BOREHOLE RECORD. Site: Wilton Tunnel Approach Investigation. Groundwater STRATA RECORD. Depth (m) Description

Size: px
Start display at page:

Download "BOREHOLE RECORD. Site: Wilton Tunnel Approach Investigation. Groundwater STRATA RECORD. Depth (m) Description"

Transcription

1 BOREHOLE RECORD Borehole WA02 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 4 of 4 Driller: LS/RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 26/06/ /07/2014 Checked By: Legend Well \Backfill Remaining Detail : 29.92m m : 29.92m-30.40m: Stepped rough joint, 5-10mm thickness, clear to gravel infill. Dip: 75-85? m-33.36m: 5no medium spaced joints, stepped and undulating, rough to smooth. Dip: 25-45? m-33.36m: Joint, stepped and rough, 1-3mm, clean. Dip: 80?. End of Borehole at m Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) after 25minssealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

2 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type Insitu Testing From - To(m) (Casing) Groundwater BOREHOLE RECORD Site: Wilton Tunnel Approach Investigation STRATA RECORD Description CLAY, boulders, gravel and sand (driller's description). GL (m AOD) Easting: Sheet: 1 of 5 Driller: RC Logged By: IN (m) Borehole WA03 Level (m AOD) Scale 1:50 Northing: Dates: 01/07/ /07/2014 Checked By: Legend Well \Backfill Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/ General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

3 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type Insitu Testing From - To(m) (Casing) Groundwater BOREHOLE RECORD Site: Wilton Tunnel Approach Investigation STRATA RECORD Description CLAY, boulders, gravel and sand (driller's description). GL (m AOD) Easting: Sheet: 2 of 5 Driller: RC Logged By: IN (m) Borehole WA03 Level (m AOD) Scale 1:50 Northing: Dates: 01/07/ /07/2014 Checked By: Legend Well \Backfill Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/ General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

4 BOREHOLE RECORD Borehole WA03 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 3 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 01/07/ /07/2014 Checked By: Legend Well \Backfill CLAY, boulders, gravel and sand (driller's description) Boulder CLAY (driller's description) % Air/Mist Boulder CLAY (driller's description). Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/ General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

5 BOREHOLE RECORD Borehole WA03 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 4 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 01/07/ /07/2014 Checked By: Legend Well \Backfill Boulder CLAY (driller's description) /07/ (32.60) Medium strong thinly interlaminated highly calcareous dark to light grey SANDSTONE and MUDSTONE. Bivalve fossils noted throughout. Laminae are planar to undulating, 1-4mm thickness. Closely to medium spaced bedding fractures, undulating, locally stepped, rough to smooth with occasional clayey gravel infill. Dip: 0-10? m-35.14m: Extremely weak mudstone. NI 35.63m-35.73m: NI m-38.04m: 3no stepped to planar, undulating, rough to smooth joints, 4-8m thickness, clear. Dip: 5-40?. 100% Air/Mist m-38.29m: Bands of dark brown sandstone. Displays ripple marks. Dip: 25?. AZCL m-39.69m: Extremely weak mudstone. Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

6 Contract No. D Client: York Potash Ltd Method: Type SAMPLE DETAILS From - To(m) N (cu) TCR (%) SCR (%) RQD (%) FI AZCL 10 NI 15 (Casing) Groundwater BOREHOLE RECORD Site: Wilton Tunnel Approach Investigation STRATA RECORD Description Medium strong thinly interlaminated highly calcareous dark to light grey SANDSTONE and MUDSTONE. Bivalve fossils noted throughout. Laminae are planar to undulating, 1-4mm thickness. Closely to medium spaced bedding fractures, undulating, locally stepped, rough to smooth with occasional clayey gravel infill. Dip: 0-10? m-40.28m: Extremely weak mudstone. Weak thinly laminated calcareous dark grey MUDSTONE. Laminae are planar to undulating, 1-4mm thickness. Unweathered. Closely spaced bedding fractures. Planar, undulating and stepped, rough and smooth, 0-10mm thickness clear to clay gravel infill. Dip: 0-10? m-42.60m: Pyrite fragemnts noted. GL (m AOD) Easting: Sheet: 5 of 5 Driller: RC Logged By: IN (m) Borehole WA03 Level (m AOD) Scale 1:50 Northing: Dates: 01/07/ /07/ Checked By: Legend Well \Backfill 03/07/ (32.60) 0.00 End of Borehole at m Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 13/08/ General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

7 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type Insitu Testing From - To(m) (Casing) Groundwater BOREHOLE RECORD Site: Wilton Tunnel Approach Investigation STRATA RECORD Description Boulder CLAY/SAND/GRAVEL (driller's description). GL (m AOD) Easting: Sheet: 1 of 5 Driller: RC Logged By: IN (m) Borehole WA05 Level (m AOD) Scale 1:50 Northing: Dates: 24/06/ /06/2014 Checked By: Legend Well \Backfill OH 8 9 Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 07/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

8 BOREHOLE RECORD Borehole WA05 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 2 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 24/06/ /06/2014 Checked By: Legend Well \Backfill Boulder CLAY/SAND/GRAVEL (driller's description) /06/ (14.50) /06/ (14.50) 7.00 BOULDER/CLAY (driller's description) NA % Air/Mist OH 19 Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 07/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

9 BOREHOLE RECORD Borehole WA05 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 3 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 24/06/ /06/2014 Checked By: Legend Well \Backfill BOULDER/CLAY (driller's description). 21 No recovery. Driller suspected rockhead at 20.60m. Probable cobble/boulder obstruction NA Boulder CLAY/SAND (driller's description) % Air/Mist OH Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 07/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

10 BOREHOLE RECORD Borehole WA05 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 4 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 24/06/ /06/2014 Checked By: Legend Well \Backfill Boulder CLAY/SAND (driller's description) Brown slightly sandy slightly gravelly CLAY. Gravel is subangular, fine to coarse of sandstone and mudstone NA AZCL 25/06/ (14.50) /06/ (14.50) 39 26/06/ (38.50) 27/06/ (37.50) Weak thinly laminated dark grey MUDSTONE. Laminae are planar and undulating, 2-6mm thick. Fossil fragments noted throughout. Unweathered. Closely spaced planar bedding fractures, stepped, undulating and smooth, 0-2mm thick, clear to clay gravel infill. Dip: 0-10? m-38.86m: Joint, undulating, smooth, 20mm thick, clay gravel infill. Dip: 35? m: Extremely weak mudstone. Continued next sheet Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 07/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

11 BOREHOLE RECORD Borehole WA05 Contract No. D Client: York Potash Ltd Method: SAMPLE DETAILS Type N (cu) From - To(m) TCR (%) SCR (%) RQD (%) FI Site: Wilton Tunnel Approach Investigation (Casing) Groundwater STRATA RECORD Description GL (m AOD) Easting: Sheet: 5 of 5 Driller: RC Logged By: IN (m) Level (m AOD) Scale 1:50 Northing: Dates: 24/06/ /06/2014 Checked By: Legend Well \Backfill Weak thinly laminated dark grey MUDSTONE. Laminae are planar and undulating, 2-6mm thick. Fossil fragments noted throughout. Unweathered m-41.26m: Joint, undulating and rough, 1-2mm thick, clean. Dip: 30? m-41.36m: Joint, undulating and rough, 1-2mm thick, clean. Dip: 30? m-45.40m: 9x closely spaced joint, undulating, planar, stepped, rough to smooth, 0-20mm thick, clear to gravel infill. Dip: 40-80? m-45.72m: Joint, undulating, closed, rough, clay gravel infill. Dip: 60? m-46.07m: 5 undulating bedding fractures, rough and closed to 10mm with clay gravel infill. Dip: 0-5? m-46.53m: Medium strong sandy mudstone NI 10 NI 9 NI AZCL 27/06/ (38.50) Extremely weak thinly laminated highly calcareous dark grey light brown MUDSTONE. Laminae are planar, undulating, below 4mm thick. Closely spaced planar and smooth bedding fractures, 1mm thick, clean. Dip: 0? m-46.92m: Joint stepped and smooth, 10mm clean. Dip: 55?. Weak thinly laminated calcareous dark grey MUDSTONE. Laminae are planar, undulating, 1-6mm thick. Unweathered. Very closely spaced bedding fractures planar smooth, occasionally infilled with gravel m-47.11m: Non intact m-47.41m: Non intact m-47.60m: Joint undulating rough, 0-10mm thick, clay gravel infill. Dip: 50-90? m-47.60m: Non intact recovered as clayey gravel m-47.66m: Extremely weak mudstone m-48.30m: Extremely weak mudstone End of Borehole at m Ground Water (m) Chiselling/ Hard Strata Casing s Hole Diameter Casing Water level Water From (m) To (m) Time (hr) Diameter Diameter Struck (m) (m) sealed (m) (mm) (m) (mm) (m) Log last updated: 07/08/2014 General Remarks 1. Hand dug pit to 1.20m. PC 29/11/2013 v13.13

12 A P P E N D I X 5 GROUNDWATER MONITORING DATA

13 Borehole Designation BH501 BH502 BH502A BH503 BH504 BH505 BH506 BH507 BH507A BH508 BH509 BH510 BH510A BH511 BH512 BH512A BH513 BH514A BH515 BH01 BH01A Hole Completed (Date) Easting Northing Aquifer Unit SUPER SUPER MST SUPER MG MG MG SUPER MST MG SUPER MG Mdst MG SUPER MST MG SUPER SUPER SUPER MST Stratigraphic Unit Till Till Redcar Mdst Till Made ground Made ground Made ground Till Redcar Mdst Made ground Till Made ground Redcar Mdst Made ground Till Redcar Mdst Made ground Till Deep Till Till Redcar Mdst Response Zone (m bgl) 1 ot 2 m 1 to 3.6 m 5.6 to 15 m 1 to 4.8 m 1 to 5 m 0.7 to 1.1 m 0.8 to 1.3 m 1 to 9 m 10 to 15 m 1 to 1.4 m 1.5 to 5 m 1 to 2.3 m 9 to 15 m 1 to 1.9 m 8.5 to 11.5 m 25 to 35 m 0.8 to 1.1 m 1 to 4 m 4 to 7.6 m 1.5 to 14 m 25 to 35 m Top Level (Top of Cover; maod) Height of Cover (m) Top Level (Top of Pipe; maod) N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Height of Pipe (m) Top Level (Ground Surface; maod) Base (m bgl - Top of Cover) Base (Top of Pipe) Base (m bgl) Base (m AOD) WATER LEVEL (m AOD) 09/05/ /06/ /07/ /07/ /07/ /07/ /07/ Min Max Ave SD Water Level (m bgl) 09/05/ /06/ /07/ /07/ /07/ /07/ /07/ Min Max Ave SD August PortOR04 - Wilton Hydrologeological Baseline Report Table 3 - Wilton Groundwater Monitoring Database

14 August PortOR04 - Wilton Hydrologeological Baseline Report Table 3 - Wilton Groundwater Monitoring Database WA02 WA03 WA N/A Artesian Artesian Artesian Artesian

15 Borehole Designation BH201 BH201A BH202 BH202A BH203 BH203A BH204 BH204A BH204B BH205 BH205A BH206-1 BH206-2 BH206A BH207 BH207A-1 BH207A-2 BH208 BH208A BH209 BH209A BH210 BH210A BH211 BH211A BH212 BH212A BH213 BH214 BH215 BH216 BH2 Hole Completed (Date) Easting Northing Response Zone (m bgl) Top Level (Top of Cover; maod) Height of Cover (m) Top Level (Top of Pipe; maod) N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Height of Pipe (m) Top Level (Ground Surface; maod) Base (Top of Cover) Base (Top of Pipe) Base (m bgl) Base (m AOD) WATER LEVEL (m AOD) BH201 BH201A BH202 BH202A BH203 BH203A BH204 BH204A BH204B BH205 BH205A BH206-1 BH206-2 BH206A BH207 BH207A-1 BH207A-2 BH208 BH208A BH209 BH209A BH210 BH210A BH211 BH211A BH212 BH212A BH213 BH214 BH215 BH216 BH02 20/05/ /05/ /06/ /06/ /06/ /06/ /07/ /07/ /07/ Maximum Minimum Range Average Standard Deviation WATER LEVEL (m bgl) BH201 BH201A BH202 BH202A BH203 BH203A BH204 BH204A BH204B BH205 BH205A BH206-1 BH206-2 BH206A BH207 BH207A-1 BH207A-2 BH208 BH208A BH209 BH209A BH210 BH210A BH211 BH211A BH212 BH212A BH213 BH214 BH215 BH216 BH02 20/05/ not read Dry Dry Dry /05/ Dry Dry Dry Dry /06/ Dry Dry Dry Dry /06/ Dry Dry Dry Dry /06/ Dry Dry Dry Dry /06/ Dry Dry Dry Dry /07/ Dry Dry Dry Dry /07/ Dry Dry Dry Dry Dry /07/ Dry Dry Dry Dry Maximum Minimum Range Average Standard Deviation july AMTSOR25 - TABLE 5 - WATER MONITORING DATA TABLE 5 WATER MONITORING DATA - TOCKETTS LYTHE Diver Serial Number N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Aquifer Unit CIS SUPER SST SUPER SST SUPER SUPER CIS SST SUPER SST SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SST SUPER CIS CIS CIS Cleveland Superficial Superficial Superficial Superficial Superficial Superficial Superficial Superficial Cleveland Cleveland Cleveland Ironstone Superficial Staithes Superficial Staithes Superficial Cleveland Staithes Superficial deposits - Superficial deposits Superficial Superficial Superficial deposits - deposits - deposits - Superficial deposits - Superficial Superficial deposits - deposits - Staithes deposits - Ironstone Ironstone Ironstone Redcar Stratigraphic Unit Formation deposits Sandstone deposits Sandstone deposits Superficial deposits Ironstone Sandstone deposits Staithes Sandstone shallow - Mid Superficial deposits deposits deposits deposits deep shallow mid deposits deep deposits deposits deep shallow Sandstone mid Formation Formation Formation Mudstone Dip level taken immediately following well development. Groundwater level still recovering following development so value excluded from summary of groundwater levels

16 Borehole Designation BH301 BH301A BH302 BH302A BH303 BH303A BH303B BH303C BH304 BH304A BH304B BH304C BH306 BH307A BH308A BH309A BH310 BH311 BH312A BH313A BH314A BH315 BH316 BH316A BH317 BH318 BH319 BH320 BH321 BH321A BH322 Hole Completed (Date) 04/06/ /05/ /06/ /05/ /05/ /05/ /05/ /05/ /05/ /05/ /05/ /05/ /07/ /06/ /06/ /05/ /06/ /05/ /05/ /05/ /05/ /05/ /06/ /06/ /07/ /07/ /07/14 10/07/ /06/ /06/ /06/2014 Easting Northing Response Zone (m bgl) 1 to to to to 10 1 to 4 27 to to to to to to to 45 2 to to 20 1 to to 11 1 to 6 3 to 11 4 to 14 5 to to 20 1 to to 17 2 to to 25 2 to 21 1 to to 14 3 to 8 Max Min Ave SD july August AmtsOR26 - Table 4 - Groundwater Levels TABLE 4 :- Groundwater Monitoring Data - Lockwood Beck Aquifer Unit Superficials Scalby Superficials Scalby Superficials SBF SBF CF SUPER Scalby SBF CF SUPER SBF SF SF SF SF SF/SBF SF/SBF SBF/CF SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER SUPER Within sand band Superficial Scalby and Scalby and top of Scarborough and Superficial Superficials and Stratigraphic Unit in superficials Superficials Superficials Scarborough Scarborough Cloughton deposits Scalby Scarborough Cloughton Superficials Scarborough Scalby Scalby Scalby Scalby Scarborough Scarborough Cloughton deposits Superficials Superficials sandstone Superficials Superficials Superficials Superficials Superficials Superficials Top Level (Top of Cover; maod) Height of Cover (m) Top Level (Top of Pipe; maod) N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Height of Pipe (m) Top Level (Ground Surface; maod) Base (Top of Cover) Base (Top of Pipe) Base (m bgl) Base (m AOD) WATER LEVEL (m AOD) 19/06/2014 and 20/06/ /06/ /07/ /07/ /07/

17 Off-Site Borehole Designation BH401 BH401A BH401B BH401C BH402 BH402A BH402B BH402C BH403 BH404 BH404A BH404B BH404C BH405 BH405A BH406 BH406A BH407 BH407A BH408 BH408A BH409 BH409A BH410 BH410A BH411 BH411A BH413A BH413B BH413C BH26P Response Zone (m bgl) 1 to to 11 1 to to to 40 1 to to to 40 1 to to to to to 58 1 to 3 3 to 10 1 to to 10 1 to to to 3 5 to to to 17 1 to 4 5 to 13 1 to to 13 4 to to to 50 1 to 5 Base (m bgl) Base (m AOD) Max Min Ave SD WATER LEVEL (m bgl) BH401 BH401A BH401B BH401C BH402 BH402A BH402B BH402C BH403 BH404 BH404A BH404B BH404C BH405 BH405A BH406 BH406A BH407 BH407A BH408 BH408A BH409 BH409A BH410 BH410A BH411 BH411A BH413A BH413B BH413C 18/06/ /06/ /07/ /07/ DRY Max Min Ave SD Table 4 Groundwater Monitoring - Lady Cross Plantation Hole Completed (Date) Easting Northing Aquifer Unit SUPER SF SBF CF SUPER SF SBF CF SUPER SUPER SF SBF CF SUPER SF SUPER SF SUPER SF SUPER SF SUPER SF SUPER SF SUPER SF SF SBF CF CF Superficial Superficial Scalby (Moor Superficial Superficial Scalby (Moor Superficial Superficial Superficial Superficial Superficial Superficial Superficial Stratigraphic Unit deposits Scalby (LN/MG) Scarborough Cloughton deposits Grit) Scarborough Cloughton deposits deposits Grit) Scarborough Cloughton deposits Scalby (LN) deposits Scalby (LN) deposits Scalby (LN/MG) deposits Scalby (LN/MG) deposits Scalby (LN/MG) deposits Scalby (LN) deposits Scalby (LN/MG) Scalby (LN/MG) Scarborough Cloughton Cloughton Top Level (Top of Cover; maod) Height of Cover (m) Top Level (Top of Pipe; maod) N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Height of Pipe (m) Top Level (Ground Surface; maod) Base (Top of Cover) Base (Top of Pipe) WATER LEVEL (m AOD) 18/06/ /06/ /07/ /07/

18 TABLE 20:- Maximum and Minimum Groundwater Levels by Borehole Borehole Max/Date Min/Date Range Timescale (From/To) Months Aquifer /05/ /03/ /02/ /05/ ** Cloughton /02/ /10/ /02/ /05/ Moor Grit /11/ /01/ /02/ /05/ ** Cloughton /06/ /03/ /02/ /05/ Scarborough/Cloughton 5A /07/ /02/ /02/ /05/ Cloughton 5B /02/ /10/ /02/ /05/ Moor Grit /02/ /09/ /02/ /05/ Cloughton 6A /04/ /11/ /02/ /05/ Cloughton /02/ /11/ /02/ /05/ Cloughton /04/ /11/ /02/ /05/ Saltwick (Eller Beck) /11/ /03/ /02/ /05/ Cloughton /04/ /11/ /02/ /05/ Cloughton 3A /03/ /03/ /03/ /05/ ** Cloughton 7B /07/ /03/ /02/ /05/ Cloughton /02/ /04/ /01/ /05/ Superficials 105A /02/ /01/ /01/ /05/ Moor Grit /02/ /03/ /01/ /05/ ** Superficials 106A /04/ /03/ /01/ /05/ Scarborough /04/ /04/ /01/ /05/ Superficials 107A /02/ /04/ /01/ /05/ Cloughton /04/ /02/ /02/ /05/ ** Superficials 108A /02/ /04/ /02/ /05/ ** Scarborough /04/ /02/ /01/ /05/ ** Superficials 109A /03/ /02/ /01/ /05/ ** Cloughton /04/ /04/ /01/ /05/ Superficials 110A /02/ /04/ /01/ /05/ Cloughton /02/ /04/ /01/ /05/ Superficials 111A /02/ /04/ /01/ /05/ Moor Grit /02/ /03/ /02/ /05/ Superficials 112A /02/ /04/ /01/ /05/ ** Cloughton /02/ /04/ /01/ /05/ Superficials 113A /02/ /03/ /01/ /05/ Cloughton /02/ /04/ /01/ /05/ Moor Grit /02/ /04/ /02/ /05/ Moor Grit /02/ /04/ /02/ /05/ Moor Grit /02/ /04/ /02/ /05/ Moor Grit 118A /02/ /03/ /01/ /05/ Moor Grit 118B /02/ /03/ /01/ /05/ Long Nab 118C /02/ /04/ /01/ /05/ Scarborough /03/ /04/ /03/ /05/ Scarborough /02/ /04/ /02/ /05/ Scarborough /02/ /04/ /01/ /05/ Moor Grit /02/ /04/ /01/ /05/ Moor Grit /02/ /12/ /12/ /05/ * Moor Grit /02/ /12/ /12/ /05/ * Scarborough /02/ /12/ /12/ /05/ * Moor Grit /02/ /12/ /12/ /05/ * Scarborough /03/ /12/ /12/ /05/ * Moor Grit /03/ /01/ /12/ /05/ * Scarborough /03/ /01/ /12/ /05/ * Cloughton /12/ /03/ /12/ /05/ * Saltwick /03/ /04/ /12/ /05/ * Moor Grit /03/ /12/ /12/ /05/ * Scarborough /03/ /01/ /12/ /05/ * Cloughton /12/ /03/ /12/ /05/ * Saltwick /03/ /12/ /12/ /05/ * Moor Grit 135A /03/ /12/ /12/ /05/ * Scarborough 135B /03/ /04/ /12/ /05/ * Cloughton 135C /04/ /03/ /12/ /05/ * Saltwick MB /02/ /03/ /02/ /05/ Superficials MB /02/ /04/ /02/ /05/ Superficials MB /02/ /04/ /02/ /05/ Superficials MB /03/ /03/ /02/ /05/ Superficials MB /02/ /04/ /02/ /05/ Superficials =value in "summer" period = value in "winter period (November to March) * Avoiding period of pumping tests from 15/1/2014 to 13/2/2014 for HG127 to 135C inclusive and 3/12 to 16/12/2013 for HG123 to 126 inclusive as pumping tests will have distorted the results. ** Initial results in database appears to be a false positive when compared to remaining results and has not been included June MineOR15A - Table 20 - Min. and Max. GW Levels

19 Lab No Sample ID BH501 BH502 BH502A Other ID Sample Type WATER WATER WATER Sampling Date 02/07/14 02/07/14 02/07/14 Sampling Time n/s n/s n/s Test Method LOD Units Metals Aluminium, DETSC ug/l Arsenic, Boron, Cadmium, Calcium, Chromium, Hexavalent Chromium Copper, Iron, Total Iron Ferrous Iron (Filtered) Ferric Iron (Filtered) Lead, Magnesium, Manganese, Total Manganese Mercury, Nickel, Potassium, Sodium, Silver Sodium, Zinc, Inorganics Conductivity ph Alkalinity as CaCO3 (Automated) Carbonate Alkalinity as CaCO3 Cyanide total Suspended Solids Suspended Solids Total Solids Ammoniacal Nitrogen as N Bromide Chloride Fluoride Nitrate as NO3 Nitrite as N Nitrite as NO2 Nitrogen Ortho Phosphate as PO4 Ortho Phosphate as P Sulphate as SO4 DETSC ug/l DETSC 2306* 12 ug/l DETSC ug/l < 0.03 < 0.03 < 0.03 DETSC mg/l DETSC ug/l < 0.25 < DETSC ug/l < 10 < 10 < 10 DETSC ug/l DETSC ug/l 6.5 < DETSC 2306* 5.5 ug/l 6.5 < DETSC 2210* 100 ug/l < 100 < 100 < 100 DETSC 2210* 100 ug/l < 100 < DETSC ug/l < 0.09 < DETSC mg/l DETSC ug/l DETSC 2306* 0.22 ug/l DETSC ug/l < 0.01 < 0.01 < 0.01 DETSC ug/l DETSC mg/l DETSC mg/l DETSC ug/l DETSC mg/l DETSC ug/l < 1.25 < 1.25 < 1.25 DETSC us/cm DETSC DETSC mg/l DETSC 2030* 10 mg/l < 10 < 10 < 10 DETSC ug/l < 40 < 40 DETSC mg/l DETSC mg/l DETSC mg/l DETSC mg/l < < DETSC mg/l DETSC mg/l DETSC mg/l DETSC mg/l 0.48 < DETSC mg/l DETSC mg/l < 0.10 < 0.10 < 0.10 DETSC 2121* 1 mg/l DETSC mg/l DETSC mg/l DETSC mg/l

20 Sulphide Total Organic Carbon Petroleum Hydrocarbons C5-C10 Gasoline Range Organics (GRO) EPH (C10-C40) Aliphatic C5-C6 Aliphatic C6-C8 Aliphatic C8-C10 Aliphatic C10-C12 Aliphatic C12-C16 Aliphatic C16-C21 Aliphatic C21-C35 Aliphatic C5-C35 Aromatic C5-C7 Aromatic C7-C8 Aromatic C8-C10 Aromatic C10-C12 Aromatic C12-C16 Aromatic C16-C21 Aromatic C21-C35 Aromatic C5-C35 TPH Ali/Aro Benzene Toluene Ethylbenzene Xylene PAHs Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(k)fluoranthene Benzo(g,h,i)perylene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3-c,d)pyrene Naphthalene Phenanthrene Pyrene PAH Phenols Phenol - Monohydric VOCs Dichlorodifluoromethane Chloromethane Vinyl Chloride DETSC ug/l < 10 < 10 < 10 DETSC 2085* 1 mg/l DETSC ug/l DETSC ug/l DETSC ug/l < 0.1 < DETSC ug/l < 0.1 < DETSC ug/l < 0.1 < 0.1 < 0.1 DETSC 3072* 1 ug/l < 1.0 DETSC 3072* 1 ug/l < DETSC 3072* 1 ug/l < DETSC 3072* 1 ug/l < DETSC 3072* 10 ug/l < DETSC ug/l < 0.1 < 0.1 < 0.1 DETSC ug/l < 0.1 < DETSC ug/l < 0.1 < 0.1 < 0.1 DETSC 3072* 1 ug/l 3.7 DETSC 3072* 1 ug/l 40 DETSC 3072* 1 ug/l 240 DETSC 3072* 1 ug/l 3700 DETSC 3072* 10 ug/l < 10 < DETSC 3072* 10 ug/l < DETSC ug/l < 1.0 DETSC ug/l 1.6 DETSC ug/l < 1.0 DETSC ug/l < 1.0 DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < 0.01 < 0.01 DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.01 ug/l < 0.01 < DETS 074* 0.2 ug/l < 0.20 < DETSC ug/l < 100 < 100

21 Bromomethane Chloroethane Trichlorofluoromethane 1,1-dichloroethylene Trans-1,2-dichloroethylene 1,1-dichloroethane cis-1,2-dichloroethylene 2,2-dichloropropane Bromochloromethane Chloroform 1,1,1-trichloroethane 1,1-dichloropropene Carbon tetrachloride Benzene 1,2-dichloroethane Trichloroethylene 1,2-dichloropropane Dibromomethane Bromodichloromethane cis-1,3-dichloropropene Toluene trans-1,3-dichloropropene 1,1,2-trichloroethane Tetrachloroethylene 1,3-dichloropropane Dibromochloromethane 1,2-dibromoethane Chlorobenzene 1,1,1,2-tetrachloroethane Ethylbenzene m+p-xylene o-xylene Styrene Bromoform Isopropylbenzene 1,1,2,2-tetrachloroethane Bromobenzene 1,2,3-trichloropropane n-propylbenzene 2-chlorotoluene 1,3,5-trimethylbenzene 4-chlorotoluene Tert-butylbenzene 1,2,4-trimethylbenzene sec-butylbenzene p-isopropyltoluene 1,3-dichlorobenzene 1,4-dichlorobenzene n-butylbenzene 1,2-dichlorobenzene DETSC 3432* 1 ug/l < 1 < 1 DETSC ug/l < 2 < 2 DETSC ug/l < 4 < 4 DETSC 3432* 1 ug/l < 1 < 1 DETSC ug/l < 4 < 4 DETSC ug/l < 1 2 DETSC ug/l < 2 < 2 DETSC ug/l < 2 < 2

BIO-CHEM Laboratories, Inc. Work Order Sample Summary. CLIENT: Cascade Thornapple River Assoc. Project: Water Analysis Lab Order:

BIO-CHEM Laboratories, Inc. Work Order Sample Summary. CLIENT: Cascade Thornapple River Assoc. Project: Water Analysis Lab Order: Date: 31-Jul-18 Work Order Sample Summary Lab Sample ID Client Sample ID Matrix Collection Date Date Received 1807123-01A Dam & Burger Water 7/25/2018 7/25/2018 1807123-02A 48th & RR Water 7/25/2018 7/25/2018

More information

BIO-CHEM Laboratories, Inc. Work Order Sample Summary. CLIENT: CTRA Project: 6454 T Lab Order: A 6454 Aqueous 3/1/2013.

BIO-CHEM Laboratories, Inc. Work Order Sample Summary. CLIENT: CTRA Project: 6454 T Lab Order: A 6454 Aqueous 3/1/2013. Date: 08-Mar-13 Work Order Sample Summary Lab Sample ID Client Sample ID Matrix Collection Date Date Received 1303004-01A 6454 Aqueous 3/1/2013 3/1/2013 Page 1 of 1 Date: 08-Mar-13 CASE NARRATIVE Samples

More information

Table 1 Soil and Groundwater Sampling Summary Table

Table 1 Soil and Groundwater Sampling Summary Table Table Soil and Groundwater Sampling Summary Table Phase II Investigation Consolidated Edison - Former kent Avenue Generating Station 0 Kent Avenue Brooklyn, NY Sample ID Date Installed Date Sample Collected

More information

CALA Directory of Laboratories

CALA Directory of Laboratories CALA Directory of Laboratories Membership Number: 2628 Laboratory Name: Caduceon Environmental Laboratories (Richmond Hill) Parent Institution: Caduceon Enterprises Inc. Address: 110 West Beavercreek Rd.

More information

Non-Potable Water A2LA Certificate

Non-Potable Water A2LA Certificate COLOR Color Biochemical Oxygen Demand (BOD); Carbonaceous DEMAND BOD; Chemical Oxygen Demand (COD); Total Organic Carbon (TOC) HEXAVALENT CHROMIUM INORGANIC NUTRIENTS LOW-LEVEL MERCURY METALS I & II METALS

More information

Certificate of Accreditation

Certificate of Accreditation PERRY JOHNSON LABORATORY ACCREDITATION, INC. Certificate of Accreditation Perry Johnson Laboratory Accreditation, Inc. has assessed the Laboratory of: (Hereinafter called the Organization) and hereby declares

More information

National Pollutant Discharge Elimination System (NPDES); BADCT Limits for Volatile Organic Compounds

National Pollutant Discharge Elimination System (NPDES); BADCT Limits for Volatile Organic Compounds Permit Guidance 12 Final National Pollutant Discharge Elimination System (NPDES); BADCT Limits for Volatile Organic Compounds Statutory references: ORC 6111.01, 6111.03, 6111.04 Rule references: OAC 3745-1-05,

More information

Appendix 2 Data Distributions for Contaminants in Water and Sediment Samples in Response to the Deepwater Horizon Oil Spill, 2010

Appendix 2 Data Distributions for Contaminants in Water and Sediment Samples in Response to the Deepwater Horizon Oil Spill, 2010 University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Publications of the US Geological Survey US Geological Survey 2013 Appendix 2 Data Distributions for Contaminants in Water

More information

ANALYTICAL RESULTS. Project: Mayflower, AR Pipeline Incident

ANALYTICAL RESULTS. Project: Mayflower, AR Pipeline Incident ANALYTICAL RESULTS Prepared by: Eurofins Lancaster Laboratories Environmental 2425 New Holland Pike Lancaster, PA 760 Prepared for: Mobil Pipeline Company PO Box 446 Houston TX 7720-446 July 30, 203 Project:

More information

OREGON Environmental Laboratory Accreditation Program ORELAP Fields of Accreditation ALS Environmental - Simi Valley

OREGON Environmental Laboratory Accreditation Program ORELAP Fields of Accreditation ALS Environmental - Simi Valley MATRIX Reference Code Analyte Code Description ASTM C471M- 14 2014 ASTM D5504-12 2012 3964 Orthorhombic Cyclooctasulfur 4842 1-Propanethiol 6113 2,5-Dimethylthiophene 4544 2-Ethylthiophene 4843 2-Propanethiol

More information

CERTIFICATE OF ANALYSIS

CERTIFICATE OF ANALYSIS Your Project #: VILLAGE OF TAHSIS Your C.O.C. #: 084437 Attention:Mark DeGagne -35 Estevan Rd Nanaimo, BC CANADA V9S 3Y3 Report #: R24287 Version: - Final MAXXAM JOB #: B5B343 Received: 205/2/22, 5:45

More information

AUTONOMOUS, REAL TIME DETECTION OF 58 VOCS IN THE PANAMA CANAL

AUTONOMOUS, REAL TIME DETECTION OF 58 VOCS IN THE PANAMA CANAL AUTONOMOUS, REAL TIME DETECTION OF 58 VOCS IN THE PANAMA CANAL Challenges of Water Monitoring Volatile Organic Compounds (VOCs) can have negative health impacts even at ppb levels VOC concentrations can

More information

Amec Foster Wheeler Environment & Infrastructure, Inc BIG SHANTY ROAD, NW, SUITE 100 KENNESAW, GEORGIA (770)

Amec Foster Wheeler Environment & Infrastructure, Inc BIG SHANTY ROAD, NW, SUITE 100 KENNESAW, GEORGIA (770) Dutch Valley Rd NE Worchester Dr NE Hillpine Dr NE Maddox Dr NE Lee St SW Maddox Dr NE Avery Dr NE E Park Ln NE Piedmont Ave NE Yorkshire Rd NE ³ Park Ln NE Westminster Dr NE Piedmont Way NE Westminster

More information

2. September 2015 Sub-Concrete Slab Soil Investigation

2. September 2015 Sub-Concrete Slab Soil Investigation To: Pam Barnett, RACER Ref. No.: 11109615 From: John-eric Pardys/kf/1 Date: October 30, 2015 Re: Summary of Sub-Concrete Slab Soil Investigation RACER Fredericksburg Facility Spotsylvania County, Virginia

More information

Certificate of Accreditation

Certificate of Accreditation PERRY JOHNSON LABORATORY ACCREDITATION, INC. Certificate of Accreditation Perry Johnson Laboratory Accreditation, Inc. has assessed the Laboratory of: (Hereinafter called the Organization) and hereby declares

More information

ANALYTICAL REPORT. Job Number: Job Description: Transform Complete

ANALYTICAL REPORT. Job Number: Job Description: Transform Complete ANALYTICAL REPORT Job Number: 640-4848-1 Job Description: Transform Complete For: American Master*Tech Scientific, Inc. 1330 Thurman Street PO BOX 2539 Lodi, CA 95240 Attention: Mr. Adam Kowalczyk Chad

More information

NELAC PT for Accreditation Fields of Proficiency Testing with PTRLs Drinking Water Effective: November 03, 2017

NELAC PT for Accreditation Fields of Proficiency Testing with PTRLs Drinking Water Effective: November 03, 2017 Microbiology CFU/100 ml CFU/100 ml 054 500 Total Coliform 8,9,10 Nine out of ten correct with no false negatives Not Applicable 055 530 Fecal Coliform 8,9,10 Nine out of ten correct with no false negatives

More information

Certificate of Accreditation

Certificate of Accreditation PERRY JOHNSON LABORATORY ACCREDITATION, INC. Certificate of Accreditation Perry Johnson Laboratory Accreditation, Inc. has assessed the Laboratory of: (Hereinafter called the Organization) and hereby declares

More information

CALA Directory of Laboratories

CALA Directory of Laboratories CALA Directory of Laboratories Membership Number: 2460 Laboratory Name: ROPEC Laboratory Parent Institution: City of Ottawa, Laboratory Services Address: 800 Greens Creek Dr, Ottawa ON K1J 1A6 Contact:

More information

CERTIFICATE OF ANALYSIS

CERTIFICATE OF ANALYSIS Brownstown Kilkieran Co Kilkenny Unit 7-8 Hawarden Business Park anor Road (off anor Lane) Hawarden Deeside CH5 3US Tel: (01244) 528700 Fax: (01244) 528701 email: customerservices@alcontrolcom Website:

More information

Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and Hplc

Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and Hplc Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and Hplc Sky Countryman, Ngoc Nguyen, Jeff Layne, Kory Kelly, and Zeshan Aqeel Phenomenex, Inc., 411 Madrid Ave.,

More information

Date Issued: April 01, 2013 Expiration Date: June 30, 2013

Date Issued: April 01, 2013 Expiration Date: June 30, 2013 State of Florida Department of Health~Bureau of Public Health Laboratories I his is to certify that ALS ENVIRONMENTAL - SIMI VALLEY 2655 PARK CENTER DRIVE, SUITE A SIMI VALLEY, CA 93065 has complied with

More information

Solid Phase Micro Extraction of Flavor Compounds in Beer

Solid Phase Micro Extraction of Flavor Compounds in Beer Solid Phase Micro Extraction of Flavor s in Beer ANNE JUREK USEPA 524.2 Method Validation Using the Evolution Purge and Trap Concentrator and the Centurion WS Autosampler Application Note Environmental

More information

317 Elm Street Milford, NH (603) Fax (603)

317 Elm Street Milford, NH (603) Fax (603) 317 Elm Street Milford, NH 03055 (603) 673-5440 Fax (603) 673-0366 Sales@chemservelab.com Friday, October 06, 2017 Domenic Carapella Greenplay Organics, LLC 6 Hawthorne Ave Merrick NY 11566 Project Name:

More information

Validation of USEPA Method Using a Stratum PTC, AQUATek 100 Autosampler, and Perkin-Elmer Clarus 600 GC/MS

Validation of USEPA Method Using a Stratum PTC, AQUATek 100 Autosampler, and Perkin-Elmer Clarus 600 GC/MS Validation of USEPA Method 524.2 Using a Stratum PTC, AQUATek 100 Autosampler, and Perkin-Elmer Clarus 600 GC/MS Application Note By: Nathan Valentine Abstract The US EPA developed Method 524.2¹, Measurement

More information

Performance of a Next Generation Vial Autosampler for the Analysis of VOCs in Water Matrices

Performance of a Next Generation Vial Autosampler for the Analysis of VOCs in Water Matrices Application Note Performance of a Next Generation Vial Autosampler for the Analysis of VOCs in Water Matrices Abstract By: Ed Price In today s laboratories, increased efficiency and productivity are of

More information

Detection of Volatile Organic Compounds in polluted air by an Agilent mini Thermal Desorber and an Agilent 5975T LTM GC/MS

Detection of Volatile Organic Compounds in polluted air by an Agilent mini Thermal Desorber and an Agilent 5975T LTM GC/MS Detection of Volatile Organic Compounds in polluted air by an Agilent mini Thermal Desorber and an Agilent 5975T LTM GC/MS Application Note Environmental Author Xiaohua Li Agilent Technologies (Shanghai)

More information

Maximizing Sample Throughput In Purge And Trap Analysis

Maximizing Sample Throughput In Purge And Trap Analysis Maximizing Sample Throughput In Purge And Trap Analysis LINDSEY PYRON ANNE JUREK INTRODUCTION There are several demands and requirements imposed on chemists performing volatile organic analysis (VOC) in

More information

EPA TO-17 Volatile Organic Compounds

EPA TO-17 Volatile Organic Compounds EPA TO-17 Volatile Organic Compounds Method TO-17 is used to analyze samples for volatile organic compounds collected on multi-bed sorbent tubes, which are thermally desorbed and cryo-focused on the capillary

More information

Analysis of Volatile Organic Compounds Using USEPA Method 8260 and the 4760 Purge and Trap and the 4100 Autosampler

Analysis of Volatile Organic Compounds Using USEPA Method 8260 and the 4760 Purge and Trap and the 4100 Autosampler Analysis of Volatile Organic Compounds Using USEPA Method 8260 and the 4760 Purge and Trap and the Introduction Although analysis of VOCs by purge and trap is considered a mature technique, advances in

More information

Optimal VOC Method Parameters for the StratUm PTC Purge & Trap Concentrator

Optimal VOC Method Parameters for the StratUm PTC Purge & Trap Concentrator Optimal VOC Method Parameters for the StratUm PTC Purge & Trap Concentrator Application Note Introduction Environmental laboratories have utilized the Purge & Trap sample concentration technique for over

More information

Target Compound Results Summary

Target Compound Results Summary Phone/ (86)88-4800 / (86)88-471 http://www.emsl.com to1lab@emsl.com Customer ID: EMSL0A K12312.D 28 cc 0 0/01/2017 K12327.D 21 cc 600 Target Compound Results Summary Propylene 11-07-1 42.08 ND.0 ND 8.6

More information

Validation of USEPA Method Using a Stratum PTC and the New AQUATek 100 Autosampler

Validation of USEPA Method Using a Stratum PTC and the New AQUATek 100 Autosampler Validation of USEPA Method 524.2 Using a Stratum PTC and the New AQUATek 100 Autosampler Application Note Abstract Automation is the key to increasing laboratory productivity and minimizing costs. It is

More information

Methods and Analytes Requiring Laboratory Certification Attachment 3

Methods and Analytes Requiring Laboratory Certification Attachment 3 s and s Requiring Laboratory Certification Attachment 3 Current as of July 1, 2011 Laboratory Certificates need to accurately reflect the methods performed and reported by the laboratory, including the

More information

Roger Bardsley, Applications Chemist; Teledyne Tekmar P a g e 1

Roger Bardsley, Applications Chemist; Teledyne Tekmar P a g e 1 Application Note US EPA Method 524.4 with the Tekmar Lumin P & T Concentrator and Thermo Scientific TRACE 1310 GC and ISQ LT MS System Roger Bardsley, Applications Chemist; Teledyne Tekmar P a g e 1 Abstract

More information

Methanol Extraction of high level soil samples by USEPA Method 8260C

Methanol Extraction of high level soil samples by USEPA Method 8260C Methanol Extraction of high level soil samples by USEPA Method 8260C Abstract In order to determine the concentration of Volatile Organic Compounds (VOCs) in soil and waste samples the USEPA developed

More information

Electronic Supplementary Material Experimentally Validated Mathematical Model of Analyte Uptake by Permeation Passive Samplers

Electronic Supplementary Material Experimentally Validated Mathematical Model of Analyte Uptake by Permeation Passive Samplers Electronic Supplementary Material (ESI) for Environmental Science: Processes & Impacts. This journal is The Royal Society of Chemistry 2017 Electronic Supplementary Material Experimentally Validated Mathematical

More information

ANALYTICAL REPORT. Attn: Dan Spector

ANALYTICAL REPORT. Attn: Dan Spector ANALYTICAL REPORT TestAmerica Laboratories, Inc. Benjamin Road Suite 0 Tampa, FL Tel: ()- TestAmerica Job I: 0-- Client Revision: For: Langan Engineering & Environmental Srvcs 0 NW th Court Suite 00 Miami

More information

Laboratory Report Number(s) Lone Tree Road (Deep) 10/5/15, 10/19/15, 6/13/16. Address Sample Date(s) Analyses Requested

Laboratory Report Number(s) Lone Tree Road (Deep) 10/5/15, 10/19/15, 6/13/16. Address Sample Date(s) Analyses Requested July 14, 216 Mr. Shaun Lehman MDEQ-OOGM Lansing District Office Constitution Hall 2 South 525 West Allegan Street Lansing, MI 48913 Re: Residential Well Sampling Hartland 36 Gas Plant SE/NE/NW Section

More information

Validation of Volatile Organic Compound by USEPA. Method 8260C. Application Note. Abstract. Introduction. Experimental-Instrument Conditions

Validation of Volatile Organic Compound by USEPA. Method 8260C. Application Note. Abstract. Introduction. Experimental-Instrument Conditions Validation of Volatile Organic Compound by USEPA Method 8260C Application Note Abstract In order to determine the concentration of volatile organic compounds (VOCs) in water and soil matrices the USEPA

More information

Optimizing of Volatile Organic Compound Determination by Static Headspace Sampling

Optimizing of Volatile Organic Compound Determination by Static Headspace Sampling JSB is an authorised partner of Optimizing of Volatile Organic Compound Determination by Static Headspace Sampling Anne Jurek Introduction: #134 Static headspace sampling has always been a viable option

More information

Validation of Environmental Water Methods on One System: Considerations for Sample Volume, Purge Parameters and Quality Control Parameters

Validation of Environmental Water Methods on One System: Considerations for Sample Volume, Purge Parameters and Quality Control Parameters Validation of Environmental Water Methods on One System: Considerations for Sample Volume, Purge Parameters and Quality Control Parameters Application Note Abstract Water quality laboratories across the

More information

October 26, Dear Mr. White:

October 26, Dear Mr. White: ExxonMobil Environmental Services Company 38 Varick Street Brooklyn, New York 11222 October 26, 2011 New York State Department of Environmental Conservation Division of Environmental Remediation Remedial

More information

Exploring US EPA Method 524 Purge and Trap Variables: Water Vapor Reduction and Minimizing Cycle Time

Exploring US EPA Method 524 Purge and Trap Variables: Water Vapor Reduction and Minimizing Cycle Time Exploring US EPA Method 524 Purge and Trap Variables: Water Vapor Reduction and Minimizing Cycle Time Roger Bardsley, Applications Chemist; Teledyne Tekmar Page 1 Introduction Purge and Trap (P&T) concentrators

More information

Building 280A and Building 450 Soil Sampling Results Richmond Field Station Site Berkeley Global Campus at Richmond Bay, Richmond, California

Building 280A and Building 450 Soil Sampling Results Richmond Field Station Site Berkeley Global Campus at Richmond Bay, Richmond, California TETRA TECH, INC. February 5, 2016 Lynn Nakashima Berkeley Regional Office 700 Heinz Avenue, Suite 200C Berkeley, California 94710 Subject: Building 280A and Building 450 Soil Sampling Results Richmond

More information

U.S. EPA VOLATILE ORGANICS METHOD USING PURGE AND TRAP GC/MS

U.S. EPA VOLATILE ORGANICS METHOD USING PURGE AND TRAP GC/MS ENVIRONMENTAL application note U.S. EPA VOLATILE ORGANICS METHOD 524.2 USING PURGE AND TRAP GC/MS Cheri Coody, Public Health Laboratory, Mississippi State Health Department, Jackson, MS USA Michael J.

More information

KSA Environmental Laboratory Inc.

KSA Environmental Laboratory Inc. February 26, 07 KSA Environmental Laboratory Inc. Hydrologic Associates - Miami Attn: Brad Waller 8925 S.W. 148th Street Suite 212 Miami, FL 33176 RE: Parkland KSA Workorder: Q0012 Dear Brad Waller, Enclosed

More information

A Comparison of Volatile Organic Compound Response When Using Nitrogen as a Purge Gas

A Comparison of Volatile Organic Compound Response When Using Nitrogen as a Purge Gas A Comparison of Volatile Organic Compound When Using Nitrogen as a Gas Application Note By: Anne Jurek Abstract For many years Helium has been the gas of choice for purging Volatile Organic Compounds (VOCs).

More information

Certificate of Analysis

Certificate of Analysis Certificate of Analysis 2139 Certificate Number: 13-92896 Date: 27/11/2013 Client: Stainton Quarry Stainton Quarry Stainton Barnard Castle DL12 8RB Our Reference: 13-92896 Client Reference: Description:

More information

Texas Commission on Environmental Quality INTEROFFICE MEMORANDUM

Texas Commission on Environmental Quality INTEROFFICE MEMORANDUM Texas Commission on Environmental Quality INTEROFFICE MEMORANDUM To: Lorinda Gardner, Director, R15 Date: Carlos Rubinstein, Texas Border Area Director From: Valerie E. Meyers, Ph.D. Toxicology Section,

More information

Using Hydrogen as An Alternative Carrier Gas for US EPA 8260

Using Hydrogen as An Alternative Carrier Gas for US EPA 8260 Using Hydrogen as An Alternative Carrier Gas for US EPA 8260 Application Note Abstract Due to regional shortages and increasing costs of helium, the preferred carrier gas in gas chromatography, alternative

More information

Roger Bardsley, Applications Chemist; Teledyne Tekmar Page 1

Roger Bardsley, Applications Chemist; Teledyne Tekmar Page 1 Application Note US EPA Method 524.2 with the Teledyne Tekmar Lumin P&T Concentrator and Agilent 7890B GC / 5977A MS Roger Bardsley, Applications Chemist; Teledyne Tekmar Page 1 Abstract US EPA Method

More information

Analysis. Introduction: necessary. presented. Discussion: As part of be carried. consistent and reliable data. (MoRT) to.

Analysis. Introduction: necessary. presented. Discussion: As part of be carried. consistent and reliable data. (MoRT) to. Optimal Conditions for USEPA Method 8260 Analysis Anne Jurek Introduction: Over the past decade, the need for environmental laboratoriess using purge and trap systems to report at or below the Method Detection

More information

Certificate of Accreditation

Certificate of Accreditation PERRY JOHNSON LABORATORY ACCREDITATION, INC. Certificate of Accreditation Perry Johnson Laboratory Accreditation, Inc. has assessed the Laboratory of: 6701 Aberdeen Avenue, Suite #9, Lubbock, TX 79424

More information

The following report includes the data for the above referenced project for sample(s) received on 5/15/2017 at Air Toxics Ltd.

The following report includes the data for the above referenced project for sample(s) received on 5/15/2017 at Air Toxics Ltd. 5/26/2017 Ms. Anna Kelley Hamilton Co. Environmental Services 250 Wm. Howard Taft Cincinnati OH 45219 Project Name: Sun Coke Project #: Workorder #: 1705303 Dear Ms. Anna Kelley The following report includes

More information

Solid Phase Micro Extraction of Flavor Compounds in Beer

Solid Phase Micro Extraction of Flavor Compounds in Beer Solid Phase Micro Extraction of Flavor Compounds in Beer ANNE JUREK Automed Sampling of Methanol Extractions Applicion Note Environmental Author Anne Jurek Applicions Chemist EST Analytical Cincinni, OH

More information

US EPA Method with the Tekmar Lumin P&T Concentrator, AQUATek LVA and Agilent 7890B GC/5977A MS

US EPA Method with the Tekmar Lumin P&T Concentrator, AQUATek LVA and Agilent 7890B GC/5977A MS APPLICATION NOTE: TECHNOLOGY: INDUSTRY: AN1806 P+T VOC ENV US EPA Method 524.2 with the Tekmar Lumin P&T Concentrator, AQUATek LVA and Agilent 7890B GC/5977A MS Amy Nutter, Applications Chemist; Teledyne

More information

US EPA Method 8260 with the Tekmar Atomx XYZ P&T System and Agilent 7890B GC/5977A MS

US EPA Method 8260 with the Tekmar Atomx XYZ P&T System and Agilent 7890B GC/5977A MS Application Note US EPA Method 8260 with the Tekmar Atomx XYZ P&T System and Agilent 7890B GC/5977A MS Author Amy Nutter Applications Chemist, Teledyne Tekmar Abstract US EPA Method 8260 in conjunction

More information

Validation of USEPA Method 8260C Using Teledyne Tekmar Atomx, and Perkin-Elmer Clarus 600 GC/MS

Validation of USEPA Method 8260C Using Teledyne Tekmar Atomx, and Perkin-Elmer Clarus 600 GC/MS Validation of USEPA Method 8260C Using Teledyne Tekmar Atomx, and Perkin-Elmer Clarus 600 GC/MS Application Note By Tyler Trent Abstract In order to determine the concentration of volatile organic compounds

More information

Certificate of Accreditation

Certificate of Accreditation PERRY JOHNSON LABORATORY ACCREDITATION, INC. Certificate of Accreditation Perry Johnson Laboratory Accreditation, Inc. has assessed the Laboratory of: (Hereinafter called the Organization) and hereby declares

More information

Optimizing. Abstract: is standardd. procedures. altered to

Optimizing. Abstract: is standardd. procedures. altered to Optimizing Standard Preparation ANNE JUREK Abstract: Standardd preparation can often be a time consuming, tedious process. The opportunity for human error or inconsistencies between individual preparation

More information

Improved Volatiles Analysis Using Static Headspace, the Agilent 5977B GC/MSD, and a High-efficiency Source

Improved Volatiles Analysis Using Static Headspace, the Agilent 5977B GC/MSD, and a High-efficiency Source Improved Volatiles Analysis Using Static Headspace, the Agilent 5977B GC/MSD, and a High-efficiency Source Application Note Environmental Authors Peter Gautschi and Harry Prest Senior Application Scientist

More information

SUBSURFACE (PHASE II) INVESTIGATION REPORT

SUBSURFACE (PHASE II) INVESTIGATION REPORT SUBSURFACE (PHASE II) INVESTIGATION REPORT AKRF, Inc. 440 Park Avenue South New York, NY 10016 212-696-0670 Submitted to: Cayuga Indian Nation P.O. Box 11 Versailles, New York 14168 299 Cayuga Street Village

More information

Maximizing Production While Minimizing Costs

Maximizing Production While Minimizing Costs JSB is an authorised partner of Maximizing Production While Minimizing Costs Anne Jurek #123 Abstract: The need to increase productivity and reduce cost is becoming of greater concern to environmental

More information

APPLICATIONS TN Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and HPLC

APPLICATIONS TN Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and HPLC Detection of Environmental Contaminants Caused by the Oil Spill in the Gulf of Mexico by GC and HPLC Sky Countryman, Ngoc Nguyen, Jeff Layne, Kory Kelly, and Zeshan Aqeel Phenomenex, Inc., 411 Madrid Ave.,

More information

System and JUREK ANNE. Introduction: in an in purge and. trap sampling. Discussion: As part of. consistent and reliable data. (MoRT) to.

System and JUREK ANNE. Introduction: in an in purge and. trap sampling. Discussion: As part of. consistent and reliable data. (MoRT) to. ANNE JUREK Optimal Conditions for USEPA Method 8260B Analysis Using the EST Analyticall Sampling System and the Shimadzu GCMS-QP2010s Introduction: The USEPA developedd Method 8260B for the determination

More information

Solid Phase Microextraction of Cyanogen Chloride and Other Volatile Organic Compounds in Drinking Water with Fast Analysis by GC-TOFMS

Solid Phase Microextraction of Cyanogen Chloride and Other Volatile Organic Compounds in Drinking Water with Fast Analysis by GC-TOFMS Solid Phase Microextraction of Cyanogen Chloride and Other Volatile Organic Compounds in Drinking Water with Fast Analysis by GC-TOFMS LECO Corporation; Saint Joseph, Michigan USA Key Words: GC-TOFMS,

More information

Analysis of Volatile Organic Compounds in Soil Samples by EPA Method 8260 with The Stratum PTC and SOLATek 72 Multi-Matrix Autosampler

Analysis of Volatile Organic Compounds in Soil Samples by EPA Method 8260 with The Stratum PTC and SOLATek 72 Multi-Matrix Autosampler Analysis of Volatile Organic Compounds in Soil Samples by EPA Method 8260 with The Stratum PTC and SOLATek 72 Multi-Matrix Autosampler Application Note By: Teri Dattilio Introduction Purge and Trap concentration

More information

A Site Location Map and Site and Surrounding Properties Map are attached as Figure 1 and Figure 2, respectively.

A Site Location Map and Site and Surrounding Properties Map are attached as Figure 1 and Figure 2, respectively. February 23, 216 Mr. Shaun Lehman MDEQ-OOGM Lansing District Office Constitution Hall 2 South 525 West Allegan Street Lansing, MI 48913 Re: Groundwater Characterization Work Plan Hartland 36 Gas Plant

More information

Analysis of Volatile Organic Compounds in Water and Soil by EPA Method 8260 with the Atomx Concentrator/Multimatrix Autosampler

Analysis of Volatile Organic Compounds in Water and Soil by EPA Method 8260 with the Atomx Concentrator/Multimatrix Autosampler Analysis of Volatile Organic Compounds in Water and Soil by EPA Method 8260 with the Atomx Concentrator/Multimatrix Autosampler Application Note By: Anne Jurek Abstract In order to determine the amount

More information

Ed George and Anaïs Viven Varian, Inc.

Ed George and Anaïs Viven Varian, Inc. Application Note SI-02408 Evaluation of EPA Method 524.3: a New Draft Method for the Analysis of VOCs in Drinking Water using GC/MS and V:Results GC/MS Software Ed George and Anaïs Viven Varian, Inc. Introduction

More information

A Single Calibration Method for Water AND Soil Samples Performing EPA Method 8260

A Single Calibration Method for Water AND Soil Samples Performing EPA Method 8260 JSB is an authorised partner of A Single Calibration Method for Water AND Soil Samples Performing EPA Method 8260 Anne Jurek #101 Introduction: The United States Environmental Protection Agency (USEPA)

More information

Copies: Dave Favero, RACER File

Copies: Dave Favero, RACER File MEMO To: Nate Nemani USEPA Region 5 77 West Jackson Boulevard Mail Code: LU-9J Chicago, Illinois 60604-3507 Copies: Dave Favero, RACER File Arcadis of Michigan, LLC 300 S. Washington Square Suite 315 Lansing

More information

PHASE II ENVIRONMENTAL SITE ASSESSMENT RICKENBACKER MARINA PARCELS 3301 RICKENBACKER CAUSEWAY MIAMI-DADE COUNTY, FLORIDA

PHASE II ENVIRONMENTAL SITE ASSESSMENT RICKENBACKER MARINA PARCELS 3301 RICKENBACKER CAUSEWAY MIAMI-DADE COUNTY, FLORIDA PHASE II ENVIRONMENTAL SITE ASSESSMENT RICKENBACKER MARINA PARCELS 3301 RICKENBACKER CAUSEWAY MIAMI-DADE COUNTY, FLORIDA PREPARED FOR: The City of Miami Department of Real Estate & Asset Management 444

More information

SUMMARY REPORT OF AIR MONITORING FOR LEED CERTIFICATION PHASE 2 SWANSFIELD ELEMENTARY SCHOOL 5610 CEDAR LANE COLUMBIA, MD PREPARED FOR:

SUMMARY REPORT OF AIR MONITORING FOR LEED CERTIFICATION PHASE 2 SWANSFIELD ELEMENTARY SCHOOL 5610 CEDAR LANE COLUMBIA, MD PREPARED FOR: SUMMARY REPORT OF AIR MONITORING FOR LEED CERTIFICATION PHASE 2 SWANSFIELD ELEMENTARY SCHOOL 5610 CEDAR LANE COLUMBIA, MD 21044 PREPARED FOR: HOWARD COUNTY PUBLIC SCHOOL SYSTEM 10910 ROUTE 108 ELLICOTT

More information

AMBIENT AIR MONITORING PROGRAM MUGGAH CREEK REMEDIATION PROJECT JANUARY 2003 SAMPLING EVENTS FINAL REPORT

AMBIENT AIR MONITORING PROGRAM MUGGAH CREEK REMEDIATION PROJECT JANUARY 2003 SAMPLING EVENTS FINAL REPORT AMBIENT AIR MONITORING PROGRAM MUGGAH CREEK REMEDIATION PROJECT JANUARY 2003 SAMPLING EVENTS FINAL REPORT AMBIENT AIR MONITORING PROGRAM MUGGAH CREEK REMEDIATION PROJECT JANUARY 2003 SAMPLING EVENTS FINAL

More information

INNOVATIVE PRODUCTS, SUPERIOR SUPPORT. Presenter: Anne Jurek, Senior Applications Chemist, EST Analytical

INNOVATIVE PRODUCTS, SUPERIOR SUPPORT. Presenter: Anne Jurek, Senior Applications Chemist, EST Analytical INNOVATIVE PRODUCTS, SUPERIOR SUPPORT Presenter: Anne Jurek, Senior Applications Chemist,, pp, EST Analytical Air pollution is a growing problem due to the global economy and industrial development in

More information

Results of a Sediment Survey in the Near Offshore Waters of the Proposed Quarry Site in the Vicinity of Whites Cove, Digby Neck, Nova Scotia

Results of a Sediment Survey in the Near Offshore Waters of the Proposed Quarry Site in the Vicinity of Whites Cove, Digby Neck, Nova Scotia Results of a Sediment Survey in the Near Offshore Waters of the Proposed Quarry Site in the Vicinity of Whites Cove, Digby Neck, Nova Scotia Prepared for Paul G. Buxton P.O. Box 98 Annapolis Royal, Nova

More information

McCAMPBELL ANALYTICAL INC Willow Pass Road Pittsburg CA

McCAMPBELL ANALYTICAL INC Willow Pass Road Pittsburg CA Comparison of VOC : s, Target Lists, MAI Acenaphthene 83-32-9 Acetalaldehyde (Ethanal) 75-07-0 Acetone 67-64-1 Acetonitrile 75-05-8 Acetophenone 96-86-2 Acrolein (Propenal) 107-02-8 Acrylamide 79-06-1

More information

Optimal Conditions for USEPA Method 8260B Analysis using the EST Analytical Sampling system and the Shimadzu GCMS-QP2010s

Optimal Conditions for USEPA Method 8260B Analysis using the EST Analytical Sampling system and the Shimadzu GCMS-QP2010s JSB is an authorised partner of Optimal Conditions for USEPA Method 8260B Analysis using the EST Analytical Sampling system and the Shimadzu GCMS-QP2010s Anne Jurek #120 Introduction: The USEPA developed

More information

AIR QUALITY SURVEY OF SYNTHETIC TURF FIELDS CONTAINING CRUMB RUBBER INFILL

AIR QUALITY SURVEY OF SYNTHETIC TURF FIELDS CONTAINING CRUMB RUBBER INFILL AIR QUALITY SURVEY OF SYNTHETIC TURF FIELDS CONTAINING CRUMB RUBBER INFILL Prepared for New York City Department of Health and Mental Hygiene New York, NY Prepared by TRC Windsor, Connecticut March 2009

More information

EL608. Deodorants [EL /1/ ]

EL608. Deodorants [EL /1/ ] EL608. Deodorants [EL608-2004/1/2004-125] 1. Scope The criteria shall apply to the chemical deodorant which is used in closed or stuffy space (hereinafter referred to as close space ), or in opened space

More information

Method 8260C by Purge and Trap Gas Chromatography Mass Spectrometry using the Clarus SQ 8

Method 8260C by Purge and Trap Gas Chromatography Mass Spectrometry using the Clarus SQ 8 application Note Gas Chromatography/ Mass Spectrometry Authors Ruben Garnica Dawn May PerkinElmer, Inc. Shelton, CT USA Method by Purge and Trap Gas Chromatography Mass Spectrometry using the Clarus SQ

More information

Application News AD Quantitative Determination of Volatile Organic Compounds in Drinking Water by EPA Method with Headspace Trap GC-MS

Application News AD Quantitative Determination of Volatile Organic Compounds in Drinking Water by EPA Method with Headspace Trap GC-MS HS-20 & GCMS-QP2010Ultra Quantitative Determination of Volatile Organic Compounds in Drinking Water by EPA Method with Headspace Trap GC-MS Introduction Volatile Organic Compounds (VOCs) refer to a group

More information

APPENDIX D Laboratory Analytical Reports

APPENDIX D Laboratory Analytical Reports Allied Aviation Initial Abatement Report, Arlington, VA December 4, 2015 Amec Foster Wheeler Project 37650016 APPENDIX D Laboratory Analytical Reports #=CL# LIMS USE: FR - JOHN MITTAUER LIMS OBJECT ID:

More information

If you have any questions or concerns, please do not hesitate to contact our office at

If you have any questions or concerns, please do not hesitate to contact our office at May 22, 2015 Jeannette DeBartolomeo Environmental Compliance Specialist MDE-OCP 1800 Washington Blvd. Suite 620 Baltimore, MD 21230 RE: Groundwater and Drinking Water Results Calvert Citgo (Former Alger

More information

18/05/2010 Soil. 18/05/2010 Soil

18/05/2010 Soil. 18/05/2010 Soil CERTIFICATE OF ANALYSIS Client: MPL Laboratories 1618 Hayden Court Myaree WA 6153 Attention: Tania Notaras Sample log in details: : No. of samples: Date samples received: Date completed instructions received:

More information

Readiness thru Health

Readiness thru Health DEPARTMENT OF THE ARMY US ARMY CENTER FOR HEALTH PROMOTION AND PREVENTIVE MEDICINE 5158 BLACKHAWK ROAD ABERDEEN PROVING GROUND MD 21010-5403 MCHB-TS-RDE - MEMORANDUM FOR Command Surgeon (LTC (b) (6) ),

More information

METHOD 5021 VOLATILE ORGANIC COMPOUNDS IN SOILS AND OTHER SOLID MATRICES USING EQUILIBRIUM HEADSPACE ANALYSIS

METHOD 5021 VOLATILE ORGANIC COMPOUNDS IN SOILS AND OTHER SOLID MATRICES USING EQUILIBRIUM HEADSPACE ANALYSIS METHOD 5021 VOLATILE ORGANIC COMPOUNDS IN SOILS AND OTHER SOLID MATRICES USING EQUILIBRIUM HEADSPACE ANALYSIS 1.0 SCOPE AND APPLICATION 1.1 Method 5021 is a general purpose method for the preparation of

More information

Optimizing Standard Preparation

Optimizing Standard Preparation JSB is an authorised partner of Optimizing Standard Preparation Anne Jurek #106 Abstract: Standard preparation can often be a time consuming, tedious process. The opportunity for human error or inconsistencies

More information

Cape Cross Salt Works PO Box 81307, Windhoek, Namibia. FINAL REPORT rev1 NHN170 NOVEMBER 2016

Cape Cross Salt Works PO Box 81307, Windhoek, Namibia. FINAL REPORT rev1 NHN170 NOVEMBER 2016 Cape Cross Salt Works PO Box 81307, Windhoek, Namibia GROUNDWATER EXPLORATION FOR SUPPLY TO THE CAPE CROSS SALT WORKS FINAL REPORT rev1 NHN170 NOVEMBER 2016 Namib Hydrosearch, PO Box 11546 Windhoek Namibia,

More information

ANALYTICAL REPORT. Results relate only to the items tested and the sample(s) as received by the laboratory. Page 1 of 5

ANALYTICAL REPORT. Results relate only to the items tested and the sample(s) as received by the laboratory. Page 1 of 5 ANALYTICAL REPORT TestAmerica Laboratories, Inc. TestAmerica Savannah 5102 LaRoche Avenue Savannah, GA 31404 Tel: (912)354-7858 Client For: Imperial Paints LLC PO BOX 489 Fairforest, South Carolina 29336

More information

Eastwood & Partners St. Andrew's House 23 Kingfield Road Sheffield S11 9AS. Co-ords: Level: Dimensions: Depth 1.50m

Eastwood & Partners St. Andrew's House 23 Kingfield Road Sheffield S11 9AS. Co-ords: Level: Dimensions: Depth 1.50m epth (m) 0.0 Kingfield Road S AS Coords: imensions: epth.0m epth Level (m) (m AO) Stratum escription 0.0m.0m TOPSOIL: Brown sandy gravelly with rootlets. Gravel is angular to subrounded fine to coarse

More information

Indoor Air Sampling and Forensic Analysis at Peter Cooper Village and Stuyvesant Town Properties October 2017

Indoor Air Sampling and Forensic Analysis at Peter Cooper Village and Stuyvesant Town Properties October 2017 Indoor Air Sampling and Forensic Analysis at Peter Cooper Village and Stuyvesant Town Properties October 2017 Prepared by: Anchor QEA 90 Elwood Davis Rd, Suite 340 Liverpool, NY 13088 Prepared for: Consolidated

More information

2017 EPA Method Update Rule and EPA Method 624.1

2017 EPA Method Update Rule and EPA Method 624.1 Introduction Method 624 is for the determination of volatile organic compounds in industrial discharges and other liquid environmental samples by gas chromatography combined with mass spectrometry (GC/MS).

More information

Patos-Marinza Development Project. Well 5761 ERP Contamination Assessment Report

Patos-Marinza Development Project. Well 5761 ERP Contamination Assessment Report Patos-arinza Development Project Well 5761 ERP Contamination Assessment Report ay 2015 1 Executive Summary Environmental Contamination Assessment Bankers Petroleum Albania Limited (BPAL) has prepared this

More information

CENTRAL LABORATORY. Sl. No. Type of sampling Charges in Rs. 1. GRAB SAMPLING:

CENTRAL LABORATORY. Sl. No. Type of sampling Charges in Rs. 1. GRAB SAMPLING: E-mail: centrallab@ospcboard.org Website : www.ospcboard.org CENTRAL LABORATORY STATE POLLUTION CONTROL BOARD, ODISHA [DEPARTMENT OF FOREST & ENVIRONMENT, GOVERNMENT OF ODISHA] Plot B-59/2 & 59/3, Chandaka

More information

Analysis of Low Level Volatile Organic Compounds in Air Anne Jurek

Analysis of Low Level Volatile Organic Compounds in Air Anne Jurek JSB is an authorised partner of Analysis of Low Level Volatile Organic s in Air Anne Jurek #111 Introduction The New Jersey Department of Environmental Protection (NJDEP) developed a new low level TO-15

More information

Volatile Organic Compounds in Water PBM

Volatile Organic Compounds in Water PBM Organic Constituents and Compounds Revision Date: July 10, 2017 Volatile Organic Compounds in Water PBM Parameter Analytical Method Introduction Method Summary MDL(s) and EMS Analyte Codes Volatile Organic

More information