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-2022-08-01-45|TLH-2022-08-03-69|2345625|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|10-AUG-2022|22:53||Total Alkalinity|87|A|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345625|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|03-AUG-2022|14:25|76|Turbidity|1.8||NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345625|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|10-AUG-2022|21:04|951|Fluoride|0.61||mg F/L|0.070|0.20|||||SM 4500-F- C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345625|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|16:02|530|TSS|3|IA|mg/L|3.0|10|||||SM 2540 D-2011|Monica Jaeger, Nicole Reistad|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345626|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|08-AUG-2022|15:21|610|Ammonia-N|0.12||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345626|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|11:11|630|NO2NO3-N|0.11||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345626|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|10-AUG-2022|15:51|665|Total-P|0.40||mg P/L|0.010|0.10|365.1 (MARCH 1983)|Automated, ascorbic acid|09-AUG-2022|09:37|EPA 365.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345626|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|15:30|625|Kjeldahl Nitrogen|1.2||mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|05-AUG-2022|10:08|EPA 351.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345626|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|10-AUG-2022|00:55|680|Organic Carbon|18||mg C/L|1.0|2.0|||||SM 5310 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345627|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|13-AUG-2022|09:53||Total Alkalinity|64||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345627|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|03-AUG-2022|14:34|76|Turbidity|3.4||NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345627|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|10-AUG-2022|06:09|951|Fluoride|0.46||mg F/L|0.035|0.10|||||SM 4500-F- C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345627|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|16:02|530|TSS|3|I|mg/L|2.0|10|||||SM 2540 D-2011|Monica Jaeger, Nicole Reistad|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345628|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|08-AUG-2022|16:11|610|Ammonia-N|0.046||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345628|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|10-AUG-2022|09:16|630|NO2NO3-N|0.24||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345628|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|10-AUG-2022|16:00|665|Total-P|0.69||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|09-AUG-2022|09:37|EPA 365.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|Total-P: Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345628|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|15:53|625|Kjeldahl Nitrogen|1.4||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|05-AUG-2022|10:08|EPA 351.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345628|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|06-AUG-2022|03:45|680|Organic Carbon|25||mg C/L|0.50|1.0|||||SM 5310 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|13-AUG-2022|08:13||Total Alkalinity|64||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|03-AUG-2022|14:28|76|Turbidity|4.5|A|NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|09-AUG-2022|09:57|940|Chloride|26||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|03-AUG-2022|15:52|80|Color (true)|300||PCU|12|30|||||DEP SOP: NU-094-1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|23-AUG-2022|23:09|951|Fluoride|0.48||mg F/L|0.035|0.10|||||SM 4500-F- C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|09-AUG-2022|09:57|945|Sulfate|42||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|16:02|70300|TDS|239||mg/L|15|25|||||SM 2540 C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345629|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|16:02|530|TSS|5|I|mg/L|2.0|10|||||SM 2540 D-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345630|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|08-AUG-2022|16:13|610|Ammonia-N|0.043||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345630|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|09:18|630|NO2NO3-N|0.41||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345630|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|16:06|665|Total-P|0.75||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|09-AUG-2022|09:37|EPA 365.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|Total-P: Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345630|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|11-AUG-2022|13:37|625|Kjeldahl Nitrogen|1.6||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|08-AUG-2022|14:48|EPA 351.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345630|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|06-AUG-2022|04:30|680|Organic Carbon|27||mg C/L|0.50|1.0|||||SM 5310 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345631|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|10-AUG-2022|23:49||Total Alkalinity|113||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345631|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|03-AUG-2022|14:35|76|Turbidity|2.9||NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345631|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|10-AUG-2022|21:33|951|Fluoride|0.80||mg F/L|0.18|0.50|||||SM 4500-F- C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345631|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|05-AUG-2022|16:02|530|TSS|8|I|mg/L|3.0|10|||||SM 2540 D-2011|Monica Jaeger, Nicole Reistad|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345632|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|19-AUG-2022|11:52|610|Ammonia-N|0.01||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345632|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|11:12|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345632|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|10-AUG-2022|15:52|665|Total-P|0.23||mg P/L|0.010|0.10|365.1 (MARCH 1983)|Automated, ascorbic acid|09-AUG-2022|09:37|EPA 365.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345632|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|12-AUG-2022|09:46|625|Kjeldahl Nitrogen|1.1||mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|09-AUG-2022|15:02|EPA 351.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345632|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|10-AUG-2022|03:53|680|Organic Carbon|16||mg C/L|1.0|2.0|||||SM 5310 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|13-AUG-2022|08:20||Total Alkalinity|0.65|U|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|03-AUG-2022|14:38|76|Turbidity|0.10|U|NTU|0.10|1.0|||||EPA 180.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|09-AUG-2022|10:09|940|Chloride|0.20|U|mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|03-AUG-2022|15:37|80|Color (true)|2.5|U|PCU|2.5|6.0|||||DEP SOP: NU-094-1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|10-AUG-2022|06:18|951|Fluoride|0.035|U|mg F/L|0.035|0.10|||||SM 4500-F- C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|09-AUG-2022|10:09|945|Sulfate|0.20|U|mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|16:02|70300|TDS|15|U|mg/L|15|25|||||SM 2540 C-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345633|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|16:02|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|Monica Jaeger, Nicole Reistad|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345634|FB|FB_08022022|02-AUG-2022|11:25|09-AUG-2022|11:15|610|Ammonia-N|0.002|U|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345634|FB|FB_08022022|02-AUG-2022|11:25|10-AUG-2022|09:19|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-69|2345634|FB|FB_08022022|02-AUG-2022|11:25|11-AUG-2022|10:47|665|Total-P|0.002|U|mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|09-AUG-2022|09:37|EPA 365.1 Rev. 2.0|Monica Jaeger, Nicole Reistad|Total-P: Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345634|FB|FB_08022022|02-AUG-2022|11:25|11-AUG-2022|14:28|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|08-AUG-2022|14:48|EPA 351.2 Rev. 2.0|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-69|2345634|FB|FB_08022022|02-AUG-2022|11:25|06-AUG-2022|04:45|680|Organic Carbon|0.50|U|mg C/L|0.50|1.0|||||SM 5310 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Acetochlor|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Alachlor|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|82184|Ametryn|0.58|U|ng/L|0.58|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|22:13|39033|Atrazine|43||ng/L|2.4|9.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Atrazine Desethyl|1.5|U|ng/L|1.5|5.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Azinphos Methyl|1.9|U|ng/L|1.9|7.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Azoxystrobin|2.8||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Bromacil|29||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Butylate|0.39|U|ng/L|0.39|1.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Caffeine|7.3|U|ng/L|7.3|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Carbophenothion|0.19|U|ng/L|0.19|0.77|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Carfentrazone Ethyl|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Chlorfenapyr|0.17|U|ng/L|0.17|0.68|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|38932|Chlorpyrifos Ethyl|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|38740|Chlorpyrifos Methyl|0.048|U|ng/L|0.048|0.19|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Coumaphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Cyanazine|3.1|U|ng/L|3.1|13|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Cyprodinil|0.097|U|ng/L|0.097|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Demeton|1.5|U|ng/L|1.5|5.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Diazinon|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Difenoconazole|0.58|U|ng/L|0.58|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Dimethenamid|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Dimethomorph|0.17|U|ng/L|0.17|1.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|81888|Disulfoton|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Dithiopyr|0.17|U|ng/L|0.17|0.68|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||EPTC|1.2|U|ng/L|1.2|4.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39398|Ethion|0.15|UJ|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|81758|Ethoprop|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Etridiazole|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fenamiphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fenbuconazole|1.3||ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fipronil|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fipronil Desulfinyl|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fipronil Sulfide|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fipronil Sulfone|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fluazifop-P-butyl|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fludioxonil|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Flumioxazin|1.7|U|ng/L|1.7|6.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Flutolanil|1.2||ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fluxapyroxad|0.32|I|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Fonofos|0.19|U|ng/L|0.19|0.77|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|22:13|38815|Hexazinone|120||ng/L|4.8|19|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Imazalil|0.73|U|ng/L|0.73|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Iprodione|0.58|U|ng/L|0.58|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Loratadine|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39530|Malathion|0.34|U|ng/L|0.34|1.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Metalaxyl|27||ng/L|0.73|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Metolachlor|38||ng/L|0.34|1.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|81408|Metribuzin|2.4|U|ng/L|2.4|9.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39610|Mevinphos|1.0|U|ng/L|1.0|4.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Molinate|0.29|U|ng/L|0.29|1.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Myclobutanil|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Naled|1.5|U|ng/L|1.5|5.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Napropamide|0.39|U|ng/L|0.39|1.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|78064|Norflurazon|74||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Oxadiazon|0.32|I|ng/L|0.29|1.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Oxyfluorfen|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Parathion Ethyl|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Parathion Methyl|0.53|U|ng/L|0.53|2.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Pendimethalin|0.97|U|ng/L|0.97|3.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Phenytoin|3.4|U|ng/L|3.4|14|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|46313|Phorate|0.51|U|ng/L|0.51|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Prodiamine|0.17|U|ng/L|0.17|0.68|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39056|Prometon|0.87|U|ng/L|0.87|3.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39057|Prometryn|0.19|U|ng/L|0.19|0.77|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Pronamide|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Propanil|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Propargite|1.5|UJ|ng/L|1.5|5.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Propiconazole|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Pyraflufen Ethyl|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Pyridaben|0.44|U|ng/L|0.44|2.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Pyriproxyfen|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|39055|Simazine|2.6||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Stirophos|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Sulfentrazone|2.1||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Tebuconazole|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03|82088|Terbufos|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Terbuthylazine|0.41|U|ng/L|0.41|1.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Thiobencarb|0.58|U|ng/L|0.58|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|04:03||Triadimefon|0.84|I|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||2-Ethylhexyl 2,3,4,5-tetrabromobenzoate (EHTBB)|12|U|ng/L|12|35|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||Avobenzone|97|U|ng/L|97|290|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||Octinoxate|19|U|ng/L|19|58|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||Oxybenzone|9.7|U|ng/L|9.7|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||PBDE-47|3.9|U|ng/L|3.9|12|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||PBDE-99|4.8|U|ng/L|4.8|15|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345646|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|09-AUG-2022|17:14||Tri-o-cresyl Phosphate|5.8|U|ng/L|5.8|17|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Acetochlor|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Alachlor|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|82184|Ametryn|1.3|I|ng/L|0.59|2.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|23:05|39033|Atrazine|52||ng/L|2.5|9.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Atrazine Desethyl|3.7|I|ng/L|1.5|5.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Azinphos Methyl|2.0|U|ng/L|2.0|7.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Azoxystrobin|3.8||ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Bromacil|62||ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Butylate|0.39|U|ng/L|0.39|1.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Caffeine|7.4|U|ng/L|7.4|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Carbophenothion|0.20|U|ng/L|0.20|0.79|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Carfentrazone Ethyl|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Chlorfenapyr|0.17|U|ng/L|0.17|0.69|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|38932|Chlorpyrifos Ethyl|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|38740|Chlorpyrifos Methyl|0.049|U|ng/L|0.049|0.20|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Coumaphos|0.49|U|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Cyanazine|3.2|U|ng/L|3.2|13|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Cyprodinil|0.098|U|ng/L|0.098|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Demeton|1.5|U|ng/L|1.5|5.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Diazinon|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Difenoconazole|0.59|U|ng/L|0.59|2.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Dimethenamid|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Dimethomorph|0.17|U|ng/L|0.17|1.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|81888|Disulfoton|0.49|U|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Dithiopyr|0.17|U|ng/L|0.17|0.69|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||EPTC|1.2|U|ng/L|1.2|4.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39398|Ethion|0.15|UJ|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|81758|Ethoprop|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Etridiazole|0.15|U|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fenamiphos|0.49|U|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fenbuconazole|0.61||ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fipronil|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fipronil Desulfinyl|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fipronil Sulfide|0.15|U|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fipronil Sulfone|0.15|U|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fluazifop-P-butyl|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fludioxonil|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Flumioxazin|1.7|U|ng/L|1.7|6.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Flutolanil|0.48||ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|23:32||Fluxapyroxad|0.55||ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Fonofos|0.20|U|ng/L|0.20|0.79|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|23:05|38815|Hexazinone|150||ng/L|4.9|20|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Imazalil|0.74|U|ng/L|0.74|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Iprodione|0.59|U|ng/L|0.59|2.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Loratadine|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39530|Malathion|0.34|U|ng/L|0.34|1.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Metalaxyl|17||ng/L|0.74|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Metolachlor|67||ng/L|0.34|1.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|81408|Metribuzin|2.5|U|ng/L|2.5|9.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39610|Mevinphos|1.0|U|ng/L|1.0|4.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Molinate|0.29|U|ng/L|0.29|1.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Myclobutanil|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Naled|1.5|U|ng/L|1.5|5.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Napropamide|0.39|U|ng/L|0.39|1.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|23:05|78064|Norflurazon|120||ng/L|4.9|20|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Oxadiazon|1.2||ng/L|0.29|1.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Oxyfluorfen|0.15|U|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Parathion Ethyl|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Parathion Methyl|0.54|U|ng/L|0.54|2.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Pendimethalin|0.98|U|ng/L|0.98|3.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Phenytoin|3.4|U|ng/L|3.4|14|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|46313|Phorate|0.52|U|ng/L|0.52|2.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Prodiamine|0.17|U|ng/L|0.17|0.69|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39056|Prometon|0.88|U|ng/L|0.88|3.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39057|Prometryn|0.20|U|ng/L|0.20|0.79|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Pronamide|0.15|U|ng/L|0.15|0.59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Propanil|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Propargite|1.5|UJ|ng/L|1.5|5.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Propiconazole|0.49|U|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Pyraflufen Ethyl|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Pyridaben|0.44|U|ng/L|0.44|2.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Pyriproxyfen|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|39055|Simazine|1.9|I|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Stirophos|0.12|U|ng/L|0.12|0.49|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Sulfentrazone|3.8||ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Tebuconazole|0.49|U|ng/L|0.49|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30|82088|Terbufos|0.098|U|ng/L|0.098|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Terbuthylazine|0.42|U|ng/L|0.42|1.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Thiobencarb|0.59|U|ng/L|0.59|2.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|04:30||Triadimefon|0.25|U|ng/L|0.25|0.98|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this paremeter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||2-Ethylhexyl 2,3,4,5-tetrabromobenzoate (EHTBB)|12|U|ng/L|12|35|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||Avobenzone|98|U|ng/L|98|290|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||Octinoxate|20|U|ng/L|20|59|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||Oxybenzone|9.8|U|ng/L|9.8|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||PBDE-47|3.9|U|ng/L|3.9|12|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||PBDE-99|4.9|U|ng/L|4.9|15|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345647|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|09-AUG-2022|17:33||Tri-o-cresyl Phosphate|5.9|U|ng/L|5.9|18|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|05:53||Chlordane|3.0|I|ng/L|2.6|13|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8276|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|05:53||Toxaphene|16|U|ng/L|16|78|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8276|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1016|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1221|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1232|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1242|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1248|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1254|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|12-AUG-2022|00:47||PCB-1260|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39330|Aldrin|0.67|U|ng/L|0.67|3.4|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39337|Alpha-BHC|0.10|U|ng/L|0.10|0.52|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Alpha-Chlordane|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39338|Beta-BHC|0.10|U|ng/L|0.10|0.52|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Beta-Cyfluthrin|1.3|U|ng/L|1.3|6.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Bifenthrin|0.52|U|ng/L|0.52|2.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39786|Carbophenothion|0.93|U|ng/L|0.93|4.7|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|70314|Chlorothalonil|1.3|U|ng/L|1.3|7.8|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Cis-Nonachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|3781|Cypermethrin|1.6|U|ng/L|1.6|7.8|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|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|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|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|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39300|DDT-p,p'|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Dacthal|0.16|U|ng/L|0.16|0.78|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|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|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Deltamethrin|1.3|U|ng/L|1.3|6.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Dichlobenil|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Dicofol|1.3|U|ng/L|1.3|6.5|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39380|Dieldrin|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|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|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|34356|Endosulfan II|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|34351|Endosulfan Sulfate|0.31|U|ng/L|0.31|1.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39390|Endrin|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|34366|Endrin Aldehyde|0.78|U|ng/L|0.78|3.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Endrin Ketone|0.41|U|ng/L|0.41|2.1|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Esfenvalerate|0.81|I|ng/L|0.78|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Ethalfluralin|0.16|U|ng/L|0.16|0.78|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Fenpropathrin|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39340|Gamma-BHC|0.13|U|ng/L|0.13|0.65|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Gamma-Chlordane|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39410|Heptachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|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|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Hexachlorobenzene|1.0|U|ng/L|1.0|5.2|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Kepone|5.2|UJ|ng/L|5.2|26|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Lambda-Cyhalothrin|0.78|U|ng/L|0.78|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||MGK-264|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Methoprene|0.78|U|ng/L|0.78|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39480|Methoxychlor|0.31|U|ng/L|0.31|1.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|39755|Mirex|0.36|U|ng/L|0.36|1.8|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Oxychlordane|0.31|U|ng/L|0.31|1.6|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|79191|Permethrin|2.6|I|ng/L|1.7|8.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Phenothrin|0.93|U|ng/L|0.93|4.7|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Piperonyl Butoxide|0.46|I|ng/L|0.16|0.78|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Prallethrin|2.1|U|ng/L|2.1|10|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Tau-Fluvalinate|0.26|U|ng/L|0.26|1.3|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Tetramethrin|0.78|U|ng/L|0.78|3.9|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Trans-Nonachlor|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30||Triclosan Methyl|0.16|U|ng/L|0.16|0.78|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345648|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|10-AUG-2022|18:30|81284|Trifluralin|0.21|U|ng/L|0.21|1.0|3535A (GC)|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|08-AUG-2022|08:30|EPA 8270E|Monica Jaeger, Nicole Reistad|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Acetochlor|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Alachlor|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|82184|Ametryn|1.1|I|ng/L|0.57|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|23:58|39033|Atrazine|14||ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Atrazine Desethyl|1.4|U|ng/L|1.4|5.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Azinphos Methyl|1.9|U|ng/L|1.9|7.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Azoxystrobin|0.88|I|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Bromacil|9.5||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Butylate|0.38|U|ng/L|0.38|1.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Caffeine|7.1|U|ng/L|7.1|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Carbophenothion|0.19|U|ng/L|0.19|0.76|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Carfentrazone Ethyl|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Chlorfenapyr|0.17|U|ng/L|0.17|0.67|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|38932|Chlorpyrifos Ethyl|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|38740|Chlorpyrifos Methyl|0.048|U|ng/L|0.048|0.19|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Coumaphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Cyanazine|3.1|U|ng/L|3.1|12|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Cyprodinil|0.095|U|ng/L|0.095|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Demeton|1.4|U|ng/L|1.4|5.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Diazinon|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Difenoconazole|0.57|U|ng/L|0.57|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Dimethenamid|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Dimethomorph|0.41|I|ng/L|0.17|1.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|81888|Disulfoton|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Dithiopyr|0.17|U|ng/L|0.17|0.67|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||EPTC|1.2|U|ng/L|1.2|4.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39398|Ethion|0.14|UJ|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|81758|Ethoprop|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Etridiazole|0.14|U|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fenamiphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fenbuconazole|0.31|I|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fipronil|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fipronil Desulfinyl|0.18|I|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fipronil Sulfide|0.14|U|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fipronil Sulfone|0.14|U|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fluazifop-P-butyl|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fludioxonil|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Flumioxazin|1.7|U|ng/L|1.7|6.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Flutolanil|0.60||ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|23:58||Fluxapyroxad|1.1||ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Fonofos|0.19|U|ng/L|0.19|0.76|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|38815|Hexazinone|30||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Imazalil|0.71|U|ng/L|0.71|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Iprodione|0.57|U|ng/L|0.57|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Loratadine|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39530|Malathion|1.1|I|ng/L|0.33|1.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Metalaxyl|15||ng/L|0.71|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Metolachlor|1.3|I|ng/L|0.33|1.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|81408|Metribuzin|2.4|U|ng/L|2.4|9.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39610|Mevinphos|1.0|U|ng/L|1.0|4.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Molinate|0.29|U|ng/L|0.29|1.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Myclobutanil|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Naled|1.4|U|ng/L|1.4|5.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Napropamide|0.38|U|ng/L|0.38|1.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|78064|Norflurazon|20||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Oxadiazon|0.34|I|ng/L|0.29|1.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Oxyfluorfen|0.14|U|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Parathion Ethyl|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Parathion Methyl|0.52|U|ng/L|0.52|2.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Pendimethalin|0.95|U|ng/L|0.95|3.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Phenytoin|3.3|U|ng/L|3.3|13|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|46313|Phorate|0.50|U|ng/L|0.50|2.0|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Prodiamine|0.17|U|ng/L|0.17|0.67|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39056|Prometon|0.86|U|ng/L|0.86|3.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39057|Prometryn|0.19|U|ng/L|0.19|0.76|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Pronamide|0.14|U|ng/L|0.14|0.57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Propanil|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Propargite|1.4|UJ|ng/L|1.4|5.7|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Propiconazole|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Pyraflufen Ethyl|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Pyridaben|0.43|U|ng/L|0.43|2.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Pyriproxyfen|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|39055|Simazine|3.2||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Stirophos|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Sulfentrazone|1.3|I|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Tebuconazole|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57|82088|Terbufos|0.095|U|ng/L|0.095|0.38|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Terbuthylazine|0.40|U|ng/L|0.40|1.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Thiobencarb|0.57|U|ng/L|0.57|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|04:57||Triadimefon|0.24|U|ng/L|0.24|0.95|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|MS accuracy for atrazine not assessed due to high content of this parameter in the sample spiked. Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||2-Ethylhexyl 2,3,4,5-tetrabromobenzoate (EHTBB)|11|U|ng/L|11|34|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||Avobenzone|95|U|ng/L|95|290|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||Octinoxate|19|U|ng/L|19|57|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||Oxybenzone|9.5|U|ng/L|9.5|29|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||PBDE-47|3.8|U|ng/L|3.8|11|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||PBDE-99|4.8|U|ng/L|4.8|14|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-73|2345649|MYAKKA CUTOFF|G3SD0073|02-AUG-2022|12:30|09-AUG-2022|17:53||Tri-o-cresyl Phosphate|5.7|U|ng/L|5.7|17|3510C (TQ)|Separatory funnel liquid-liquid extraction|05-AUG-2022|08:00|EPA 8270E|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:27||AMPA|0.31|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|06-AUG-2022|06:17||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:27||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:27||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:27||Glyphosate|0.71||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|06-AUG-2022|06:17||Sucralose|0.44||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|05-AUG-2022|09:10|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for sucralose could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50|39730|2,4-D|0.11||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Bentazon|0.013||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Carbamazepine|0.0011|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Clothianidin|0.027||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Dinotefuran|0.0046|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Diuron|0.056||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Fenuron|0.032|U|ug/L|0.032|0.064|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Fluridone|0.0019|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Imazapyr|0.025||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Imidacloprid|0.15||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||MCPP|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Thiamethoxam|0.082||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-74|2345650|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|14:50||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|04-AUG-2022|13:00|EPA 8321B|Monica Jaeger, Nicole Reistad|MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|916|Calcium|153||mg/L|0.22|0.90|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1045|Iron|260|I|ug/L|90|360|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|08:31|927|Magnesium|411||mg/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1082|Strontium|3.64E+03||ug/L|6.0|24|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1102|Tin|22|I|ug/L|9.0|36|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1152|Titanium|2.2|U|ug/L|2.2|9.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1087|Vanadium|6.0|U|ug/L|6.0|24|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|06-AUG-2022|03:22|1092|Zinc|15|U|ug/L|15|60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for calcium, magnesium and strontium are unavailable because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1105|Aluminum|41|I|ug/L|20|80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1097|Antimony|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1002|Arsenic|1.91||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1012|Beryllium|0.040|U|ug/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|04-AUG-2022|17:18|1027|Cadmium|0.080|U|ug/L|0.080|0.32|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1034|Chromium|1.6|U|ug/L|1.6|6.4|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|04-AUG-2022|17:18|1037|Cobalt|0.13|I|ug/L|0.080|0.32|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1042|Copper|2.4|I|ug/L|1.6|3.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1051|Lead|0.80|U|ug/L|0.80|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|04-AUG-2022|17:18|1055|Manganese|26.8||ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1062|Molybdenum|4.0||ug/L|0.60|2.4|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|04-AUG-2022|17:18|1067|Nickel|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1147|Selenium|0.80|U|ug/L|0.80|3.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|04-AUG-2022|17:18|1077|Silver|0.040|U|ug/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345651|Emerald Pointe Canal|G3SD0216|02-AUG-2022|08:35|05-AUG-2022|19:12|1059|Thallium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|04-AUG-2022|09:06|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|916|Calcium|37.3||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1045|Iron|560||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|927|Magnesium|41.7||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|937|Potassium|16.1||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1082|Strontium|1.40E+03||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1102|Tin|3.1|I|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1152|Titanium|1.6|I|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1087|Vanadium|2.0|I|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|05-AUG-2022|20:10|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1105|Aluminum|103||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1097|Antimony|0.17|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1002|Arsenic|1.43||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1012|Beryllium|0.018|I|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1034|Chromium|0.58|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1037|Cobalt|0.148||ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1042|Copper|1.02||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1055|Manganese|20.0||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1062|Molybdenum|1.58||ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1067|Nickel|0.74|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1147|Selenium|0.27|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345652|Peace River Estuary @ Harbour Heights|G3SD0148|02-AUG-2022|09:10|16-AUG-2022|16:08|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|46570|Hardness|41.0||mg/L|0.35|1.4|||||SM 2340 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|916|Calcium|10.5||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1045|Iron|1.49E+03||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|927|Magnesium|3.56||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|937|Potassium|0.30|U|mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|929|Sodium|7.9||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1082|Strontium|208||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1152|Titanium|1.2|I|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1087|Vanadium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|05-AUG-2022|20:25|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1105|Aluminum|148||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1097|Antimony|0.071|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1002|Arsenic|1.05||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1007|Barium|4.94||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1012|Beryllium|0.026|I|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1022|Boron|21.9||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1027|Cadmium|0.022|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1034|Chromium|0.77|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1037|Cobalt|0.251||ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1042|Copper|0.46|I|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1051|Lead|0.24|I|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1055|Manganese|17.6||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1062|Molybdenum|0.18|I|ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1067|Nickel|0.66|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345653|BOBCAT CREEK IN PRESERVE EAST|G3SD0131|02-AUG-2022|09:50|16-AUG-2022|16:17|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|46570|Hardness|124||mg/L|0.35|1.4|||||SM 2340 B-2011|Monica Jaeger, Nicole Reistad|
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|916|Calcium|28.4||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1045|Iron|650||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|927|Magnesium|12.8||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|937|Potassium|7.6||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|929|Sodium|15.4||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1082|Strontium|1.18E+03||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1152|Titanium|2.2|I|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1087|Vanadium|2.6|I|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|05-AUG-2022|20:31|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1105|Aluminum|184||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1097|Antimony|0.15|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1002|Arsenic|1.25||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1007|Barium|15.9||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1012|Beryllium|0.024|I|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1022|Boron|44.8||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1027|Cadmium|0.031|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1034|Chromium|0.78|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1037|Cobalt|0.239||ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1042|Copper|0.95||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1051|Lead|0.23|I|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1055|Manganese|31.2||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1062|Molybdenum|1.13||ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1067|Nickel|1.0|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1147|Selenium|0.25|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345654|Peace River Above Horse Creek 2|G3SD0154|02-AUG-2022|10:50|16-AUG-2022|16:26|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|916|Calcium|0.075|U|mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1045|Iron|30|U|ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|927|Magnesium|0.040|U|mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|937|Potassium|0.30|U|mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|929|Sodium|0.50|U|mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1082|Strontium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1152|Titanium|0.75|U|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1087|Vanadium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|05-AUG-2022|18:29|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.7 Rev. 4.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for potassium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1105|Aluminum|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1097|Antimony|0.050|U|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1002|Arsenic|0.050|U|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1007|Barium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1012|Beryllium|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1022|Boron|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1034|Chromium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1037|Cobalt|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1042|Copper|0.40|U|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1055|Manganese|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1062|Molybdenum|0.15|U|ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1067|Nickel|0.50|U|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2022-08-01-45|TLH-2022-08-03-75|2345655|FB|FB_08022022|02-AUG-2022|11:25|16-AUG-2022|13:44|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-AUG-2022|09:45|EPA 200.8 Rev. 5.4|Monica Jaeger, Nicole Reistad|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.