REQUEST_ID|JOB_ID|SAMPLE_ID|SAMPLE_SITE|FIELD_ID|SAMPLE_DATE|SAMPLE_TIME|ANALYSIS_DATE|ANALYSIS_TIME|PARAM_CODE|PARAM_NAME|RESULT|VALUE_QUAL|UOM|MDL|PQL|PREP_METHOD|PREP_DESC|PREP_DATE|PREP_TIME|ANALYSIS_METHOD|SAMPLER|LAB_COMMENTS
RQ-2020-08-24-36|TLH-2020-09-01-47|2193331|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|02-SEP-2020|17:55||Total Alkalinity|176||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193331|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|01-SEP-2020|14:24|76|Turbidity|1.5||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193331|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|10-SEP-2020|05:47|71870|Bromide|1.1||mg Br/L|0.13|0.40|||||EPA 300.0 Rev. 2.1|John Barrington/Miranda Carroll|Bromide: Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193331|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|02-SEP-2020|17:55|951|Fluoride|0.16||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193331|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|15:01|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|John Barrington/Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193332|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|15:28||Total Alkalinity|52|A|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193332|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|01-SEP-2020|14:24|76|Turbidity|5.6||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193332|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|10-SEP-2020|02:38|71870|Bromide|0.22||mg Br/L|0.013|0.040|||||EPA 300.0 Rev. 2.1|John Barrington/Miranda Carroll|Bromide: Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193332|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|15:18|951|Fluoride|0.21||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193332|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|03-SEP-2020|15:01|530|TSS|17||mg/L|2.0|10|||||SM 2540 D-2011|John Barrington/Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193333|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|06-SEP-2020|11:27|610|Ammonia-N|0.074||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193333|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|02-SEP-2020|09:24|630|NO2NO3-N|0.029||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193333|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|17-SEP-2020|10:45|665|Total-P|0.25||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-SEP-2020|13:46|EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193333|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|08-SEP-2020|11:03|625|Kjeldahl Nitrogen|1.4||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|04-SEP-2020|11:25|EPA 351.2 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193333|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|09-SEP-2020|21:35|680|Organic Carbon|28||mg C/L|0.50|1.0|||||SM 5310 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193334|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|06-SEP-2020|11:29|610|Ammonia-N|0.045||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193334|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|09:25|630|NO2NO3-N|0.054||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193334|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|17-SEP-2020|10:49|665|Total-P|0.29||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-SEP-2020|13:46|EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193334|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|04-SEP-2020|09:46|625|Kjeldahl Nitrogen|1.2||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-SEP-2020|09:45|EPA 351.2 Rev. 2.0|John Barrington/Miranda Carroll|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193334|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|09-SEP-2020|21:47|680|Organic Carbon|24||mg C/L|0.50|1.0|||||SM 5310 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193335|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|01-SEP-2020|16:12|671|O-Phosphate-P|0.21||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193336|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|01-SEP-2020|16:12|671|O-Phosphate-P|0.21||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193337|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|02-SEP-2020|18:08||Total Alkalinity|80||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193337|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|01-SEP-2020|14:24|76|Turbidity|4.8||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193337|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|10-SEP-2020|06:04|71870|Bromide|0.19||mg Br/L|0.013|0.040|||||EPA 300.0 Rev. 2.1|John Barrington/Miranda Carroll|Bromide: Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193337|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|02-SEP-2020|18:08|951|Fluoride|0.33||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193337|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|03-SEP-2020|15:01|530|TSS|4|I|mg/L|2.0|10|||||SM 2540 D-2011|John Barrington/Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193338|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|06-SEP-2020|11:30|610|Ammonia-N|0.046||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193338|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|02-SEP-2020|09:32|630|NO2NO3-N|0.10||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193338|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|17-SEP-2020|10:49|665|Total-P|0.38||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-SEP-2020|13:46|EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193338|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|04-SEP-2020|09:54|625|Kjeldahl Nitrogen|1.4||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-SEP-2020|09:45|EPA 351.2 Rev. 2.0|John Barrington/Miranda Carroll|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193338|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|09-SEP-2020|21:59|680|Organic Carbon|27||mg C/L|0.50|1.0|||||SM 5310 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193339|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|01-SEP-2020|15:38|671|O-Phosphate-P|0.29||mg P/L|0.0080|0.020|||||EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|O-Phosphate-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193340|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|02-SEP-2020|18:22||Total Alkalinity|123||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193340|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|01-SEP-2020|14:24|76|Turbidity|6.5||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193340|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|10-SEP-2020|17:23|71870|Bromide|0.26||mg Br/L|0.013|0.040|||||EPA 300.0 Rev. 2.1|John Barrington/Miranda Carroll|Bromide: Batch matrix spike recoveries for one of two spiked samples are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193340|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|02-SEP-2020|18:22|951|Fluoride|0.35||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193340|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|03-SEP-2020|15:01|530|TSS|12||mg/L|2.0|10|||||SM 2540 D-2011|John Barrington/Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193341|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|06-SEP-2020|11:32|610|Ammonia-N|0.10||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193341|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|02-SEP-2020|09:43|630|NO2NO3-N|0.093||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193341|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|17-SEP-2020|10:50|665|Total-P|0.39||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|02-SEP-2020|13:46|EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193341|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|04-SEP-2020|09:55|625|Kjeldahl Nitrogen|1.4||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|03-SEP-2020|09:45|EPA 351.2 Rev. 2.0|John Barrington/Miranda Carroll|Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-47|2193341|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|09-SEP-2020|18:03|680|Organic Carbon|23||mg C/L|0.50|1.0|||||SM 5310 B-2011|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-47|2193342|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|01-SEP-2020|15:47|671|O-Phosphate-P|0.22||mg P/L|0.0080|0.020|||||EPA 365.1 Rev. 2.0|John Barrington/Miranda Carroll|O-Phosphate-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|10-SEP-2020|12:27|99937|Sucralose|0.36|J|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|14:53||AMPA|1.5|I|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|MDL for some parameters elevated due to matrix interference.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|04-SEP-2020|15:54||Acesulfame K|1.0|UJ|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|MDL for some parameters elevated due to matrix interference.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|04-SEP-2020|15:54||Endothall|2.5|U|ug/L|2.5|10|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|MDL for some parameters elevated due to matrix interference.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|14:53||Glufosinate|1.0|UJ|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|MDL for some parameters elevated due to matrix interference.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|14:53||Glyphosate|1.4|IJ|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|MDL for some parameters elevated due to matrix interference.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48|39730|2,4-D|0.010||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Bentazon|0.0043||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Carbamazepine|0.0047||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Dinotefuran|0.0035|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Fluridone|0.0013|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|09-SEP-2020|10:54||Imazapyr|0.96||ug/L|0.040|0.16|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Imidacloprid|0.016||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193353|Cleveland Cemetary Ditch @ Riverside Rd|G3SD0076|31-AUG-2020|08:40|03-SEP-2020|02:48||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|10-SEP-2020|13:02|99937|Sucralose|0.066||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|03-SEP-2020|12:06||AMPA|0.81||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|04-SEP-2020|12:58||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|04-SEP-2020|12:58||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|03-SEP-2020|12:06||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|03-SEP-2020|12:06||Glyphosate|4.2||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|03-SEP-2020|10:00|EPA 8321B|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36|39730|2,4-D|0.012||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Bentazon|0.0078||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Dinotefuran|0.0076|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Diuron|0.0038|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Fluridone|0.0054||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Imazapyr|0.41||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Imidacloprid|0.015||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Thiamethoxam|0.0041|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-51|2193354|Myakka River (tidal) @ US 41|G3SD0068|31-AUG-2020|10:15|02-SEP-2020|21:36||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|02-SEP-2020|14:30|EPA 8321B|John Barrington/Miranda Carroll|MS accuracy for imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|04-SEP-2020|17:09|1045|Iron|1.24E+03||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|04-SEP-2020|17:09|927|Magnesium|16.1||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|04-SEP-2020|17:09|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1105|Aluminum|84||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1097|Antimony|0.080|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1002|Arsenic|1.98||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1034|Chromium|0.80|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|15-SEP-2020|18:10|1042|Copper|0.93||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|14-SEP-2020|15:10|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1067|Nickel|0.74|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1147|Selenium|0.23|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|19:08|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193355|Big Slough @ Butler Park|G3SD0168|31-AUG-2020|09:20|11-SEP-2020|00:16|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|04-SEP-2020|17:17|1045|Iron|1.51E+03||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|04-SEP-2020|17:17|927|Magnesium|15.7||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|04-SEP-2020|17:17|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.7 Rev. 4.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1105|Aluminum|124||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1097|Antimony|0.13|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1002|Arsenic|2.47||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1034|Chromium|0.90|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|15-SEP-2020|17:23|1042|Copper|0.93||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|14-SEP-2020|15:10|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1067|Nickel|0.79|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1147|Selenium|0.28|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|19:16|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|
RQ-2020-08-24-36|TLH-2020-09-01-52|2193356|Big Slough Canal|G3SD0161|31-AUG-2020|09:50|11-SEP-2020|00:24|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|02-SEP-2020|13:20|EPA 200.8 Rev. 5.4|John Barrington/Miranda Carroll|