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-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|30-AUG-2019|09:20||Total Alkalinity|189||mg CaCO3/L|0.65|2.5|||||SM 2320 B-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|27-AUG-2019|16:17|76|Turbidity|4.4||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|29-AUG-2019|03:55|940|Chloride|54||mg Cl/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|27-AUG-2019|16:28|80|Color (true)|230||PCU|7.5|18|||||SM 2120 B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|30-AUG-2019|09:20|951|Fluoride|0.29||mg F/L|0.035|0.10|||||SM 4500 F-C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|29-AUG-2019|03:55|945|Sulfate|36||mg SO4/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|28-AUG-2019|14:52|70300|TDS|371||mg/L|15|25|||||SM 2540 C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114774|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|28-AUG-2019|14:52|530|TSS|6|I|mg/L|2.0|10|||||SM 2540 D-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|30-AUG-2019|09:34||Total Alkalinity|204||mg CaCO3/L|0.65|2.5|||||SM 2320 B-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|27-AUG-2019|16:17|76|Turbidity|6.1||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|29-AUG-2019|04:07|940|Chloride|38||mg Cl/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|27-AUG-2019|16:07|80|Color (true)|91||PCU|2.5|6.0|||||SM 2120 B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|30-AUG-2019|09:34|951|Fluoride|0.28||mg F/L|0.035|0.10|||||SM 4500 F-C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|29-AUG-2019|04:07|945|Sulfate|37||mg SO4/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|28-AUG-2019|14:52|70300|TDS|358|A|mg/L|15|25|||||SM 2540 C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114775|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|28-AUG-2019|14:52|530|TSS|24|A|mg/L|2.0|10|||||SM 2540 D-97|Gary Snorek|Sample contains high density particulates with sandy appearance that settle out quickly.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114776|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|05-SEP-2019|12:05|610|Ammonia-N|0.21||mg N/L|0.020|0.050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114776|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|29-AUG-2019|13:47|630|NO2NO3-N|0.28||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114776|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|30-AUG-2019|10:05|665|Total-P|0.26||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|29-AUG-2019|07:30|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114776|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|29-AUG-2019|13:11|625|Kjeldahl Nitrogen|2.1||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|28-AUG-2019|12:55|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114776|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|04-SEP-2019|17:42|680|Organic Carbon|28||mg C/L|0.50|1.0|||||SM 5310 B-00|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114777|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|05-SEP-2019|12:07|610|Ammonia-N|0.070|Y|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|The sample was received unpreserved: pH > 2.  Sample preserved in laboratory.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114777|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|29-AUG-2019|13:48|630|NO2NO3-N|0.38|Y|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|The sample was received unpreserved: pH > 2.  Sample preserved in laboratory.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114777|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|30-AUG-2019|11:00|665|Total-P|0.18|Y|mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|29-AUG-2019|07:30|EPA 365.1 Rev. 2.0|Gary Snorek|Total-P:  The sample was received unpreserved: pH > 2.  Sample preserved in laboratory.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114777|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|29-AUG-2019|13:13|625|Kjeldahl Nitrogen|1.4|Y|mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|28-AUG-2019|12:55|EPA 351.2 Rev. 2.0|Gary Snorek|The sample was received unpreserved: pH > 2.  Sample preserved in laboratory.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114777|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|04-SEP-2019|17:56|680|Organic Carbon|17|Y|mg C/L|0.50|1.0|||||SM 5310 B-00|Gary Snorek|The sample was received unpreserved: pH > 2.  Sample preserved in laboratory.
RQ-2019-08-19-20|TLH-2019-08-27-08|2114778|Lake Hicpochee Canal|G3SD0102|26-AUG-2019|10:50|27-AUG-2019|15:41|671|O-Phosphate-P|0.20||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114779|Nine Mile Canal @SR80|G3SD0088|26-AUG-2019|11:25|27-AUG-2019|15:48|671|O-Phosphate-P|0.052||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|13:01||Total Alkalinity|57||mg CaCO3/L|0.65|2.5|||||SM 2320 B-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|27-AUG-2019|16:17|76|Turbidity|3.1||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|29-AUG-2019|04:19|940|Chloride|26||mg Cl/L|0.20|0.60|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|27-AUG-2019|16:29|80|Color (true)|750||PCU|20|48|||||SM 2120 B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|13:01|951|Fluoride|0.11||mg F/L|0.035|0.10|||||SM 4500 F-C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|29-AUG-2019|04:19|945|Sulfate|7.4||mg SO4/L|0.20|0.60|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|28-AUG-2019|14:52|70300|TDS|203||mg/L|15|25|||||SM 2540 C-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114780|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|28-AUG-2019|14:52|530|TSS|4|I|mg/L|2.0|10|||||SM 2540 D-97|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114781|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|05-SEP-2019|12:08|610|Ammonia-N|0.34||mg N/L|0.020|0.050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114781|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|29-AUG-2019|13:50|630|NO2NO3-N|0.034||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114781|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|11:03|665|Total-P|0.36||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|29-AUG-2019|07:30|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114781|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|04-SEP-2019|15:45|625|Kjeldahl Nitrogen|2.7||mg N/L|0.40|1.0|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-SEP-2019|16:50|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114781|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|04-SEP-2019|18:10|680|Organic Carbon|49||mg C/L|0.50|1.0|||||SM 5310 B-00|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-08|2114782|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|27-AUG-2019|15:49|671|O-Phosphate-P|0.27||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|04-SEP-2019|21:02|99937|Sucralose|0.010|U|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|09:51||AMPA|0.32|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|29-AUG-2019|14:14||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|29-AUG-2019|14:14||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|09:51||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|09:51||Glyphosate|0.57||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|29-AUG-2019|09:45|EPA 8321B|Gary Snorek|
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38|39730|2,4-D|0.012||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Imazapyr|0.022||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Imidacloprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.
RQ-2019-08-19-20|TLH-2019-08-27-12|2114790|C-19 @ US 27|G3SD0087|26-AUG-2019|10:10|30-AUG-2019|20:38||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|27-AUG-2019|13:30|EPA 8321B|Gary Snorek|MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample. J - second source check standards for some analytes were not available for analysis.