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-2020-08-03-55|TLH-2020-08-06-78|2189024|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|07-AUG-2020|18:37||Total Alkalinity|56||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189024|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|06-AUG-2020|16:18|76|Turbidity|3.8||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189024|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|15-AUG-2020|21:46|71870|Bromide|0.94||mg Br/L|0.13|0.40|||||EPA 300.0 Rev. 2.1|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189024|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|07-AUG-2020|18:37|951|Fluoride|0.51||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|C.Conley / C.Hormuth|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189024|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|07-AUG-2020|18:09|530|TSS|2|IJ|mg/L|2.0|10|||||SM 2540 D-2011|C.Conley / C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample. The recovery of the QC standard was outside of the acceptable limit.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189025|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|12-AUG-2020|13:53|610|Ammonia-N|0.053||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189025|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|07-AUG-2020|10:42|630|NO2NO3-N|0.16||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189025|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|11-AUG-2020|13:10|665|Total-P|0.63||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|10-AUG-2020|11:00|EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189025|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|12-AUG-2020|14:18|625|Kjeldahl Nitrogen|1.2||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|11-AUG-2020|08:40|EPA 351.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189025|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|11-AUG-2020|02:16|680|Organic Carbon|25||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189026|Peace River Estuary @ Harbour Heights|G3SD0148|05-AUG-2020|09:50|06-AUG-2020|16:02|671|O-Phosphate-P|0.57||mg P/L|0.0080|0.020|||||EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|07-AUG-2020|18:25||Total Alkalinity|54||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|06-AUG-2020|16:18|76|Turbidity|4.5||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|08-AUG-2020|19:24|940|Chloride|19||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|06-AUG-2020|16:36|80|Color (true)|340||PCU|7.5|18|||||SM 2120 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|07-AUG-2020|18:25|951|Fluoride|0.51||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|C.Conley / C.Hormuth|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|08-AUG-2020|19:24|945|Sulfate|32||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|07-AUG-2020|17:33|70300|TDS|206|A|mg/L|15|25|||||SM 2540 C-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189027|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|07-AUG-2020|18:09|530|TSS|4|IAJ|mg/L|2.0|10|||||SM 2540 D-2011|C.Conley / C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample. The recovery of the QC standard was outside of the acceptable limit.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189028|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|12-AUG-2020|13:55|610|Ammonia-N|0.032||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189028|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|07-AUG-2020|10:21|630|NO2NO3-N|0.20||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189028|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|12-AUG-2020|14:37|665|Total-P|0.66||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|11-AUG-2020|11:28|EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|Total-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189028|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|12-AUG-2020|14:20|625|Kjeldahl Nitrogen|1.4||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|11-AUG-2020|08:40|EPA 351.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189028|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|11-AUG-2020|04:11|680|Organic Carbon|30||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189029|Peace River Above Horse Creek 2|G3SD0154|05-AUG-2020|10:45|06-AUG-2020|16:03|671|O-Phosphate-P|0.56||mg P/L|0.0080|0.020|||||EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|11-AUG-2020|00:06||Total Alkalinity|0.65|U|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|06-AUG-2020|16:18|76|Turbidity|0.10|U|NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|08-AUG-2020|19:36|940|Chloride|0.20|U|mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|06-AUG-2020|16:10|80|Color (true)|2.5|U|PCU|2.5|6.0|||||SM 2120 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|07-AUG-2020|20:57|951|Fluoride|0.035|U|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|08-AUG-2020|19:36|945|Sulfate|0.20|U|mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|12-AUG-2020|10:04|70300|TDS|15|U|mg/L|15|25|||||SM 2540 C-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189030|FB080520|FB080520|05-AUG-2020|11:00|07-AUG-2020|18:09|530|TSS|2|UJ|mg/L|2.0|10|||||SM 2540 D-2011|C.Conley / C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample. The recovery of the QC standard was outside of the acceptable limit.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189031|FB080520|FB080520|05-AUG-2020|11:00|12-AUG-2020|14:03|610|Ammonia-N|0.002|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Conley / C.Hormuth|The result was confirmed on 08/26/2020.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189031|FB080520|FB080520|05-AUG-2020|11:00|07-AUG-2020|10:22|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189031|FB080520|FB080520|05-AUG-2020|11:00|13-AUG-2020|08:16|665|Total-P|0.002|U|mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|11-AUG-2020|11:28|EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|Total-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-03-55|TLH-2020-08-06-78|2189031|FB080520|FB080520|05-AUG-2020|11:00|12-AUG-2020|14:21|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|11-AUG-2020|08:40|EPA 351.2 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189031|FB080520|FB080520|05-AUG-2020|11:00|11-AUG-2020|04:23|680|Organic Carbon|0.50|U|mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-78|2189032|FB080520|FB080520|05-AUG-2020|11:00|06-AUG-2020|16:04|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|11-AUG-2020|06:22|99937|Sucralose|1.9||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|06-AUG-2020|15:16||AMPA|4.1||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|07-AUG-2020|12:37||Acesulfame K|0.15|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|07-AUG-2020|12:37||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|06-AUG-2020|15:16||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|11-AUG-2020|12:06||Glyphosate|26||ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|06-AUG-2020|13:00|EPA 8321B|C.Conley / C.Hormuth|
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|22:32|39730|2,4-D|14||ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|22:32||Bentazon|0.27||ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Carbamazepine|0.0018|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Fluridone|0.015||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|22:32||Imazapyr|11||ug/L|0.16|0.64|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Imidacloprid|0.024||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Primidone|0.014|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.
RQ-2020-08-03-55|TLH-2020-08-06-82|2189039|Whiskey Creek @ College Blvd|G3SD0169|05-AUG-2020|08:40|12-AUG-2020|15:01||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|11-AUG-2020|09:00|EPA 8321B|C.Conley / C.Hormuth|The surrogate 2,4-D-d3 recovery could not be assessed due to an elevated level of 2,4-D in the sample matrix.