INITIAL ANNUAL GROUNDWATER MONITORING AND CORRECTIVE ACTION REPORT FOR YEAR 2017 FOR ASH BASIN 6 U.S. EPA COAL COMBUSTION RESIDUALS (CCR) RULE BRUNNER ISLAND STEAM ELECTRIC STATION EAST MANCHESTER TOWNSHIP YORK COUNTY, PENNSYLVANIA Prepared for: BRUNNER ISLAND, LLC East Manchester Township York County, Pennsylvania Prepared by: West Chester, PA and the V.F. BRITTON GROUP, LLC Wayne, PA AGC Project No: 2015-3397 January 31, 2018
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INITIAL ANNUAL GROUNDWATER MONITORING AND CORRECTIVE ACTION REPORT FOR YEAR 2017
FOR ASH BASIN 6
U.S. EPA COAL COMBUSTION RESIDUALS (CCR) RULE BRUNNER ISLAND STEAM ELECTRIC STATION
EAST MANCHESTER TOWNSHIP YORK COUNTY, PENNSYLVANIA
Prepared for:
BRUNNER ISLAND, LLC East Manchester Township York County, Pennsylvania
LIST OF TABLES TABLE 1 CCR Rule Monitoring Well Construction Overview 2 Groundwater Analytical Testing Results
LIST OF FIGURES FIGURE 1 Site Location Map 2 Monitoring Well Locations for CCR Groundwater Monitoring 3 Schematic Conceptual Cross Section Local Geology 4 Schematic Cross Section Conceptual Regional Groundwater Movement – Vertical
Component 5 Existing Groundwater Elevation Contour – Active Discharge 6 Static Groundwater Elevation Contour – No Active Discharge to Basin 6 7 MW-6-3 Area 8 Hydrogeologic Cross Section - MW-6-3 Area
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1.0 INTRODUCTION
1.1 PURPOSE
The United States Environmental Protection Agency (USEPA) issued 40 CFR 257, Subpart D,
Disposal of Coal Combustion Residuals from Electric Utilities (CCR Rule) on April 17, 2015. The
CCR Rule regulates disposal of coal combustion residuals (CCR) in CCR landfills and
impoundments. Advanced GeoServices Corp. and the V.F. Britton Group, LLC (Advanced
GeoServices) have prepared this Initial Annual Groundwater Monitoring and Corrective Action
(GWMCA) Report for Ash Basin 6, a state-permitted ash impoundment, located at the Brunner
Island Stream Electric Station (Brunner) in East Manchester Township, York County,
Pennsylvania.
The CCR Rule states the following requirements for the GWMCA Report (40 CFR §257.90):
(e) Annual groundwater monitoring and corrective action report. For existing CCR landfills and existing CCR surface impoundments, no later than January 31, 2018, and annually thereafter, the owner or operator must prepare an annual groundwater monitoring and corrective action report. For new CCR landfills, new CCR surface impoundments, and all lateral expansions of CCR units, the owner or operator must prepare the initial annual groundwater monitoring and corrective action report no later than January 31 of the year following the calendar year a groundwater monitoring system has been established for such CCR unit as required by this subpart, and annually thereafter. For the preceding calendar year, the annual report must document the status of the groundwater monitoring and corrective action program for the CCR unit, summarize key actions completed, describe any problems encountered, discuss actions to resolve the problems, and project key activities for the upcoming year. For purposes of this section, the owner or operator has prepared the annual report when the report is placed in the facility’s operating record as required by § 257.105(h)(1). At a minimum, the annual groundwater monitoring and corrective action report must contain the following information, to the extent available:
(1) A map, aerial image, or diagram showing the CCR unit and all background (or upgradient) and downgradient monitoring wells, to include the well identification numbers, that are part of the groundwater monitoring program for the CCR unit; (2) Identification of any monitoring wells that were installed or decommissioned during the preceding year, along with a narrative description of why those actions were taken;
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(3) In addition to all the monitoring data obtained under §§ 257.90 through 257.98, a summary including the number of groundwater samples that were collected for analysis for each background and downgradient well, the dates the samples were collected, and whether the sample was required by the detection monitoring or assessment monitoring programs; (4) A narrative discussion of any transition between monitoring programs (e.g., the date and circumstances for transitioning from detection monitoring to assessment monitoring in addition to identifying the constituent(s) detected at a statistically significant increase over background levels); and (5) Other information required to be included in the annual report as specified in §§ 257.90 through 257.98.
(f) The owner or operator of the CCR unit must comply with the recordkeeping requirements specified in § 257.105(h), the notification requirements specified in § 257.106(h), and the internet requirements specified in § 257.107(h).
This Report has been prepared to satisfy these requirements.
1.2 SITE LOCATION
The Brunner Island Steam Electric Station (Brunner) is an active electric generation facility located
on the west bank of the Susquehanna River in East Manchester Township, York County,
Pennsylvania. Figure 1 provides a site location map for the facility. Brunner is owned and
operated by Brunner Island, LLC. Ash Basin 6 (Basin 6) is located on the southern end of Brunner
Island and is bordered to the east by the Susquehanna River and to the west by Black Gut Creek.
Basin 6 is an active coal ash impoundment. When the plant is fully operational, process water
discharges into Basin 6, where sediments settle in a settling pond. Water is then routed to a
polishing (clarifying) pond located directly southeast of the settling pond. Treated water
discharges to the Susquehanna River via an NPDES-permitted outfall. The remaining portion of
water recharges into Basin 6, creating a groundwater mound and subsequent radial flow outward
from the basin footprint. Figure 2 provides a general site plan showing the existing CCR Rule
groundwater monitoring well network that currently exists within the area of Basin 6.
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Basin 6 consists of earthen berms around the perimeter of the basin which have been lined with an
impervious clay material on the inside of the berms. The bottom of the basin has not been lined
and allows some of the water to infiltrate though the bottom of the basin. Prior to the development
of the area, sediments from the Susquehanna River had built up Brunner Island. These sediments
consist of a silty clay material overlaying a sand and gravel layer. This unconsolidated material
lies directly on top of a fractured bedrock which has been carved over time by the Susquehanna
River. It is understood that the earthen berms constructed for Basin 6 were constructed directly
on top of the bedrock material, and that most of the unconsolidated materials underlying the berm
footprint were removed. Figure 3 provides a schematic cross-section through the Basin 6 area.
Ash in Basin 6 is currently being excavated and beneficially used at an off-site location.
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2.0 GROUNDWATER MONITORING NETWORK
The CCR Rule also outlines well installation, development, sampling, and decommissioning
requirements. The CCR Rule requires the owner or operator to obtain a certification from a
qualified professional engineer stating that the groundwater monitoring system has been designed
and constructed as outlined above. A detailed description and justification for the Basin 6
groundwater monitoring network is detailed in the report entitled Groundwater Monitoring System
Plan (Advanced GeoServices, October 2017).
Basin 6 has been monitored for numerous years in accordance with state permit requirements and
there is a good understanding of the site characteristics, as described in the following sections.
2.1 GEOLOGIC SETTING
The Basin 6 site area is generally underlain by the Triassic Age New Oxford Formation which
consists of a shale unit and a conglomerate unit. The very southern tip of the site is underlain by
the Cambrian Age Ledger Formation which consists of dolomite. The contact between the Triassic
and Cambrian age rock is an apparent angular unconformity. The bedrock is overlain by native
sand and gravel and silty clay (see Figure 3).
The local bedrock geology is evident based on outcrops along the roadway and railroad tracks that
are west of Black Gut Creek. Several strike and dip measurements were collected from the
outcrops to identify the bedrock structural orientation. Based on the measurements, the bedding
of the New Oxford Formation has an average strike of N45°E and dips to the northwest
approximately 12°. Joint sets were evident in near vertical orientations perpendicular to the strike
orientation.
As discussed above, Basin 6 is surrounded by earthen berms that were constructed directly on the
surface of the bedrock. During the construction of these berms, overburden material (sand, gravel,
and silty -clay) were excavated to the top of bedrock in the area of the berms. This resulted in the
absence of overburden along the edge of the berm; however, the native overburden was untouched
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in the central portion of Basin 6 and coal ash material was placed directly on the overburden
material. Figure 3 provides a schematic cross section of Basin 6.
2.2 HYDROGEOLOGY 2.2.1 Regional Flow
Brunner Island (specifically the Basin 6 area) is located on an island, with the Susquehanna River
bordering the east side and a small tributary (Black Gut Creek) bordering the west side of the island
(see Figure 2). Topographic highlands exist to the west of Brunner Island with groundwater
moving from the highland recharge zone to the east toward Black Gut Creek locally and the
Susquehanna River regionally. Thus, Brunner Island is isolated hydrogeologically from the
topographic highlands to the west which also prevents potential contaminants emanating from
Brunner Island from migrating westward past Black Gut Creek and impacting properties west of
Brunner Island. The regional flow characteristics result in an upward vertical groundwater
gradient under the footprint of Brunner Island hindering the vertical migration of any potential
contaminants downward into the groundwater column. Figure 4 provides a schematic cross section
which shows the conceptual regional vertical groundwater movement associated with Basin 6.
2.2.2 Groundwater Movement
Under fully operational plant conditions, process water enters Basin 6. Based on review of site-
specific groundwater elevation data in March, April, June, and July 2017 and on groundwater
modeling completed for Basin 6, the plant process water that is discharged to the surface of Basin
6 is creating a groundwater mound under the basin with radial flow outward. It is estimated that
up to one-million gallons of water per day infiltrates into Basin 6 as a result of the plant process
water (estimated up to 5-million gallons/day) entering Basin 6. The majority of water discharges
though the NPDES-permitted outfall.
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Figure 5 provides a mean groundwater elevation contour map of the four sets of water level data
collected in March, April, June, and July 2017. It should be noted that vertical groundwater
elevation fluctuation is minimal and does not result in changes to the radial groundwater flow
characteristics indicated on Figure 5.
The average groundwater elevation below Basin 6 is 280 feet Mean Sea Level (ft MSL) which is
within the ash material and above the overburden material.
2.2.3 Water Bearing Zones
The CCR rule requires monitoring of the upper-most aquifer under the CCR unit. As discussed
above, Basin 6 is underlain by a native silty clay and a sand and gravel layer. This overburden
material overlies the fractured bedrock system. Piezometers installed near the northwest corner of
Basin 6 penetrate both the overburden and the bedrock material. Based on water level data
collected in these paired piezometers, it was evident that a slight upward vertical gradient exists
typical of discharge zone hydraulics; a characteristic that would be expected in this area.
Evaluation of this area suggests that the potentiometric surface observed in the overburden and
bedrock wells is connected. A separate overburden water bearing zone does not exist. Based on
published geologic data, it is apparent that the bottom of the aquifer can range from 100 to 400
feet below the ground surface where the fractures in the bedrock (secondary porosity) no longer
transmit groundwater.
Based on site-specific data collected from the area, the hydraulic conductivity of the bedrock zone
is transitional with depth with approximate upper, middle, and deep values of 0.24, 7.54, and 0.91
feet per day, respectively. However, this is not consistent over the entire Brunner Island area.
Low hydraulic conductivity in the upper portion of the bedrock has been suggested in geologic
publications to be the result of silt and clay filling in the shallow rock fractures which reduce the
conductivity. Clay-filled fractures in the bedrock were generally not observed on the site.
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2.3 CCR-RULE MONITORING WELL NETWORK OVERVIEW
The CCR rule states that wells monitoring a CCR unit must be installed in the upper most aquifer.
Overburden and bedrock piezometers were previously installed on the perimeter of the northwest
portion of Basin 6 (see Figure 7). Water levels in paired overburden wells and the bedrock wells
proximate to the northwest corner of Basin 6 show similar water elevations with a slight upward
vertical gradient. Figure 8 provides a hydrogeological cross-section through this area. Further
evaluation of this area suggests that a separate water-bearing zone does not exist in the overburden
material, but rather that the water levels observed in the overburden wells/piezometers are actually
the potentiometric surface of the bedrock water-bearing zone.
As indicated in Figure 5, the structure of Ash Basin 6 results in a radial flow pattern. There is no
appropriate location on the island for a background well. Therefore, a new background well was
installed at an off-site location, with general concurrence from the Pennsylvania Department of
Environmental Protection (PADEP).
Eight (8) monitoring wells (including 2 new wells, MW-6-7 and MW-6-8 installed in March 2016)
located near the perimeter of the basin and one (1) new off-site background well (MW-BG-1) have
been selected for use in the groundwater detection monitoring plan. The general well construction
for these nine (9) wells is provided on Table 1, and their locations are shown on Figure 2.
2.4 MONITORING WELL INSTALLATION
Two (2) new wells (named MW-6-7 and MW-6-8) adjacent to Basin 6, and the new off-site well
MW-BG-1 were installed, in accordance with appropriate state regulations and in conformance
with the CCR rule, by a licensed monitoring well drilling contractor during March 2016. Table 1
provides the construction of these wells, and Figure 2 provides the well locations. The new 4-inch
wells were, screened to monitor the uppermost aquifer at the site and constructed in a similar
fashion to the preexisting site wells.
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Upon completion of the well installation activities, the wells were developed to clear the wells of
turbidity. The pumping rate was kept low to promote an approximate 50% drawdown of the static
water level (based on the static water level to the bottom of the well).
The wells have new dedicated low-flow bladder pumps installed by Talen personnel, so that the
pump’s intakes are positioned in the center of the well screen interval. Tubing and fittings were
installed at the well head in the same manner as the existing wells for future sampling events.
HydraSleeve sampling may be utilized at some future date (if the Pennsylvania Department of
Environmental Protection (PADEP) concurs.
The new monitoring wells were surveyed by a Pennsylvania licensed professional surveyor for
their PVC casing elevation and horizontal location. The results of the survey are presented on
Table 1.
2.5 WATER LEVEL MEASUREMENT
Groundwater level measurements were collected for each groundwater sampling event in 2017
prior to purging (March, April, June, and July 2017). These measurements were performed by
using an electronic depth-to-water meter and measured to the nearest 0.01 feet from the indicated
survey mark at the top of each PVC well casing identified in Table 1. This procedure allows a
depth measurement from the survey mark to the groundwater table to be converted to a
groundwater table elevation. Results of the data are discussed in Section 2.2.2.
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3.0 GROUNDWATER SAMPLING Eight (8) rounds of groundwater samples were collected and tested for Appendix III and Appendix
IV parameters to characterize “baseline” conditions. The parameters, or constituents, associated
with each appendix are provided below:
Appendix III Parameters Appendix IV Parameters Boron Calcium Chloride Fluoride pH Sulfate Total Dissolved Solids (TDS)
The sampling events occurred during the following periods:
April 2016 June 2016 September 2016 December 2016
March 2017 April 2017 June 2017 July 2017
A detection monitoring event (Sample #9) was completed in September 2017 and analyzed for
Appendix III parameters. The September 2017 detection monitoring event was used for statistical
evaluation described in Section 4.0 of this Report.
Sample collection was performed in accordance with Talen procedures for low-flow sampling. In
addition to the CCR Rule Appendix III constituents mentioned above, groundwater depth, field
pH, field Redox, field turbidity, total alkalinity, and iron were analyzed. For every 10 or fewer
groundwater sampling points collected during a CCR Rule sampling event at Basin 6, a duplicate
sample was collected. Matrix spike and matrix spike duplicates were included in analytical batches
per specific test method requirements to assess matrix effects on laboratory precision and accuracy.
The results of laboratory testing are provided as Table 2.
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4.0 STATISTICAL ANALYSIS
40 C.F.R. § 257.93(f) defines the statistical analysis methods to determine whether a statistically
significant increase (SSI) of any Appendix III parameter has occurred. 40 C.F.R. § 257.93(h) (1)
further instructs that the SSI for each parameter at each well will statistically be compared to
“background” data. The sampling events required to commence the SSI analysis (as scheduled
for early 2018) were completed in 2017. .
A Certification defining the Statistical Method, Selection of Statistical Method Certification
Groundwater Monitoring and Analysis Program for Ash Basin 6 (Advanced GeoServices, October
2017), for evaluating possible statistically-significant increases (SSI) in concentrations of
Appendix III groundwater constituents, was placed on the Talen CCR Rule publicly-accessible
website.
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5.0 CORRECTIVE ACTIONS
Ash above the water table within the basin is currently being excavated and the ash is being
beneficially reused off-site. It is anticipated that this process will take 15 years to complete (from
start to finish). Further actions, if and as needed, regarding assessment and/or corrective action,
will be described in future CCR-rule required documents.
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6.0 ANTICIPATED UPCOMING ACTIVITIES
During the 2018 calendar year, the following activities are anticipated to occur relative to
implementation of groundwater-related requirements of the CCR Rule:
Complete Statistical Analysis to determine whether an SSI has occurred.
If an SSI has not occurred, Detection Monitoring and reporting will continue
through 2018.
If an SSI has occurred, the following would occur:
Establish and implement an Assessment Monitoring Program (AMP);
Provide required notices that an AMP has been established;
Establish Groundwater Protection Standards (GWPS) for Basin 6; and
Determine whether constituents are detected as statistically significant
levels (SSL) above the GWPS.
Other actions may also be completed, if/as necessary, in accordance with the CCR regulations,
depending on the results of the above analyses.
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7.0 CERTIFICATION
CCR Impoundment Information Name: Ash Basin 6 Operator: Brunner Island, LLC Address: 1400 Wago Road, York Haven, PA 17370
Qualified Professional Engineer: Name: Christopher T. Reitman, P.E. Company: Advanced GeoServices Corp.
I, Christopher Reitman, certify that this Initial Annual Groundwater Monitoring and Corrective Measures Report for 2017 for Ash Basin 6 has been compiled to meet the requirements of the Coal Combustion Residual (CCR) rule 40 CFR §257.90 (e). I am a duly licensed Professional Engineer under the laws of the Commonwealth of Pennsylvania.
Print Name: _________________________
Signature: __________________________
Date: ______________________________
License Number: P.E. 040717 My license renewal date is September 30, 2019
Qualified Professional Geologist: Name: Val F. Britton Company: V.F. Britton Group, LLC
I, Val F. Britton, certify that this Initial Annual Groundwater Monitoring and Corrective Measures Report for 2017 for Ash Basin 6 has been compiled to meet the requirements of the Coal Combustion Residual (CCR) rule 40 CFR §257.90 (e). I am a duly licensed Professional Geologist under the laws of the Commonwealth of Pennsylvania.
Print Name: _________________________
Signature: __________________________
Date: ______________________________
License Number: P.G. 001358 My license renewal date is September 30, 2019
Northings, Eastings, and TOIC for MW-BG-1 was provided to Advanced GeoServices by Cross Roads Surveying
Northings, Eastings, and TOIC for all wells except MW-BG-1 were developed by Kimball Surveyingbased on surveying completed on June 5-7 and July 18, 2017 for V.F. Britton Group
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample Location MW-6-2 MW-6-2D MW-6-3N MW-6-4 MW-6-6 PZ-6-5B MW-6-7 MW-6-8 MW-8-2 MW-BG-1Sample Name BR 6-2 BR 6-2D BR 6-3N BR 6-4 BR 6-6 BR PZ65B BR 6-7 BR 6-8 BR 8-2 BR BG-1Lab ID 2016003373 2016003374 2016003375 2016003376 2016003377 2016003378 2016003379 2016003380 2016003381 2016003382Date Sampled 4/26/2016 8:11 4/26/2016 8:11 4/26/2016 14:45 4/26/2016 11:47 4/26/2016 8:08 4/26/2016 10:40 4/26/2016 15:05 4/26/2016 12:26 4/26/2016 11:24 4/26/2016 8:37Matrix Groundwater Groundwater Groundwater Groundwater Groundwater Groundwater Groundwater Groundwater Groundwater GroundwaterRemarks FD of BR 6-2Event ID Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1 Basin 6 Round 1Parameters Units Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQ Result Q LOQAppendix III ParametersConventionalsChloride mg/L 23.2 0.5 23.4 0.5 21.6 0.5 20.6 0.5 10.8 0.5 23.6 1 21.2 0.5 3.7 0.5 29.1 0.5 15.6 0.5Fluoride mg/L 0.23 0.05 0.23 0.05 1.35 0.05 0.11 0.05 0.08 0.05 0.13 0.1 0.53 0.05 0.04 J 0.05 0.98 0.05 0.02 J 0.05Lab pH * S.U. 6.69 1.68 6.69 1.68 7.61 1.68 7.58 1.68 6.95 1.68 7.22 1.68 6.41 1.68 6.7 1.68 6.95 1.68 7.33 1.68Sulfate mg/L 45.6 3 46 3 113 3 126 3 102 3 381 6 175 3 30.3 3 135 3 23.3 3Total Dissolved Solids mg/L 301 15 299 15 304 15 305 15 500 15 756 15 351 15 258 15 340 15 372 15Metals, Total Boron, Total µg/L 192 20 191 20 423 20 143 20 172 20 332 20 776 20 18.7 J 20 442 20 12.4 J 20Calcium, Total mg/L 51.3 0.2 51.7 0.2 69.8 0.2 65.1 0.2 134 0.2 145 0.2 82.3 0.2 52.2 0.2 76.7 0.2 111 0.2Metals, DissolvedBoron, Dissolved µg/L 196 20 192 20 413 20 147 20 170 20 335 20 785 20 24.8 20 451 20 15.7 J 20Calcium, Dissolved mg/L 51.9 0.2 51.3 0.2 69.5 0.2 65.9 0.2 133 0.2 147 0.2 82.7 0.2 51.4 0.2 77.1 0.2 111 0.2Field ParameterspH field reading ** S.U. 6.4 6.4 6.99 7.18 6.77 7.07 6.21 6.41 7.05 6.7Appendix IV ParametersConventionalsFluoride mg/L 0.23 0.05 0.23 0.05 1.35 0.05 0.11 0.05 0.08 0.05 0.13 0.1 0.53 0.05 0.04 J 0.05 0.98 0.05 0.02 J 0.05Radiochemistry ***Radium-226 pCi/L 0.322+/-0.300 0.000+/-0.280 U 0.218+/-0.371 U -0.050+/-0.260 U 0.225+/-0.382 U 0.151+/-0.231 U -0.053+/-0.242 U 0.241+/-0.473 U 0.995+/-0.564 0.156+/-0.368 URadium-228 pCi/L 0.212+/-0.417 U 0.127+/-0.318 U 0.0136+/-0.316 U 0.234+/-0.310 U 0.325+/-0.383 U 0.361+/-0.353 0.175+/-0.344 U 0.379+/-0.371 0.553+/-0.382 0.471+/-0.357Metals, Total Antimony, total µg/L U 2 U 2 U 2 U 2 U 2 U 2 0.67 J 2 U 2 U 2 U 2Arsenic, total µg/L 1.21 0.5 1.19 0.5 228 0.5 0.914 0.5 0.495 J 0.5 0.489 J 0.5 1.46 0.5 0.848 0.5 0.13 J 0.5 0.102 J 0.5Barium, total µg/L 55.6 0.5 55.6 0.5 44.8 0.5 3.37 0.5 50 0.5 48.6 0.5 70.6 0.5 43 0.5 28 0.5 351 0.5Beryllium, total µg/L U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5Cadmium, total µg/L U 0.2 U 0.2 0.177 J 0.2 0.063 J 0.2 U 0.2 0.042 J 0.2 0.148 J 0.2 U 0.2 0.237 0.2 U 0.2Chromium, total µg/L U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5Cobalt, total µg/L U 5 U 5 U 5 U 5 U 5 U 5 U 5 3.086 J 5 U 5 U 5Lead, total µg/L U 0.5 U 0.5 0.106 J 0.5 2.2 0.5 U 0.5 U 0.5 U 0.5 0.149 J 0.5 U 0.5 U 0.5Lithium, total µg/L 20.9 2 20.1 2 70 2 3.36 2 9.61 2 11.2 2 64.8 2 2.99 2 21.1 2 5.96 2Mercury, total µg/L 0.012 J 0.05 U 0.05 0.019 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05Molybdenum, total µg/L 2.236 J 5 2.259 J 5 306 5 140 5 U 5 61.1 5 239 5 1.71 J 5 287 5 U 5Selenium, total µg/L 0.068 J 0.2 0.044 J 0.2 0.078 J 0.2 0.043 J 0.2 U 0.2 U 0.2 0.178 J 0.2 0.154 J 0.2 U 0.2 U 0.2Thallium, total µg/L U 0.5 U 0.5 0.202 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.137 J 0.5 U 0.5 U 0.5Metals, DissolvedAntimony, dissolved µg/L U 2 U 2 U 2 U 2 U 2 U 2 0.623 J 2 U 2 U 2 U 2Arsenic, dissolved µg/L 0.936 0.5 0.79 0.5 229 0.5 0.972 0.5 0.235 J 0.5 0.463 J 0.5 1.4 0.5 0.836 0.5 0.196 J 0.5 0.175 J 0.5Barium, dissolved µg/L 49.4 0.5 48.6 0.5 45.3 0.5 3.45 0.5 44.9 0.5 49.8 0.5 67.5 0.5 42.2 0.5 28.3 0.5 353 0.5Beryllium, dissolved µg/L U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5Cadmium, dissolved µg/L U 0.2 U 0.2 0.168 J 0.2 0.077 J 0.2 U 0.2 0.047 J 0.2 0.199 J 0.2 U 0.2 0.235 0.2 U 0.2Chromium, dissolved µg/L U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5Cobalt, dissolved µg/L U 5 U 5 U 5 U 5 U 5 U 5 U 5 3.167 J 5 U 5 U 5Lead, dissolved µg/L U 0.5 U 0.5 U 0.5 0.121 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5Lithium, dissolved µg/L 20.4 2 19.8 2 69.5 2 3.51 2 9.67 2 11.4 2 62.6 2 3.02 2 21.1 2 6.01 2Mercury, dissolved µg/L 0.013 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05Molybdenum, dissolved µg/L 2.38 J 5 2.186 J 5 307 5 141 5 U 5 61.9 5 233 5 1.902 J 5 291 5 U 5Selenium, dissolved µg/L 0.075 J 0.2 U 0.2 0.082 J 0.2 0.04 J 0.2 U 0.2 0.04 J 0.2 0.206 0.2 0.063 J 0.2 U 0.2 U 0.2Thallium, dissolved µg/L 0.265 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.122 J 0.5 U 0.5 U 0.5 U 0.5
Notes:mg/L - milligrams per liter J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionµg/L - micrograms per liter LOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCS.U. - Standard Units NS - Not sampled * Laboratory pH analyzed outside of the method hold timepCi/L - picocuries per liter P- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationDL - Detection Limit Q - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncFD - Field Duplicate R - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
-0.326+/-1.13 U -0.256+/-1.04 U 0.111+/-0.525 U 0.0751+/-0.819 U -0.095+/-0.530 U 0.192+/-0.958 U 0.751+/-1.14 U -0.389+/-0.853 U -0.075+/-0.790 U -0.30+/-0.675 U0.615+/-0.391 0.435+/-0.364 0.399+/-0.446 0.147+/-0.334 U 0.340+/-0.341 U 0.251+/-0.302 U 0.0538+/-0.364 U 0.348+/-0.347 0.699+/-0.454 0.428+/-0.373
U 2 U 2 U 2 U 2 U 2 U 2 0.698 J 2 U 2 U 2 U 21.31 0.5 262 0.5 0.786 0.5 0.7 0.5 0.198 J 0.5 0.245 J 0.5 3.03 0.5 3.75 0.5 U 0.5 0.117 J 0.558.3 0.5 45.3 0.5 3.56 0.5 3.57 0.5 46.1 0.5 53.7 0.5 58.2 0.5 35.5 0.5 29 0.5 335 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.164 J 0.2 0.067 J 0.2 0.069 J 0.2 U 0.2 U 0.2 0.187 J 0.2 U 0.2 0.211 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 3.833 J 5 1.019 J 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
19.4 2 63 2 3.11 2 3.09 2 9.07 2 10.7 2 71.4 2 3.73 2 19.9 2 4.99 2U 0.05 0.015 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05
2.067 J 5 312 5 138 5 138 5 U 5 76.2 5 335 5 U 5 309 5 U 5U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.324 0.2 0.132 J 0.2 U 0.2 U 0.2U 0.5 U 0.5 U 0.5 0.196 J 0.5 U 0.5 U 0.5 0.214 J 0.5 0.135 J 0.5 U 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 0.679 J 2 U 2 U 2 U 20.704 0.5 244 0.5 0.927 0.5 0.791 0.5 0.169 J 0.5 0.271 J 0.5 2.94 0.5 3.3 0.5 U 0.5 0.123 J 0.546.8 0.5 45 0.5 3.64 0.5 3.68 0.5 46.5 0.5 52.9 0.5 57.4 0.5 35.2 0.5 28.6 0.5 341 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.155 J 0.2 0.052 J 0.2 0.055 J 0.2 U 0.2 0.044 J 0.2 0.144 J 0.2 U 0.2 0.2 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 3.669 J 5 1.012 J 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
19.6 2 64.3 2 3.28 2 3.06 2 8.51 2 10.8 2 71.3 2 3.94 2 19.7 2 4.77 2U 0.05 0.017 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05
2.322 J 5 315 5 139 5 141 5 U 5 77.2 5 333 5 1.132 J 5 302 5 U 50.05 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.367 0.2 0.155 J 0.2 U 0.2 U 0.2
0.113 J 0.5 U 0.5 U 0.5 U 0.5 0.105 J 0.5 U 0.5 0.186 J 0.5 U 0.5 U 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
0.202+/-0.627 U 0.232+/-0.267 U -0.397+/-0.455 U 0.0964+/-0.440 U 0.187+/-0.635 U -0.089+/-0.407 U 0.180+/-0.557 U 0.000+/-0.415 U 0.000+/-0.462 U 0.177+/-0.424 U0.865+/-0.471 1.04+/-0.631 0.513+/-0.397 0.779+/-0.505 -0.117+/-0.366 U 0.622+/-0.403 0.121+/-0.389 U 0.811+/-0.554 0.160+/-0.439 U 0.559+/-0.418
U 2 U 2 U 2 U 2 U 2 U 2 1.246 J 2 U 2 0.43 J 2 U 21.15 0.5 219 0.5 0.769 0.5 0.25 J 0.5 0.256 J 0.5 0.463 J 0.5 7.65 0.5 0.804 0.5 0.256 J 0.5 0.187 J 0.558.4 0.5 44.2 0.5 5.14 0.5 47.8 0.5 50.6 0.5 47.4 0.5 42 0.5 44.4 0.5 32.3 0.5 325 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.50.041 J 0.2 0.168 J 0.2 0.045 J 0.2 U 0.2 U 0.2 0.053 J 0.2 0.271 0.2 0.058 J 0.2 0.159 J 0.2 U 0.2
U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 1.746 J 5 1.063 J 5 U 5U 0.5 0.18 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.327 J 0.5 U 0.5 U 0.5 U 0.5
20 2 72.5 2 3.69 2 9.93 2 11 2 10.5 2 56.1 2 3.09 2 24.4 2 5.23 2U 0.05 0.01 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 0.01 J 0.05 U 0.05
2.207 J 5 317 5 108 5 U 5 U 5 76.3 5 323 5 1.248 J 5 306 5 U 5U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.469 0.2 0.166 J 0.2 0.041 J 0.2 U 0.2U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.461 J 0.5 U 0.5 0.12 J 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 1.229 J 2 U 2 U 2 U 21.01 0.5 220 0.5 0.746 0.5 0.221 J 0.5 0.236 J 0.5 0.487 J 0.5 7.38 0.5 0.77 0.5 0.197 J 0.5 0.185 J 0.552.5 0.5 43.8 0.5 5.04 0.5 48.3 0.5 46.8 0.5 46.6 0.5 43.3 0.5 44.4 0.5 31.6 0.5 329 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.165 J 0.2 0.06 J 0.2 U 0.2 U 0.2 U 0.2 0.257 0.2 0.056 J 0.2 0.205 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 1.602 J 5 U 5 U 5U 0.5 U 0.5 0.201 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
20 2 73.2 2 3.59 2 10.3 2 10.2 2 10.6 2 57.2 2 3.24 2 23.6 2 4.97 2U 0.05 0.017 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 0.01 J 0.05 U 0.05
2.213 J 5 313 5 106 5 U 5 U 5 76.8 5 325 5 1.623 J 5 312 5 U 5U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.445 0.2 0.117 J 0.2 0.055 J 0.2 U 0.2U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.433 J 0.5 U 0.5 0.113 J 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
-0.199 +/-0.344 U -0.256 +/-0.356 U -0.062+/- 0.283 U -0.146 +/-0.451 U 0.128 +/- 0.292 U 0.133 +/- 0.303 U 0.514 +/- 0.597 U 0.133 +/- 0.489 U -0.063 +/-0.286 U -0.280 +/-0.337 U0.635 +/- 0.403 0.673 +/- 0.411 -0.376 +/-0.558 U 0.603 +/- 0.391 0.311 +/- 0.323 U 0.240 +/- 0.315 U 0.577 +/- 0.378 0.369 +/- 0.425 U 0.708 +/- 0.429 0.723 +/- 0.386
U 2 U 2 U 2 U 2 U 2 U 2 1.025 J 2 U 2 U 2 U 20.977 0.5 1.06 0.5 218 0.5 0.78 0.5 0.25 J 0.5 0.461 J 0.5 5.19 0.5 0.444 J 0.5 0.197 J 0.5 0.176 J 0.554.9 0.5 55.9 0.5 43.7 0.5 5.46 0.5 39.4 0.5 47.5 0.5 49.3 0.5 51.8 0.5 30.2 0.5 327 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 U 0.2 0.121 J 0.2 0.074 J 0.2 U 0.2 0.047 J 0.2 0.243 0.2 0.054 J 0.2 0.237 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 0.137 J 0.5 U 0.5 U 0.5 U 0.5 0.108 J 0.5 U 0.5 U 0.5
20.4 2 20.3 2 75 2 3.73 2 10.5 2 11.8 2 63.8 2 2.96 2 23 2 5.06 20.014 J 0.05 U 0.05 0.011 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.052.399 J 5 2.479 J 5 331 5 114 5 U 5 77.3 5 286 5 U 5 326 5 U 50.073 J 0.2 0.043 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 1.44 0.2 0.146 J 0.2 0.041 J 0.2 U 0.20.147 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.226 J 0.5 U 0.5 U 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 1.009 J 2 U 2 U 2 U 21.03 0.5 0.994 0.5 217 0.5 0.727 0.5 0.162 J 0.5 0.425 J 0.5 5.19 0.5 0.374 J 0.5 0.215 J 0.5 0.188 J 0.554.5 0.5 54.2 0.5 43.3 0.5 5.51 0.5 38.7 0.5 54.2 0.5 49.3 0.5 53.8 0.5 30.9 0.5 326 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 U 0.2 0.14 J 0.2 0.073 J 0.2 U 0.2 0.054 J 0.2 0.197 J 0.2 0.062 J 0.2 0.263 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5
0.102 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.520.2 2 20.3 2 75.9 2 3.72 2 10.5 2 13.4 2 63.9 2 3.16 2 23.4 2 5.19 2
0.012 J 0.05 U 0.05 0.014 J 0.05 U 0.05 0.011 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.052.534 J 5 2.418 J 5 333 5 114 5 U 5 87.6 5 288 5 U 5 329 5 U 50.072 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 1.39 0.2 0.121 J 0.2 U 0.2 U 0.2
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.223 J 0.5 U 0.5 U 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2 oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
0.122 +/- 0.447 U -0.135+/- 0.417 U -0.130+/- 0.313 U 0.267 +/- 0.491 U -0.067+/- 0.349 U -0.129+/- 0.310 U 0.0643+/- 0.378 U 0.000 +/- 0.380 U -0.189+/- 0.289 U -0.116+/- 0.323 U0.405 +/- 0.333 0.205 +/- 0.319 U 0.776 +/- 0.405 0.315 +/- 0.341 U 0.250 +/- 0.294 U 0.483 +/- 0.338 1.09 +/- 0.480 0.624 +/- 0.385 0.563 +/- 0.363 0.378 +/- 0.305
U 2 U 2 U 2 U 2 U 2 U 2 0.52 J 2 U 2 U 2 U 20.932 0.5 221 0.5 223 0.5 0.724 0.5 0.418 J 0.5 0.348 J 0.5 9.82 0.5 0.324 J 0.5 0.149 J 0.5 0.13 J 0.547.4 0.5 42.7 0.5 42.6 0.5 3.71 0.5 40.9 0.5 45.1 0.5 125 0.5 40.1 0.5 28.3 0.5 335 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.144 J 0.2 0.139 J 0.2 0.057 J 0.2 U 0.2 0.048 J 0.2 0.072 J 0.2 U 0.2 0.185 J 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 0.109 J 0.5 U 0.5 U 0.5 0.169 J 0.5 U 0.5 U 0.5
20.2 2 67.5 2 67.2 2 3.34 2 9.79 2 11.1 2 43.7 2 3.05 2 18.6 2 4.99 2U 0.05 0.011 J 0.05 0.015 J 0.05 U 0.05 U 0.05 0.012 J 0.05 0.013 J 0.05 U 0.05 U 0.05 U 0.05
1.903 J 5 328 5 331 5 111 5 U 5 70 5 104 5 6.95 5 297 5 U 5U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.296 0.2 0.124 J 0.2 U 0.2 U 0.2U 0.5 0.15 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.3 J 0.5 0.108 J 0.5 0.101 J 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 0.446 J 2 U 2 U 2 U 20.905 0.5 217 0.5 216 0.5 0.787 0.5 0.226 J 0.5 0.393 J 0.5 9.23 0.5 0.259 J 0.5 0.174 J 0.5 0.178 J 0.5
44 0.5 41.5 0.5 40.9 0.5 3.56 0.5 38.4 0.5 44.2 0.5 119 0.5 38.3 0.5 29.1 0.5 325 0.5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
0.05 J 0.2 0.133 J 0.2 0.136 J 0.2 U 0.2 U 0.2 U 0.2 0.049 J 0.2 0.049 J 0.2 0.191 J 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
0.000 +/- 0.427 U -0.161 +/-0.246 U 0.181 +/- 0.355 U -0.060 +/-0.274 U 0.658 +/- 0.568 0.166 +/- 0.288 U 0.118 +/- 0.283 U 0.000 +/- 0.403 U 0.663 +/- 0.667 U 0.166 +/- 0.327 U0.623 +/- 0.336 0.634 +/- 0.375 0.495 +/- 0.429 0.579 +/- 0.412 0.322 +/- 0.357 U -0.238 +/-0.302 U 0.190 +/- 0.352 U -0.238 +/-0.353 U 0.575 +/- 0.343 0.448 +/- 0.355
U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 21.11 0.5 231 0.5 0.75 0.5 0.843 0.5 0.424 J 0.5 0.354 J 0.5 12.8 0.5 0.319 J 0.5 0.123 J 0.5 0.22 J 0.554.4 0.5 43.8 0.5 3.9 0.5 3.97 0.5 46.1 0.5 44.9 0.5 114 0.5 33.5 0.5 31.3 0.5 346 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.143 J 0.2 0.054 J 0.2 0.044 J 0.2 U 0.2 U 0.2 0.058 J 0.2 0.042 J 0.2 0.225 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 0.109 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
20 2 66.2 2 3.02 2 2.84 2 9.52 2 10 2 39.5 2 2.86 2 16.9 2 4.63 20.012 J 0.05 0.019 J 0.05 U 0.05 0.012 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.052.009 J 5 314 5 106 5 104 5 U 5 65.6 5 93 5 4.32 J 5 288 5 U 50.048 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.076 J 0.2 0.078 J 0.2 U 0.2 U 0.2
U 0.5 U 0.5 U 0.5 0.103 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 2 U 20.855 0.5 227 0.5 0.747 0.5 0.79 0.5 0.126 J 0.5 0.318 J 0.5 12.6 0.5 0.296 J 0.5 0.15 J 0.5 0.148 J 0.548.1 0.5 43 0.5 3.99 0.5 3.82 0.5 43.1 0.5 45.1 0.5 112 0.5 32.7 0.5 30.3 0.5 327 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.50.042 J 0.2 0.102 J 0.2 0.052 J 0.2 0.044 J 0.2 U 0.2 U 0.2 0.051 J 0.2 0.055 J 0.2 0.178 J 0.2 U 0.2
U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 0.113 J 0.5 0.112 J 0.5 0.113 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
19.7 2 65.2 2 3.04 2 2.81 2 9.2 2 10.1 2 38.3 2 2.83 2 16.9 2 4.38 20.014 J 0.05 0.019 J 0.05 0.01 J 0.05 0.017 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.052.02 J 5 315 5 108 5 104 5 U 5 65.4 5 90.6 5 4.365 J 5 280 5 U 5
0.055 J 0.2 U 0.2 U 0.2 0.045 J 0.2 0.047 J 0.2 U 0.2 0.065 J 0.2 0.11 J 0.2 0.063 J 0.2 U 0.20.133 J 0.5 U 0.5 U 0.5 0.166 J 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.119 J 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
0.131 +/- 0.300 U 0.296 +/- 0.273 0.125 +/- 0.285 U 0.432 +/- 0.324 0.508 +/- 0.476 0.273 +/- 0.329 U 0.0648 +/-0.296 U 0.145 +/- 0.349 U 0.273 +/- 0.330 U 0.0562 +/-0.257 U0.420 +/- 0.454 U -0.169 +/-0.325 U 0.719 +/- 0.401 0.866 +/- 0.451 0.541 +/- 0.358 0.507 +/- 0.380 0.173 +/- 0.311 U 0.644 +/- 0.397 0.991 +/- 0.454 0.283 +/- 0.296 U
U 2 U 2 U 2 U 2 U 2 U 2 0.565 J 2 U 2 U 2 U 21.09 0.5 226 0.5 0.856 0.5 0.235 J 0.5 0.238 J 0.5 0.292 J 0.5 6.25 0.5 0.33 J 0.5 0.169 J 0.5 0.182 J 0.554.9 0.5 42.5 0.5 3.51 0.5 45.1 0.5 45.9 0.5 46.4 0.5 119 0.5 35.1 0.5 29.2 0.5 320 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.131 J 0.2 0.053 J 0.2 U 0.2 U 0.2 0.042 J 0.2 0.146 J 0.2 0.042 J 0.2 0.198 J 0.2 0.073 J 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.172 J 0.5
2.049 J 5 309 5 113 5 U 5 U 5 77.2 5 191 5 8.87 5 293 5 U 50.045 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.04 J 0.2 0.154 J 0.2 0.136 J 0.2 0.05 J 0.2 U 0.2
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.163 J 0.5 0.1 J 0.5 U 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 0.561 J 2 U 2 U 2 U 20.739 0.5 227 0.5 0.673 0.5 0.199 J 0.5 0.223 J 0.5 0.308 J 0.5 6.37 0.5 0.318 J 0.5 0.141 J 0.5 0.146 J 0.545.4 0.5 42.3 0.5 3.62 0.5 44.4 0.5 44.3 0.5 45.6 0.5 117 0.5 33 0.5 28.2 0.5 314 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5U 0.2 0.111 J 0.2 0.064 J 0.2 U 0.2 U 0.2 0.338 0.2 0.133 J 0.2 U 0.2 0.18 J 0.2 U 0.2U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.225 J 0.5 U 0.5 U 0.5 U 0.5
19.7 2 65.2 2 2.82 2 9.43 2 9.5 2 11 2 57 2 3.44 2 21.8 2 5.02 2U 0.05 0.012 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 0.012 J 0.05
2.159 J 5 304 5 112 5 U 5 U 5 75.6 5 189 5 8.75 5 284 5 U 5U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.2 0.2 0.167 J 0.2 0.043 J 0.2 U 0.2U 0.5 U 0.5 U 0.5 U 0.5 0.127 J 0.5 U 0.5 0.174 J 0.5 0.163 J 0.5 U 0.5 U 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
0.840 +/- 0.679 -0.084+/-0.385 U 0.000 +/- 0.411 U 1.01 +/- 0.631 0.762 +/- 0.690 1.09 +/- 0.649 0.269 +/- 0.584 U 0.255 +/- 0.501 U 0.372 +/- 0.517 U 0.776 +/- 0.5670.0325+/-0.329 U -0.084+/-0.385 U 0.393 +/- 0.398 U 0.913 +/- 0.524 0.237 +/- 0.376 U 0.261 +/- 0.383 U 0.282 +/- 0.303 U 0.434 +/- 0.423 0.105 +/- 0.317 U 0.433 +/- 0.357
U 2 U 2 U 2 U 2 U 2 U 2 0.878 J 2 U 2 U 2 U 21.52 0.5 231 0.5 0.736 0.5 0.259 J 0.5 0.52 0.5 0.549 0.5 3.35 0.5 0.466 J 0.5 0.188 J 0.5 0.129 J 0.563.3 0.5 42.7 0.5 3.72 0.5 47.7 0.5 46.8 0.5 47.3 0.5 61.6 0.5 39.1 0.5 30.5 0.5 324 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.50.067 J 0.2 0.191 J 0.2 0.067 J 0.2 U 0.2 U 0.2 U 0.2 0.175 J 0.2 0.084 J 0.2 0.208 0.2 U 0.2
U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
22.1 2 71.3 2 3.19 2 9.99 2 11.8 2 11.9 2 64.4 2 3.65 2 20.8 2 4.82 20.022 J 0.05 0.02 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.052.106 J 5 320 5 133 5 U 5 76.6 5 76.6 5 303 5 6.09 5 300 5 U 5
U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.275 0.2 0.166 J 0.2 U 0.2 0.043 J 0.2U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 0.214 J 0.5 U 0.5 U 0.5 U 0.5
U 2 U 2 U 2 U 2 U 2 U 2 0.864 J 2 U 2 U 2 U 21.07 0.5 230 0.5 0.819 0.5 0.186 J 0.5 0.486 J 0.5 0.531 0.5 3.2 0.5 0.399 J 0.5 0.204 J 0.5 0.168 J 0.550.4 0.5 41.2 0.5 3.75 0.5 45.9 0.5 46.2 0.5 45.7 0.5 60.6 0.5 38.3 0.5 30.1 0.5 317 0.5
U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.50.065 J 0.2 0.201 0.2 0.074 J 0.2 U 0.2 U 0.2 0.048 J 0.2 0.194 J 0.2 0.068 J 0.2 0.195 J 0.2 U 0.2
U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5 U 5U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5
21.2 2 69.8 2 2.95 2 9.81 2 11.1 2 11.5 2 64 2 3.52 2 20.6 2 4.63 20.018 J 0.05 0.025 J 0.05 0.011 J 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 0.012 J 0.05 U 0.052.238 J 5 308 5 131 5 U 5 75.4 5 74.3 5 292 5 5.91 5 291 5 U 50.047 J 0.2 U 0.2 U 0.2 U 0.2 U 0.2 U 0.2 0.294 0.2 0.127 J 0.2 U 0.2 U 0.20.122 J 0.5 U 0.5 U 0.5 U 0.5 0.141 J 0.5 U 0.5 0.211 J 0.5 U 0.5 U 0.5 0.1 J 0.5
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits
Ash Basin 6, Brunner Island Steam Electric Station East Manchester Township York County, PA
AGC Project No.: 2015-3397
Sample LocationSample NameLab IDDate SampledMatrixRemarksEvent IDParameters UnitsAppendix III ParametersConventionalsChloride mg/LFluoride mg/LLab pH * S.U.Sulfate mg/LTotal Dissolved Solids mg/LMetals, Total Boron, Total µg/LCalcium, Total mg/LMetals, DissolvedBoron, Dissolved µg/LCalcium, Dissolved mg/LField ParameterspH field reading ** S.U.Appendix IV ParametersConventionalsFluoride mg/LRadiochemistry ***Radium-226 pCi/LRadium-228 pCi/LMetals, Total Antimony, total µg/LArsenic, total µg/LBarium, total µg/LBeryllium, total µg/LCadmium, total µg/LChromium, total µg/LCobalt, total µg/LLead, total µg/LLithium, total µg/LMercury, total µg/LMolybdenum, total µg/LSelenium, total µg/LThallium, total µg/LMetals, DissolvedAntimony, dissolved µg/LArsenic, dissolved µg/LBarium, dissolved µg/LBeryllium, dissolved µg/LCadmium, dissolved µg/LChromium, dissolved µg/LCobalt, dissolved µg/LLead, dissolved µg/LLithium, dissolved µg/LMercury, dissolved µg/LMolybdenum, dissolved µg/LSelenium, dissolved µg/LThallium, dissolved µg/L
Notes:mg/L - milligrams per literµg/L - micrograms per literS.U. - Standard UnitspCi/L - picocuries per liter DL - Detection LimitFD - Field Duplicate
J - Analyte detected below limit of quantitation and above limit of detection. U - Analyte was not detected above the limit of detectionLOQ - Limit of Quantitation X - Oven temperature was outside 180+/-2oC degree method criteria at 177oCNS - Not sampled * Laboratory pH analyzed outside of the method hold timeP- Sample not preserved properly ** Field pH is not certified in NELAC Scope of AccreditationQ - Qualifier *** Radiochemistry analyzed by HawkMtn Labs IncR - Replicate recovery outside accepted recovery limits