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-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:44||Total Alkalinity|214||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|02:20|940|Chloride|14||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|07-APR-2020|19:13|951|Fluoride|0.27||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|02:20|945|Sulfate|7.7||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|07-APR-2020|14:10|70300|TDS|275||mg/L|15|25|||||SM 2540 C-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169435|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|07-APR-2020|14:10|530|TSS|50||mg/L|2.0|10|||||SM 2540 D-2011|Nicole Reistad/John Barrington|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|05:55||Total Alkalinity|115||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|02:33|940|Chloride|83||mg Cl/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|07-APR-2020|20:48|951|Fluoride|0.37||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|02:33|945|Sulfate|100||mg SO4/L|0.40|1.0|||||EPA 300.0 Rev. 2.1|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|07-APR-2020|14:10|70300|TDS|413||mg/L|15|25|||||SM 2540 C-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169436|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|07-APR-2020|14:10|530|TSS|21||mg/L|2.0|10|||||SM 2540 D-2011|Nicole Reistad/John Barrington|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-49|2169437|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|04-APR-2020|13:46|610|Ammonia-N|0.19||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169437|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|02-APR-2020|15:27|630|NO2NO3-N|0.14||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169437|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|06-APR-2020|09:33|665|Total-P|0.40||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|03-APR-2020|14:45|EPA 365.1 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169437|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|06-APR-2020|11:04|625|Kjeldahl Nitrogen|1.1||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-APR-2020|09:10|EPA 351.2 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169437|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|04-APR-2020|06:44|680|Organic Carbon|7.2||mg C/L|0.50|1.0|||||SM 5310 B-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169438|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|04-APR-2020|14:00|610|Ammonia-N|0.049||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169438|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|02-APR-2020|15:38|630|NO2NO3-N|0.032||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169438|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|06-APR-2020|09:34|665|Total-P|0.076||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|03-APR-2020|14:45|EPA 365.1 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169438|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|06-APR-2020|11:06|625|Kjeldahl Nitrogen|1.0||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-APR-2020|09:10|EPA 351.2 Rev. 2.0|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-49|2169438|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|04-APR-2020|06:58|680|Organic Carbon|15||mg C/L|0.50|1.0|||||SM 5310 B-2011|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|14-APR-2020|21:24|99937|Sucralose|0.65||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|06-APR-2020|17:38||AMPA|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|03-APR-2020|15:34||Acesulfame K|0.10|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|03-APR-2020|15:34||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|06-APR-2020|17:38||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|06-APR-2020|17:38||Glyphosate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-APR-2020|11:30|EPA 8321B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34|39730|2,4-D|0.0025|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Carbamazepine|0.0096||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Imazapyr|0.0044|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Imidacloprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-51|2169442|Pollywog Creek @ SR 78|G3SD0098|01-APR-2020|10:20|08-APR-2020|16:34||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|06-APR-2020|09:00|EPA 8321B|Nicole Reistad/John Barrington|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|46570|Hardness|233||mg/L|0.35|1.4|||||SM 2340B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|1007|Barium|20.1||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|916|Calcium|72.2||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|1045|Iron|6.40E+03||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|927|Magnesium|12.9||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|937|Potassium|4.1||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|929|Sodium|18.8||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|13-APR-2020|16:28|1092|Zinc|7.9|I|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1105|Aluminum|1.79E+03||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|21:55|1097|Antimony|0.15|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1002|Arsenic|1.77||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1022|Boron|47.4||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1034|Chromium|5.3||ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1042|Copper|2.32||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1051|Lead|1.22||ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1067|Nickel|0.93|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169443|Drainage Ditch @ CR850|G1SD0061|01-APR-2020|09:30|10-APR-2020|05:53|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|46570|Hardness|260||mg/L|0.35|1.4|||||SM 2340B|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|1007|Barium|58.2||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|916|Calcium|68.1||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|1045|Iron|750||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|927|Magnesium|21.7||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|937|Potassium|8.4||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|929|Sodium|43.6||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|13-APR-2020|16:34|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.7 Rev. 4.4|Nicole Reistad/John Barrington|Batch matrix spike recoveries for calcium are unavailable for one of two spiked samples because of high analyte concentration in the QC sample.
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1105|Aluminum|112||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|22:02|1097|Antimony|0.19|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1002|Arsenic|1.29||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1022|Boron|67.6||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1034|Chromium|0.47|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1042|Copper|0.58|I|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1067|Nickel|1.1|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1147|Selenium|0.25|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|
RQ-2020-03-30-50|TLH-2020-04-02-52|2169444|Cow Slough @FarabeeRoad|G3SD0160|01-APR-2020|11:35|10-APR-2020|06:02|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|08-APR-2020|16:30|EPA 200.8 Rev. 5.4|Nicole Reistad/John Barrington|