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-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|06:41||Total Alkalinity|210||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|29-JAN-2020|16:18|76|Turbidity|1.5||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|22:18|940|Chloride|170||mg Cl/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|29-JAN-2020|18:45|80|Color (true)|38||PCU|2.5|6.0|||||SM 2120 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|06-FEB-2020|23:24|951|Fluoride|0.26||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|22:18|945|Sulfate|91||mg SO4/L|2.0|5.0|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|30-JAN-2020|14:40|70300|TDS|686||mg/L|30|50|||||SM 2540 C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152594|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|30-JAN-2020|14:40|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|07-FEB-2020|05:44||Total Alkalinity|144||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|29-JAN-2020|16:18|76|Turbidity|3.7||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|04-FEB-2020|22:54|940|Chloride|4.2E+03||mg Cl/L|8.0|20|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|29-JAN-2020|18:46|80|Color (true)|49||PCU|2.5|6.0|||||SM 2120 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|07-FEB-2020|03:30|951|Fluoride|0.58||mg F/L|0.070|0.20|||||SM 4500 F-C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|04-FEB-2020|22:54|945|Sulfate|680||mg SO4/L|8.0|20|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|14:40|70300|TDS|7.83E+03||mg/L|150|250|||||SM 2540 C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152595|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|14:40|530|TSS|12||mg/L|2.0|10|||||SM 2540 D-2011|C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-68|2152596|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|05-FEB-2020|12:42|610|Ammonia-N|0.004|I|mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152596|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|10:18|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152596|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|05-FEB-2020|12:12|665|Total-P|0.052||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|03-FEB-2020|15:03|EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152596|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|06-FEB-2020|12:03|625|Kjeldahl Nitrogen|0.71||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|05-FEB-2020|14:50|EPA 351.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152596|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|03-FEB-2020|08:11|680|Organic Carbon|12||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152597|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|04-FEB-2020|13:20|610|Ammonia-N|0.008||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152597|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|05-FEB-2020|08:18|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152597|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|05-FEB-2020|12:19|665|Total-P|0.12||mg P/L|0.010|0.10|365.1 (MARCH 1983)|Automated, ascorbic acid|03-FEB-2020|15:03|EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152597|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|05-FEB-2020|18:12|625|Kjeldahl Nitrogen|0.75||mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|04-FEB-2020|12:30|EPA 351.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152597|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|03-FEB-2020|08:26|680|Organic Carbon|13||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152598|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|29-JAN-2020|15:43|671|O-Phosphate-P|0.035||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152599|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|29-JAN-2020|14:52|671|O-Phosphate-P|0.056||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152600|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|04-FEB-2020|06:55||Total Alkalinity|174||mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152600|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|29-JAN-2020|16:18|76|Turbidity|1.0||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152600|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|12-FEB-2020|01:35|71870|Bromide|8.1||mg Br/L|0.26|0.80|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152600|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|06-FEB-2020|23:28|951|Fluoride|0.30||mg F/L|0.035|0.10|||||SM 4500 F-C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152600|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|30-JAN-2020|14:40|530|TSS|2|U|mg/L|2.0|10|||||SM 2540 D-2011|C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-68|2152601|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|07-FEB-2020|05:31||Total Alkalinity|103|A|mg CaCO3/L|0.65|2.5|||||SM 2320 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152601|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|29-JAN-2020|16:18|76|Turbidity|3.0||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152601|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|12-FEB-2020|01:52|71870|Bromide|13||mg Br/L|0.52|1.6|||||EPA 300.0 Rev. 2.1|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152601|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|07-FEB-2020|03:34|951|Fluoride|0.54||mg F/L|0.070|0.20|||||SM 4500 F-C-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152601|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|30-JAN-2020|14:40|530|TSS|10||mg/L|2.0|10|||||SM 2540 D-2011|C.Hormuth|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-68|2152602|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|04-FEB-2020|13:22|610|Ammonia-N|0.030||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152602|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|05-FEB-2020|08:22|630|NO2NO3-N|0.24||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152602|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|05-FEB-2020|12:25|665|Total-P|0.14||mg P/L|0.010|0.10|365.1 (MARCH 1983)|Automated, ascorbic acid|03-FEB-2020|15:03|EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152602|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|06-FEB-2020|12:12|625|Kjeldahl Nitrogen|0.76||mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|05-FEB-2020|14:50|EPA 351.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152602|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|08:44|680|Organic Carbon|16||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152603|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|04-FEB-2020|13:23|610|Ammonia-N|0.007||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152603|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|05-FEB-2020|08:23|630|NO2NO3-N|0.004|U|mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152603|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|05-FEB-2020|12:26|665|Total-P|0.15||mg P/L|0.010|0.10|365.1 (MARCH 1983)|Automated, ascorbic acid|03-FEB-2020|15:03|EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152603|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|06-FEB-2020|12:17|625|Kjeldahl Nitrogen|0.78||mg N/L|0.16|0.40|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|05-FEB-2020|14:50|EPA 351.2 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152603|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|09:00|680|Organic Carbon|13||mg C/L|0.50|1.0|||||SM 5310 B-2011|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152604|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|29-JAN-2020|15:54|671|O-Phosphate-P|0.11||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-68|2152605|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|29-JAN-2020|15:06|671|O-Phosphate-P|0.12||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|31-JAN-2020|17:44|99937|Sucralose|0.11|I|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL elevated due to matrix interference.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|23:10||AMPA|1.6|I|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|16:55||Acesulfame K|0.10|UJ|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|16:55||Endothall|0.25|UJ|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|23:10||Glufosinate|1.0|U|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|03-FEB-2020|23:10||Glyphosate|1.0|I|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41|39730|2,4-D|0.011||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Bentazon|0.0084||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Carbamazepine|0.0060||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Clothianidin|0.010||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Dinotefuran|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Fluridone|0.0016|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Imazapyr|0.34||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Imidacloprid|0.033||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Thiamethoxam|0.029||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152616|ClevelandCemeteryDitch|G3SD0076|28-JAN-2020|09:45|01-FEB-2020|21:41||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|31-JAN-2020|01:35|99937|Sucralose|0.11|J|ug/L|0.010|0.040|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|23:21||AMPA|1.0|U|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|17:08||Acesulfame K|0.10|UJ|ug/L|0.10|0.40|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|17:08||Endothall|0.25|UJ|ug/L|0.25|1.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|23:21||Glufosinate|1.0|U|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|03-FEB-2020|23:21||Glyphosate|1.0|U|ug/L|1.0|4.0|LC-FILTER|Filtration of samples prior to analysis|30-JAN-2020|12:00|EPA 8321B|C.Hormuth|MDL for some parameters elevated due to matrix interference. Results confirmed in sample duplicate.  Refer to the Lab Analysis Report for an explanation of QC Codes.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16|39730|2,4-D|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Acetaminophen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Acetamiprid|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Afidopyropen|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Bentazon|0.0057||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Benzovindiflupyr|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Carbamazepine|0.0012|I|ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Clothianidin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Dinotefuran|0.021||ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Diuron|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Fenuron|0.016|U|ug/L|0.016|0.064|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Fluridone|0.0098||ug/L|8.0E-04|0.0032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Hydrocodone|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Ibuprofen|0.020|U|ug/L|0.020|0.080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Imazapyr|0.027||ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Imidacloprid|0.0063|I|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Linuron|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||MCPP|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Mandestrobin|0.0020|UJ|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Naproxen|0.0080|U|ug/L|0.0080|0.032|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Primidone|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Pyraclostrobin|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Thiamethoxam|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Tolfenpyrad|0.0020|U|ug/L|0.0020|0.0080|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-72|2152617|Myakka(Tidal) @US41|G3SD0068|28-JAN-2020|11:15|01-FEB-2020|22:16||Triclopyr|0.0040|U|ug/L|0.0040|0.016|3535A|Prep for herbicides and carbamates|30-JAN-2020|10:00|EPA 8321B|C.Hormuth|J - second source check standards for some analytes were not available for analysis. MS accuracy for bentazon and imazapyr could not be assessed due to high concentration of parameter in the spiked sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|46570|Hardness|354||mg/L|0.35|1.4|||||SM 2340B|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|1007|Barium|42.0||ug/L|1.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|916|Calcium|116||mg/L|0.075|0.30|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|1045|Iron|67|I|ug/L|30|120|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|927|Magnesium|15.7||mg/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|937|Potassium|6.6||mg/L|0.30|1.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|929|Sodium|77.3||mg/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|04-FEB-2020|18:32|1092|Zinc|5.0|U|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.7 Rev. 4.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1105|Aluminum|13|I|ug/L|5.0|20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|11-FEB-2020|15:58|1097|Antimony|0.18|I|ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1002|Arsenic|0.86||ug/L|0.050|0.20|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|14-FEB-2020|16:27|1022|Boron|73.2||ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1027|Cadmium|0.020|U|ug/L|0.020|0.080|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1034|Chromium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1042|Copper|0.64|I|ug/L|0.40|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1051|Lead|0.20|U|ug/L|0.20|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|14-FEB-2020|16:27|1067|Nickel|1.1|I|ug/L|0.50|2.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1147|Selenium|0.31|I|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|14-FEB-2020|16:27|1077|Silver|0.010|U|ug/L|0.010|0.040|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152618|Shell Cr@HathawayPark|G3SD0120|28-JAN-2020|09:15|07-FEB-2020|20:49|1059|Thallium|0.10|U|ug/L|0.10|0.40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|03-FEB-2020|14:55|EPA 200.8 Rev. 5.4|C.Hormuth|
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|46570|Hardness|1.66E+03||mg/L|1.0|4.2|||||SM 2340B|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|1007|Barium|27||ug/L|3.0|12|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|916|Calcium|178||mg/L|0.22|0.90|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|1045|Iron|300|I|ug/L|90|360|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|927|Magnesium|296||mg/L|0.12|0.48|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|31-JAN-2020|11:20|937|Potassium|86||mg/L|6.0|24|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|31-JAN-2020|11:20|929|Sodium|2.40E+03||mg/L|10|40|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|30-JAN-2020|18:04|1092|Zinc|15|U|ug/L|15|60|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.7 Rev. 4.4|C.Hormuth|Batch matrix spike recoveries for calcium, magnesium, potassium and sodium are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|15-FEB-2020|03:43|1105|Aluminum|50|U|ug/L|50|200|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1097|Antimony|0.20|U|ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1002|Arsenic|1.30||ug/L|0.20|0.80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:11|1022|Boron|840||ug/L|20|80|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1027|Cadmium|0.080|U|ug/L|0.080|0.32|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:11|1034|Chromium|4.0|U|ug/L|4.0|16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|12-FEB-2020|18:07|1042|Copper|1.6|U|ug/L|1.6|3.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|12-FEB-2020|17:28|1051|Lead|2.0|U|ug/L|2.0|4.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1067|Nickel|2.0|U|ug/L|2.0|8.0|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1147|Selenium|0.80|U|ug/L|0.80|3.2|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1077|Silver|0.040|U|ug/L|0.040|0.16|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.
RQ-2020-01-27-49|TLH-2020-01-29-73|2152619|Big Slough@Biscayne|G3SD0161|28-JAN-2020|10:46|08-FEB-2020|09:50|1059|Thallium|0.40|U|ug/L|0.40|1.6|200.2|Sample prep procedure for spectrochemical determination of total recoverable elements|29-JAN-2020|14:30|EPA 200.8 Rev. 5.4|C.Hormuth|Batch matrix spike recoveries for boron are unavailable because of high analyte concentration in the QC sample.