
and iodinated analogues. This study evaluated the minimum volume percentage
of two Marcellus Shale and one Fayetteville Shale HFWs diluted by
fresh water collected from the Ohio and Allegheny Rivers that would
generate and/or alter the formation and speciation of DBPs following
chlorination, chloramination, and ozonation treatments of the blended
solutions. During chlorination, dilutions as low as 0.01% HFW altered
the speciation toward formation of brominated and iodinated trihalomethanes
(THMs) and brominated haloacetonitriles (HANs), and dilutions as low
as 0.03% increased the overall formation of both compound classes.
The increase in bromide concentration associated with 0.01–0.03%
contribution of Marcellus HFW (a range of 70–200 μg/L
for HFW with bromide = 600 mg/L) mimics the increased bromide levels
observed in western Pennsylvanian surface waters following the Marcellus
Shale gas production boom. Chloramination reduced HAN and regulated
THM formation; however, iodinated trihalomethane formation was observed
at lower pH. For municipal wastewater-impacted river water, the presence
of 0.1% HFW increased the formation of <i>N</i>-nitrosodimethylamine
(NDMA) during chloramination, particularly for the high iodide (54
ppm) Fayetteville Shale HFW. Finally, ozonation of 0.01–0.03%
HFW-impacted river water resulted in significant increases in bromate
formation. The results suggest that total elimination of HFW discharge
and/or installation of halide-specific removal techniques in centralized
brine treatment facilities may be a better strategy to mitigate impacts
on downstream drinking water treatment plants than altering disinfection
strategies. The potential formation of multiple DBPs in drinking water
utilities in areas of shale gas development requires comprehensive
monitoring plans beyond the common regulated DBPs