REQUEST_ID|JOB_ID|SAMPLE_ID|SAMPLE_SITE|FIELD_ID|SAMPLE_DATE|SAMPLE_TIME|ANALYSIS_DATE|ANALYSIS_TIME|PARAM_CODE|PARAM_NAME|RESULT|VALUE_QUAL|UOM|MDL|PQL|PREP_METHOD|PREP_DESC|PREP_DATE|PREP_TIME|ANALYSIS_METHOD|SAMPLER|LAB_COMMENTS
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|15-NOV-2023|22:15||Total Alkalinity|129||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|14:09|76|Turbidity|1.6||NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|16-NOV-2023|08:47|940|Chloride|160||mg Cl/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|15:31|80|Color (true)|57||PCU|2.5|6.0|||||DEP SOP: NU-094-1|Nicole Reistad, Other|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|15-NOV-2023|22:15|951|Fluoride|0.55||mg F/L|0.025|0.10|||||SM 4500-F- C-2011|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|16-NOV-2023|08:47|945|Sulfate|150||mg SO4/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|09-NOV-2023|13:42|70300|TDS|572||mg/L|30|50|||||SM 2540 C-2015|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449845|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|09-NOV-2023|13:42|530|TSS|2|I|mg/L|2.0|10|||||SM 2540 D-2015|Nicole Reistad, Other|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-29|2449846|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|28-NOV-2023|11:47|610|Ammonia-N|0.031||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449846|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|17-NOV-2023|12:08|630|NO2NO3-N|0.44||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449846|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|19:19|665|Total-P|0.19||mg P/L|0.010|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|14-NOV-2023|15:38|EPA 365.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449846|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|15:14|625|Kjeldahl Nitrogen|0.82|J|mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|09-NOV-2023|11:24|EPA 351.2 Rev. 2.0|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-29|2449846|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|20:12|680|Organic Carbon|13||mg C/L|0.50|1.0|||||SM 5310 B-2014|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|15-NOV-2023|23:31||Total Alkalinity|0.65|U|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|14:12|76|Turbidity|0.10|U|NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|16-NOV-2023|09:02|940|Chloride|0.20|U|mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|15:32|80|Color (true)|2.5|U|PCU|2.5|6.0|||||DEP SOP: NU-094-1|Nicole Reistad, Other|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|15-NOV-2023|23:31|951|Fluoride|0.025|U|mg F/L|0.025|0.10|||||SM 4500-F- C-2011|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|16-NOV-2023|09:02|945|Sulfate|0.20|U|mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|09-NOV-2023|13:42|70300|TDS|15|U|mg/L|15|25|||||SM 2540 C-2015|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449847|FB|FB_11072023|07-NOV-2023|11:50|09-NOV-2023|13:42|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2015|Nicole Reistad, Other|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-29|2449848|FB|FB_11072023|07-NOV-2023|11:50|17-NOV-2023|15:02|610|Ammonia-N|0.002|U|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449848|FB|FB_11072023|07-NOV-2023|11:50|17-NOV-2023|12:09|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449848|FB|FB_11072023|07-NOV-2023|11:50|15-NOV-2023|12:15|665|Total-P|0.002|U|mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|14-NOV-2023|15:38|EPA 365.1 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449848|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|15:19|625|Kjeldahl Nitrogen|0.080|U|mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|09-NOV-2023|11:24|EPA 351.2 Rev. 2.0|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-29|2449848|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|20:54|680|Organic Carbon|0.50|U|mg C/L|0.50|1.0|||||SM 5310 B-2014|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-DEC-2023|03:25||Chlordane|2.1|U|ng/L|2.1|6.4|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8276|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-DEC-2023|03:25||Toxaphene|15|U|ng/L|15|39|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8276|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1016|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1221|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1232|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1242|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1248|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1254|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:28||PCB-1260|2.1|UJ|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39330|Aldrin|0.67|U|ng/L|0.67|3.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39337|Alpha-BHC|0.10|U|ng/L|0.10|0.51|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Alpha-Chlordane|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39338|Beta-BHC|0.10|U|ng/L|0.10|0.51|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Beta-Cyfluthrin|1.3|U|ng/L|1.3|6.4|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Bifenthrin|0.51|U|ng/L|0.51|2.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39786|Carbophenothion|0.92|U|ng/L|0.92|4.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|70314|Chlorothalonil|3.7|U|ng/L|3.7|18|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Cis-Nonachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|3781|Cypermethrin|1.5|U|ng/L|1.5|7.7|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39310|DDD-p,p'|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39320|DDE-p,p'|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39300|DDT-p,p'|0.82|U|ng/L|0.82|4.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Dacthal|0.15|U|ng/L|0.15|0.77|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|34259|Delta-BHC|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Deltamethrin|1.3|U|ng/L|1.3|6.4|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Dichlobenil|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Dicofol|1.3|U|ng/L|1.3|6.4|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39380|Dieldrin|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|34361|Endosulfan I|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|34356|Endosulfan II|0.92|U|ng/L|0.92|4.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|34351|Endosulfan Sulfate|0.31|U|ng/L|0.31|1.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39390|Endrin|0.92|U|ng/L|0.92|4.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|34366|Endrin Aldehyde|0.77|U|ng/L|0.77|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Endrin Ketone|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Esfenvalerate|0.77|U|ng/L|0.77|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Ethalfluralin|0.15|U|ng/L|0.15|0.77|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Fenpropathrin|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39340|Gamma-BHC|0.13|U|ng/L|0.13|0.64|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Gamma-Chlordane|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39410|Heptachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39420|Heptachlor Epoxide|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Hexachlorobenzene|1.0|U|ng/L|1.0|5.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Kepone|14|U|ng/L|14|69|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Lambda-Cyhalothrin|0.77|U|ng/L|0.77|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||MGK-264|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Methoprene|0.77|U|ng/L|0.77|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39480|Methoxychlor|0.31|U|ng/L|0.31|1.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|39755|Mirex|0.36|U|ng/L|0.36|1.8|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Oxychlordane|0.31|U|ng/L|0.31|1.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|79191|Permethrin|1.6|U|ng/L|1.6|8.2|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Phenothrin|0.92|U|ng/L|0.92|4.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Piperonyl Butoxide|0.15|U|ng/L|0.15|0.77|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Prallethrin|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Tau-Fluvalinate|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Tetramethrin|0.77|U|ng/L|0.77|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Trans-Nonachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13||Triclosan Methyl|0.15|U|ng/L|0.15|0.77|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-35|2449880|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|28-NOV-2023|00:13|81284|Trifluralin|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|13-NOV-2023|08:00|EPA 8270E|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|08-NOV-2023|21:26||AMPA|0.16|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|09-NOV-2023|23:53||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|08-NOV-2023|21:26||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|08-NOV-2023|21:26||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|08-NOV-2023|21:26||Glyphosate|0.11|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|09-NOV-2023|23:53||Sucralose|0.030|I|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06|39730|2,4-D|0.010||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Clothianidin|0.0028|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Diuron|0.0054|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Imazapyr|0.028||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Imidacloprid|0.017||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449881|CHARLIE CREEK UP STRM HWY 17|G3SD0237|07-NOV-2023|09:55|14-NOV-2023|20:06||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|08-NOV-2023|22:08||AMPA|2.2||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|09-NOV-2023|18:16||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|08-NOV-2023|22:08||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|08-NOV-2023|22:08||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|08-NOV-2023|22:08||Glyphosate|0.78||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|09-NOV-2023|18:16||Sucralose|1.7||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24|39730|2,4-D|0.017||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Carbamazepine|0.0046||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Clothianidin|0.26||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Diuron|0.018||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Imazapyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Imidacloprid|0.49||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Primidone|0.0051|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Thiamethoxam|0.34||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449882|HOG BAY AT CR 763|G3SD0096|07-NOV-2023|10:40|14-NOV-2023|20:24||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-NOV-2023|22:21||AMPA|1.3||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|10-NOV-2023|00:07||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-NOV-2023|22:21||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-NOV-2023|22:21||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|08-NOV-2023|22:21||Glyphosate|1.3||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|10-NOV-2023|00:07||Sucralose|0.54||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42|39730|2,4-D|0.32||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Bentazon|0.0056||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Carbamazepine|0.0013|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Clothianidin|0.073||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Diuron|0.14||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Imazapyr|0.025||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Imidacloprid|0.22||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Thiamethoxam|0.11||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449883|JOSHUA CREEK ABOVE PEACE RIVER|G3SD0159|07-NOV-2023|11:05|14-NOV-2023|20:42||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|22:35||AMPA|1.9||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|09-NOV-2023|18:44||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|22:35||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|22:35||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|08-NOV-2023|22:35||Glyphosate|2.5||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|09-NOV-2023|18:44||Sucralose|0.71||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00|39730|2,4-D|0.81||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Bentazon|0.014||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Carbamazepine|0.0017|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Clothianidin|0.12||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Diuron|0.43||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Fenuron|0.056|I|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Imazapyr|0.0086|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Imidacloprid|0.27||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Thiamethoxam|0.16||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449884|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|21:00||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|22:49||AMPA|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|09-NOV-2023|18:58||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|22:49||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|22:49||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|08-NOV-2023|22:49||Glyphosate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|09-NOV-2023|18:58||Sucralose|0.010|U|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|08-NOV-2023|16:00|EPA 8321B|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18|39730|2,4-D|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Imazapyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Imidacloprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-36|2449885|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|21:18||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|13-NOV-2023|09:00|EPA 8321B|Nicole Reistad, Other|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|46570|Hardness|346||mg/L|0.35|1.4|||||SM 2340 B-2011|Nicole Reistad, Other|
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|916|Calcium|94.3||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1045|Iron|170||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|927|Magnesium|26.9||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|937|Potassium|8.6||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|929|Sodium|65.6||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1082|Strontium|7.02E+03||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1152|Titanium|0.98|I|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1087|Vanadium|2.9|I|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|19:43|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1105|Aluminum|39||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|14-NOV-2023|17:24|1097|Antimony|0.66||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1002|Arsenic|1.26||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1007|Barium|36.2||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1012|Beryllium|0.012|I|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1022|Boron|64.8||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1027|Cadmium|0.075|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1034|Chromium|0.42|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1037|Cobalt|0.117||ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1042|Copper|0.87||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1055|Manganese|25.1||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1062|Molybdenum|2.49||ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1067|Nickel|1.6|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1147|Selenium|0.25|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449886|HAWTHORNE CREEK AT REYNOLDS ST|G3SD0011|07-NOV-2023|11:35|13-NOV-2023|21:44|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|916|Calcium|0.075|U|mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1045|Iron|30|U|ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|927|Magnesium|0.040|U|mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|937|Potassium|0.30|U|mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|929|Sodium|0.50|U|mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1082|Strontium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1152|Titanium|0.75|U|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1087|Vanadium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|17:21|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.7 Rev. 4.4|Nicole Reistad, Other|Batch matrix spike recoveries for titanium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1105|Aluminum|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|14-NOV-2023|15:39|1097|Antimony|0.050|U|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1002|Arsenic|0.050|U|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1007|Barium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1012|Beryllium|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1022|Boron|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1034|Chromium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1037|Cobalt|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1042|Copper|0.40|U|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1055|Manganese|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1062|Molybdenum|0.15|U|ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1067|Nickel|0.50|U|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2023-11-06-61|TLH-2023-11-08-37|2449887|FB|FB_11072023|07-NOV-2023|11:50|13-NOV-2023|18:11|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|09-NOV-2023|13:40|EPA 200.8 Rev. 5.4|Nicole Reistad, Other|Batch matrix spike recoveries for aluminum are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.