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-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|28-FEB-2020|01:03||Total Alkalinity|20||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|20-FEB-2020|17:14|76|Turbidity|2.0||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|28-FEB-2020|02:41|940|Chloride|21||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|20-FEB-2020|17:28|80|Color (true)|20|A|PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|26-FEB-2020|18:02|951|Fluoride|0.049|I|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|28-FEB-2020|02:41|945|Sulfate|32||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|24-FEB-2020|15:24|70300|TDS|98||mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159547|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|24-FEB-2020|15:24|530|TSS|2|I|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|28-FEB-2020|01:12||Total Alkalinity|16||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|20-FEB-2020|17:14|76|Turbidity|0.70||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|28-FEB-2020|04:06|940|Chloride|19|A|mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|20-FEB-2020|17:28|80|Color (true)|3.4|I|PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|26-FEB-2020|18:13|951|Fluoride|0.078|I|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|28-FEB-2020|04:06|945|Sulfate|56|A|mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|Sulfate:  Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|24-FEB-2020|15:24|70300|TDS|183||mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159548|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|24-FEB-2020|15:24|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159549|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|26-FEB-2020|10:42|610|Ammonia-N|0.005|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159549|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|03-MAR-2020|11:00|630|NO2NO3-N|0.72||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159549|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|06-MAR-2020|12:56|665|Total-P|0.008||mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159549|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|09-MAR-2020|12:07|625|Kjeldahl Nitrogen|0.49||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159549|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|25-FEB-2020|02:04|680|Organic Carbon|7.1||mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159550|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|26-FEB-2020|10:57|610|Ammonia-N|0.004|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159550|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|03-MAR-2020|12:41|630|NO2NO3-N|12||mg N/L|0.080|0.20|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159550|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|06-MAR-2020|12:57|665|Total-P|0.003|I|mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159550|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|09-MAR-2020|12:22|625|Kjeldahl Nitrogen|0.38|IJ|mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|The PQL was elevated because of high nitrate concentration in the sample.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159550|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|25-FEB-2020|02:44|680|Organic Carbon|3.6||mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159551|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|20-FEB-2020|17:18|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159552|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|20-FEB-2020|17:19|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|28-FEB-2020|01:21||Total Alkalinity|27||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|20-FEB-2020|17:14|76|Turbidity|4.0|A|NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|28-FEB-2020|04:54|940|Chloride|20||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|20-FEB-2020|17:29|80|Color (true)|7.8||PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|26-FEB-2020|18:25|951|Fluoride|0.054|I|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|28-FEB-2020|04:54|945|Sulfate|24||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|Sulfate:  Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|24-FEB-2020|15:24|70300|TDS|99||mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159553|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|24-FEB-2020|15:24|530|TSS|6|I|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|28-FEB-2020|01:29||Total Alkalinity|20||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|20-FEB-2020|17:14|76|Turbidity|4.2||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|28-FEB-2020|05:06|940|Chloride|19||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|20-FEB-2020|17:30|80|Color (true)|7.7||PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|26-FEB-2020|18:35|951|Fluoride|0.062|I|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|28-FEB-2020|05:06|945|Sulfate|26||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|Sulfate:  Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|24-FEB-2020|15:24|70300|TDS|89||mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159554|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|24-FEB-2020|15:24|530|TSS|5|I|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|28-FEB-2020|01:38||Total Alkalinity|20||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|20-FEB-2020|17:14|76|Turbidity|11||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|28-FEB-2020|05:18|940|Chloride|15||mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|20-FEB-2020|17:31|80|Color (true)|8.5||PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|26-FEB-2020|18:46|951|Fluoride|0.052|I|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|28-FEB-2020|05:18|945|Sulfate|17||mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|Sulfate:  Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|24-FEB-2020|15:24|70300|TDS|69||mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159555|Lake Placid|G4SD0102|19-FEB-2020|13:15|24-FEB-2020|15:24|530|TSS|8|I|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159556|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|26-FEB-2020|10:59|610|Ammonia-N|0.003|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159556|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|03-MAR-2020|12:38|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159556|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|06-MAR-2020|13:05|665|Total-P|0.014||mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159556|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|09-MAR-2020|12:08|625|Kjeldahl Nitrogen|0.54||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159556|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|25-FEB-2020|02:56|680|Organic Carbon|6.4||mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159557|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|26-FEB-2020|11:00|610|Ammonia-N|0.003|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159557|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|03-MAR-2020|11:12|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159557|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|06-MAR-2020|13:25|665|Total-P|0.014||mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159557|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|09-MAR-2020|12:10|625|Kjeldahl Nitrogen|0.63||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159557|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|25-FEB-2020|03:12|680|Organic Carbon|6.4||mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159558|Lake Placid|G4SD0102|19-FEB-2020|13:15|26-FEB-2020|11:02|610|Ammonia-N|0.004|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159558|Lake Placid|G4SD0102|19-FEB-2020|13:15|03-MAR-2020|11:13|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159558|Lake Placid|G4SD0102|19-FEB-2020|13:15|06-MAR-2020|13:26|665|Total-P|0.021||mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159558|Lake Placid|G4SD0102|19-FEB-2020|13:15|09-MAR-2020|12:11|625|Kjeldahl Nitrogen|0.70||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159558|Lake Placid|G4SD0102|19-FEB-2020|13:15|25-FEB-2020|03:27|680|Organic Carbon|6.1||mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159559|Lake Francis @ Center|G4SD0187|19-FEB-2020|11:50|20-FEB-2020|17:20|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159560|Lake June @ Center|G4SD0186|19-FEB-2020|12:25|20-FEB-2020|17:20|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159561|Lake Placid|G4SD0102|19-FEB-2020|13:15|20-FEB-2020|17:21|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|28-FEB-2020|01:46||Total Alkalinity|0.65|U|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|20-FEB-2020|17:14|76|Turbidity|0.10|U|NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|28-FEB-2020|05:31|940|Chloride|0.20|U|mg Cl/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|20-FEB-2020|17:35|80|Color (true)|2.5|U|PCU|2.5|6.0|||||SM 2120 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|26-FEB-2020|19:01|951|Fluoride|0.035|U|mg F/L|0.035|0.10|||||SM 4500 F-C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|28-FEB-2020|05:31|945|Sulfate|0.20|U|mg SO4/L|0.20|0.50|||||EPA 300.0 Rev. 2.1|Gary Snorek|Sulfate:  Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|24-FEB-2020|15:24|70300|TDS|15|U|mg/L|15|25|||||SM 2540 C-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159562|Lake Placid|FB_02192020|19-FEB-2020|13:30|24-FEB-2020|15:24|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|Gary Snorek|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-02-17-52|TLH-2020-02-20-47|2159563|Lake Placid|FB_02192020|19-FEB-2020|13:30|26-FEB-2020|11:05|610|Ammonia-N|0.002|U|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159563|Lake Placid|FB_02192020|19-FEB-2020|13:30|05-MAR-2020|09:54|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159563|Lake Placid|FB_02192020|19-FEB-2020|13:30|06-MAR-2020|13:24|665|Total-P|0.002|U|mg P/L|0.0020|0.0050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-MAR-2020|16:52|EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159563|Lake Placid|FB_02192020|19-FEB-2020|13:30|09-MAR-2020|12:13|625|Kjeldahl Nitrogen|0.080|U|mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|06-MAR-2020|12:00|EPA 351.2 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159563|Lake Placid|FB_02192020|19-FEB-2020|13:30|25-FEB-2020|03:39|680|Organic Carbon|0.50|U|mg C/L|0.50|1.0|||||SM 5310 B-2011|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-47|2159564|Lake Placid|FB_02192020|19-FEB-2020|13:30|20-FEB-2020|17:31|671|O-Phosphate-P|0.004|U|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|27-FEB-2020|06:11|99937|Sucralose|0.66||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|21-FEB-2020|04:26||AMPA|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|24-FEB-2020|11:37||Acesulfame K|0.10|UJ|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|24-FEB-2020|11:37||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|21-FEB-2020|04:26||Glufosinate|0.10|UJ|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|21-FEB-2020|04:26||Glyphosate|0.10|UJ|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11|39730|2,4-D|0.0031|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Bentazon|0.0046||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Clothianidin|0.014||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Diuron|0.0038|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Fluridone|0.0044||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Imazapyr|0.010|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Imidacloprid|0.14||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Primidone|0.0060|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Thiamethoxam|0.030||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159570|Lake Apthorpe @ Center|G4SD0185|19-FEB-2020|10:20|07-MAR-2020|01:11||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|27-FEB-2020|06:23|99937|Sucralose|0.012|I|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|21-FEB-2020|04:37||AMPA|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|24-FEB-2020|11:51||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|24-FEB-2020|11:51||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|21-FEB-2020|04:37||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|21-FEB-2020|04:37||Glyphosate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|20-FEB-2020|14:30|EPA 8321B|Gary Snorek|
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46|39730|2,4-D|0.0061|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Bentazon|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Clothianidin|0.14||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Diuron|0.057||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Imazapyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Imidacloprid|0.42||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Thiamethoxam|0.21||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-02-17-52|TLH-2020-02-20-49|2159571|Buck Lake @ Middle|G4SD0158|19-FEB-2020|11:00|07-MAR-2020|01:46||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|24-FEB-2020|10:00|EPA 8321B|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. MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample.