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-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|05-MAR-2020|11:31||Total Alkalinity|111||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|25-FEB-2020|16:14|76|Turbidity|1.1||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|05-MAR-2020|17:31|940|Chloride|120||mg Cl/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|25-FEB-2020|16:17|80|Color (true)|50||PCU|2.5|6.0|||||SM 2120 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|14-MAR-2020|02:03|951|Fluoride|0.26||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|05-MAR-2020|17:31|945|Sulfate|140||mg SO4/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|26-FEB-2020|14:06|70300|TDS|521||mg/L|15|25|||||SM 2540 C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160462|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|26-FEB-2020|14:06|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|Nicole Reistad, Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-38|2160463|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|13:10|610|Ammonia-N|0.047||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160463|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|05-MAR-2020|10:11|630|NO2NO3-N|0.65||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160463|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|05-MAR-2020|12:23|665|Total-P|0.087||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|04-MAR-2020|13:06|EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160463|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|28-FEB-2020|10:02|625|Kjeldahl Nitrogen|1.0||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|27-FEB-2020|12:00|EPA 351.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160463|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|26-FEB-2020|22:40|680|Organic Carbon|13||mg C/L|0.50|1.0|||||SM 5310 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160464|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|25-FEB-2020|16:57|671|O-Phosphate-P|0.064||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|05-MAR-2020|10:44||Total Alkalinity|144||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|25-FEB-2020|16:14|76|Turbidity|0.80||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|05-MAR-2020|18:07|940|Chloride|190||mg Cl/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|25-FEB-2020|16:25|80|Color (true)|50|A|PCU|2.5|6.0|||||SM 2120 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|14-MAR-2020|02:08|951|Fluoride|0.40||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|05-MAR-2020|18:07|945|Sulfate|140||mg SO4/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|26-FEB-2020|14:06|70300|TDS|652||mg/L|15|25|||||SM 2540 C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160465|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|26-FEB-2020|14:06|530|TSS|2|I|mg/L|2.0|10|||||SM 2540 D-2011|Nicole Reistad, Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-38|2160466|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|13:12|610|Ammonia-N|0.025||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160466|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|05-MAR-2020|10:18|630|NO2NO3-N|0.48||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160466|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|05-MAR-2020|12:24|665|Total-P|0.14||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|04-MAR-2020|13:06|EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160466|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|28-FEB-2020|10:11|625|Kjeldahl Nitrogen|0.86||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|27-FEB-2020|12:00|EPA 351.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160466|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|26-FEB-2020|22:52|680|Organic Carbon|12||mg C/L|0.50|1.0|||||SM 5310 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160467|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|25-FEB-2020|16:58|671|O-Phosphate-P|0.12||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|11:43||Total Alkalinity|109||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|25-FEB-2020|16:14|76|Turbidity|1.5||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|18:19|940|Chloride|140||mg Cl/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|25-FEB-2020|16:18|80|Color (true)|56||PCU|2.5|6.0|||||SM 2120 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|14-MAR-2020|02:13|951|Fluoride|0.36||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|18:19|945|Sulfate|140||mg SO4/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|26-FEB-2020|14:06|70300|TDS|511||mg/L|15|25|||||SM 2540 C-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160468|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|26-FEB-2020|14:06|530|TSS|2|I|mg/L|2.0|10|||||SM 2540 D-2011|Nicole Reistad, Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-38|2160469|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|13:13|610|Ammonia-N|0.019||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160469|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|10:19|630|NO2NO3-N|0.33||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160469|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|12:25|665|Total-P|0.21||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|04-MAR-2020|13:06|EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160469|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|10:12|625|Kjeldahl Nitrogen|0.79||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|27-FEB-2020|12:00|EPA 351.2 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160469|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|26-FEB-2020|23:05|680|Organic Carbon|13||mg C/L|0.50|1.0|||||SM 5310 B-2011|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-38|2160470|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|25-FEB-2020|16:59|671|O-Phosphate-P|0.17||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|06-MAR-2020|12:00|99937|Sucralose|0.56||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|28-FEB-2020|14:31||AMPA|0.82||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|27-FEB-2020|19:26||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|27-FEB-2020|19:26||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|28-FEB-2020|14:31||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|28-FEB-2020|14:31||Glyphosate|1.1||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14|39730|2,4-D|0.0027|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Carbamazepine|0.0078||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Clothianidin|0.12||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Diuron|0.0038|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Imazapyr|0.024||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Imidacloprid|0.78||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||MCPP|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Primidone|0.0070|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Thiamethoxam|0.37||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160476|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|08-MAR-2020|08:14||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|06-MAR-2020|12:53|99937|Sucralose|0.52||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|28-FEB-2020|14:42||AMPA|1.2||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|27-FEB-2020|19:40||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|27-FEB-2020|19:40||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|28-FEB-2020|14:42||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|28-FEB-2020|14:42||Glyphosate|0.74||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48|39730|2,4-D|0.0090||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Bentazon|0.027||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Carbamazepine|0.0027|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Clothianidin|0.12||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Dinotefuran|0.0024|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Diuron|0.010||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Fenuron|0.14||ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Imazapyr|0.018||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Imidacloprid|0.61||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||MCPP|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Thiamethoxam|0.40||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160477|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|08-MAR-2020|08:48||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||3-Hydroxycarbofuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Aldicarb|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Aldicarb Sulfone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Aldicarb Sulfoxide|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28|39750|Carbaryl|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28|81405|Carbofuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Methiocarb|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28|39051|Methomyl|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Oxamyl|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160478|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|03:28||Propoxur|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|26-FEB-2020|08:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|12-MAR-2020|14:44|99937|Sucralose|0.10||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|11-MAR-2020|14:53|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|14:53||AMPA|1.1||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|27-FEB-2020|19:54||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|27-FEB-2020|19:54||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|14:53||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|14:53||Glyphosate|0.70||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|27-FEB-2020|11:30|EPA 8321B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23|39730|2,4-D|0.041||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Bentazon|0.012||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Carbamazepine|0.0016|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Clothianidin|0.12||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Diuron|0.0076|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Fenuron|0.065||ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Imazapyr|0.15||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Imidacloprid|0.42||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||MCPP|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Thiamethoxam|0.39||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-42|2160479|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|08-MAR-2020|09:23||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|28-FEB-2020|10:00|EPA 8321B|Nicole Reistad, Gary Snorek|J - second source check standards for some analytes were not available for analysis. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|09:03||Chlordane|17|I|ng/L|5.4|21|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8276|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|05-MAR-2020|09:03||Toxaphene|32|U|ng/L|32|130|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8276|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39330|Aldrin|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39337|Alpha-BHC|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Alpha-Chlordane|1.1|U|ng/L|1.1|4.3|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39338|Beta-BHC|11|U|ng/L|11|43|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Beta-Cyfluthrin|16|U|ng/L|16|64|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Bifenthrin|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|70314|Chlorothalonil|2.1|UJ|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Cis-Nonachlor|1.1|I|ng/L|1.1|4.3|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|3781|Cypermethrin|21|U|ng/L|21|86|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39310|DDD-p,p'|6.4|U|ng/L|6.4|26|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39320|DDE-p,p'|6.4|U|ng/L|6.4|26|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39300|DDT-p,p'|7.5|U|ng/L|7.5|30|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Dacthal|1.1|U|ng/L|1.1|2.1|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|34259|Delta-BHC|8.6|UJ|ng/L|8.6|34|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Dicofol|32|U|ng/L|32|130|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39380|Dieldrin|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|34361|Endosulfan I|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|34356|Endosulfan II|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|34351|Endosulfan Sulfate|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39390|Endrin|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|34366|Endrin Aldehyde|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Endrin Ketone|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Ethalfluralin|3.2|U|ng/L|3.2|13|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39340|Gamma-BHC|8.6|U|ng/L|8.6|34|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Gamma-Chlordane|1.1|U|ng/L|1.1|4.3|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39410|Heptachlor|1.6|U|ng/L|1.6|6.4|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39420|Heptachlor Epoxide|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Hexachlorobenzene|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Lambda-Cyhalothrin|16|U|ng/L|16|64|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39480|Methoxychlor|4.3|U|ng/L|4.3|17|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|39755|Mirex|2.1|U|ng/L|2.1|8.6|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|79191|Permethrin|11|U|ng/L|11|43|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Phenothrin|32|U|ng/L|32|130|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Prallethrin|32|U|ng/L|32|130|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13||Trans-Nonachlor|1.1|U|ng/L|1.1|4.3|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160480|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|20:13|81284|Trifluralin|2.7|U|ng/L|2.7|11|USGS-O-1126-95|Prep for organochlorine pesticides in water matrix by GC/MS-SIM|28-FEB-2020|08:30|EPA 8270E|Nicole Reistad, Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Acetochlor|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Alachlor|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|82184|Ametryn|0.58|U|ng/L|0.58|2.3|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39033|Atrazine|1.5||ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Atrazine Desethyl|1.5|U|ng/L|1.5|5.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Azinphos Methyl|4.8|U|ng/L|4.8|19|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|17:19||Bromacil|870||ng/L|12|48|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Butylate|0.39|UJ|ng/L|0.39|1.5|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Carbophenothion|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|38932|Chlorpyrifos Ethyl|5.8||ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|38740|Chlorpyrifos Methyl|0.048|U|ng/L|0.048|0.19|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Cyanazine|3.1|U|ng/L|3.1|13|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Demeton|6.8|U|ng/L|6.8|27|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Diazinon|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Dimethenamid|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|81888|Disulfoton|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Dithiopyr|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||EPTC|1.2|UJ|ng/L|1.2|4.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39398|Ethion|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|81758|Ethoprop|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fenamiphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fipronil|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fipronil Desulfinyl|0.12|U|ng/L|0.12|0.48|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fipronil Sulfide|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fipronil Sulfone|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Flumioxazin|1.7|U|ng/L|1.7|6.8|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Fonofos|0.19|U|ng/L|0.19|0.77|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|38815|Hexazinone|26||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Imazalil|0.73|U|ng/L|0.73|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39530|Malathion|0.34|U|ng/L|0.34|1.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Metalaxyl|61||ng/L|0.73|2.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Metolachlor|16||ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|81408|Metribuzin|3.1|U|ng/L|3.1|13|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39610|Mevinphos|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Molinate|0.29|U|ng/L|0.29|1.2|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|06-MAR-2020|17:19|78064|Norflurazon|1.0E+03||ng/L|12|48|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Oxadiazon|0.16|I|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Parathion Ethyl|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Parathion Methyl|0.53|U|ng/L|0.53|2.1|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Pendimethalin|0.97|U|ng/L|0.97|3.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|46313|Phorate|0.24|U|ng/L|0.24|0.97|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Prodiamine|0.17|U|ng/L|0.17|0.68|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39056|Prometon|0.87|U|ng/L|0.87|3.4|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39057|Prometryn|0.19|U|ng/L|0.19|0.77|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Pronamide|0.15|U|ng/L|0.15|0.58|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Propiconazole|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|39055|Simazine|0.48|U|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Sulfentrazone|5.2|J|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Tebuconazole|1.4|I|ng/L|0.48|1.9|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27|82088|Terbufos|0.097|U|ng/L|0.097|0.39|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-43|2160481|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|28-FEB-2020|16:27||Terbuthylazine|0.41|U|ng/L|0.41|1.6|3510C (TQ)|Separatory funnel liquid-liquid extraction|26-FEB-2020|09:00|EPA 8270E|Nicole Reistad, Gary Snorek|MS accuracy for some parameters not assessed due to high content of these parameters in the sample spiked.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|46570|Hardness|284||mg/L|0.35|1.4|||||SM 2340B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|1007|Barium|45.1||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|916|Calcium|80.9||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|1045|Iron|150||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|927|Magnesium|20.0||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|937|Potassium|13.0||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|929|Sodium|57.4||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|02-MAR-2020|19:08|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1105|Aluminum|32||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1097|Antimony|1.45||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1002|Arsenic|1.08||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1022|Boron|88.5||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1034|Chromium|0.59|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|04-MAR-2020|19:27|1042|Copper|1.26||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1067|Nickel|3.1||ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1147|Selenium|0.53|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160482|Hog Bay @ CR 763|G3SD0096|24-FEB-2020|12:20|03-MAR-2020|22:03|1059|Thallium|0.13|I|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|46570|Hardness|377||mg/L|0.35|1.4|||||SM 2340B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|1007|Barium|43.6||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|916|Calcium|106||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|1045|Iron|88|I|ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|927|Magnesium|27.3||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|937|Potassium|10.7||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|929|Sodium|82.7||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|02-MAR-2020|19:15|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1105|Aluminum|18|I|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1097|Antimony|0.67||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1002|Arsenic|1.26||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1022|Boron|68.4||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1027|Cadmium|0.045|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1034|Chromium|0.40|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|04-MAR-2020|19:37|1042|Copper|1.19||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1067|Nickel|2.2||ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1147|Selenium|0.33|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160483|HawthorneCreek@Reynolds|G3SD0011|24-FEB-2020|11:50|03-MAR-2020|22:12|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|46570|Hardness|316||mg/L|0.35|1.4|||||SM 2340B|Nicole Reistad, Gary Snorek|
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|1007|Barium|37.6||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|916|Calcium|83.7||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|1045|Iron|200||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|927|Magnesium|25.9||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|937|Potassium|11.4||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|929|Sodium|58.2||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|02-MAR-2020|19:23|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.7 Rev. 4.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for barium and sodium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1105|Aluminum|47||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1097|Antimony|0.48||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1002|Arsenic|0.95||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1022|Boron|64.4||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1027|Cadmium|0.052|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1034|Chromium|0.54|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|04-MAR-2020|19:46|1042|Copper|0.96||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1067|Nickel|1.6|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1147|Selenium|0.24|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-02-24-39|TLH-2020-02-25-45|2160484|Joshua Creek @ 17|G3SD0159|24-FEB-2020|13:25|03-MAR-2020|22:22|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|27-FEB-2020|15:45|EPA 200.8 Rev. 5.4|Nicole Reistad, Gary Snorek|Batch matrix spike recoveries for boron are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.