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-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|07-APR-2023|10:48||AMPA|0.15|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|09-APR-2023|07:44||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|07-APR-2023|10:48||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|07-APR-2023|10:48||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|07-APR-2023|10:48||Glyphosate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|09-APR-2023|07:44||Sucralose|0.010|U|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08|39730|2,4-D|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Bentazon|0.0012|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Imazapyr|0.15||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Imidacloprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||MCPP|0.0028|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08|39760|Silvex|0.0064|I|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397529|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|08-APR-2023|00:08||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|07-APR-2023|11:01||AMPA|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|09-APR-2023|07:58||Acesulfame K|0.17|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|07-APR-2023|11:01||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|07-APR-2023|11:01||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|07-APR-2023|11:01||Glyphosate|0.12|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|09-APR-2023|07:58||Sucralose|0.60||ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27|39730|2,4-D|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Bentazon|0.0017|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Fluridone|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Imazapyr|0.051||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Imidacloprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397530|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|08-APR-2023|00:27||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|07-APR-2023|11:14||AMPA|1.0||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|09-APR-2023|08:12||Acesulfame K|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|07-APR-2023|11:14||Endothall|0.25|U|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|07-APR-2023|11:14||Glufosinate|0.10|U|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|07-APR-2023|11:14||Glyphosate|1.4||ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|09-APR-2023|08:12||Sucralose|0.019|I|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46|39740|2,4,5-T|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46|39730|2,4-D|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Afidopyropen|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|10-APR-2023|11:56||Bentazon|0.48||ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Benzovindiflupyr|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Carbamazepine|8.0E-04|U|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Clothianidin|0.012||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Dinotefuran|0.0024|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Diuron|0.0028|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Fenuron|0.032|U|ug/L|0.032|0.13|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Fluridone|0.025||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Ibuprofen|0.080|U|ug/L|0.080|0.32|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Imazapyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Imidacloprid|0.050||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Mandestrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46|39760|Silvex|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Thiamethoxam|0.0037|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-22|2397531|MYRTLE SLOUGH AT SR 31|G3SD0097|03-APR-2023|10:25|08-APR-2023|00:46||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|07-APR-2023|09:00|EPA 8321B|Nicole R, Gary S|MS accuracy and precision for bentazon could not be assessed due to high concentration of parameter in the spiked sample. MS accuracy for some analytes could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|46570|Hardness|311||mg/L|0.35|1.4|||||SM 2340 B-2011|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|916|Calcium|112||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1045|Iron|380||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|927|Magnesium|7.36||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|937|Potassium|1.0|I|mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|929|Sodium|40.3||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1082|Strontium|791||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1152|Titanium|0.75|U|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1087|Vanadium|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|10-APR-2023|19:55|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1105|Aluminum|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1097|Antimony|0.058|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1002|Arsenic|0.73||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1007|Barium|31.1||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1012|Beryllium|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1022|Boron|55.3||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1034|Chromium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1037|Cobalt|0.055|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1042|Copper|0.40|U|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1055|Manganese|16.1||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1062|Molybdenum|5.71||ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1067|Nickel|0.50|U|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397532|TELEGRAPH SWAMP SOUTH SITE|G3SD0100|03-APR-2023|09:10|06-APR-2023|18:12|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|46570|Hardness|221||mg/L|0.35|1.4|||||SM 2340 B-2011|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|916|Calcium|65.9||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1045|Iron|1.79E+03||ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|927|Magnesium|13.8||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|937|Potassium|4.8||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|929|Sodium|108||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1082|Strontium|4.80E+03||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1102|Tin|3.0|U|ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1152|Titanium|2.1|I|ug/L|0.75|3.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1087|Vanadium|4.1|I|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|10-APR-2023|20:11|1092|Zinc|10|I|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.7 Rev. 4.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1105|Aluminum|415||ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1097|Antimony|0.15|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1002|Arsenic|1.87||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1007|Barium|38.2||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1012|Beryllium|0.028|I|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1022|Boron|70.2||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1027|Cadmium|0.024|I|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1034|Chromium|0.95|I|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1037|Cobalt|0.192||ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1042|Copper|1.82||ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1051|Lead|1.64||ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1055|Manganese|90.1||ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1062|Molybdenum|1.13||ug/L|0.15|0.60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1067|Nickel|0.83|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1147|Selenium|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|
RQ-2023-03-06-45|TLH-2023-04-04-24|2397533|ALLIGATOR NORTH AT JONES LOOP RD|G2SD0032|03-APR-2023|11:15|06-APR-2023|18:21|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|05-APR-2023|11:40|EPA 200.8 Rev. 5.4|Nicole R, Gary S|