REQUEST_ID|JOB_ID|SAMPLE_ID|SAMPLE_SITE|FIELD_ID|SAMPLE_DATE|SAMPLE_TIME|ANALYSIS_DATE|ANALYSIS_TIME|PARAM_CODE|PARAM_NAME|RESULT|VALUE_QUAL|UOM|MDL|PQL|PREP_METHOD|PREP_DESC|PREP_DATE|PREP_TIME|ANALYSIS_METHOD|SAMPLER|LAB_COMMENTS
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|02-AUG-2019|03:23||Total Alkalinity|180||mg CaCO3/L|0.65|2.5|||||SM 2320 B-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|26-JUL-2019|10:14|76|Turbidity|6.1||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|31-JUL-2019|02:38|940|Chloride|20||mg Cl/L|0.20|0.60|||||EPA 300.0 Rev. 2.1|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|26-JUL-2019|11:08|80|Color (true)|110|Q|PCU|2.5|6.0|||||SM 2120 B|Miranda Carroll|The sample expired upon receipt.
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|02-AUG-2019|03:23|951|Fluoride|0.098|I|mg F/L|0.035|0.10|||||SM 4500 F-C-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|31-JUL-2019|02:38|945|Sulfate|40||mg SO4/L|0.20|0.60|||||EPA 300.0 Rev. 2.1|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|30-JUL-2019|14:45|70300|TDS|344|A|mg/L|15|25|||||SM 2540 C-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106237|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|30-JUL-2019|14:45|530|TSS|5|IA|mg/L|2.0|10|||||SM 2540 D-97|Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|02-AUG-2019|03:37||Total Alkalinity|181||mg CaCO3/L|0.65|2.5|||||SM 2320 B-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|26-JUL-2019|10:16|76|Turbidity|2.7||NTU|0.10|0.13|||||EPA 180.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|31-JUL-2019|03:14|940|Chloride|44||mg Cl/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|26-JUL-2019|11:11|80|Color (true)|160|A|PCU|5.0|12|||||SM 2120 B|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|02-AUG-2019|03:37|951|Fluoride|0.20||mg F/L|0.035|0.10|||||SM 4500 F-C-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|31-JUL-2019|03:14|945|Sulfate|13||mg SO4/L|0.40|1.2|||||EPA 300.0 Rev. 2.1|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|30-JUL-2019|14:45|70300|TDS|325||mg/L|15|25|||||SM 2540 C-97|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106238|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|30-JUL-2019|14:45|530|TSS|3|I|mg/L|2.0|10|||||SM 2540 D-97|Miranda Carroll|Batch relative percent difference is unavailable because of low analyte concentration in the QC sample.
RQ-2019-07-22-19|TLH-2019-07-26-01|2106239|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|06-AUG-2019|19:06|610|Ammonia-N|0.073||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106239|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|30-JUL-2019|10:52|630|NO2NO3-N|0.36||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106239|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|01-AUG-2019|08:09|665|Total-P|0.066||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|30-JUL-2019|12:01|EPA 365.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106239|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|31-JUL-2019|09:57|625|Kjeldahl Nitrogen|1.2||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|30-JUL-2019|11:45|EPA 351.2 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106239|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|29-JUL-2019|18:06|680|Organic Carbon|17||mg C/L|0.50|1.0|||||SM 5310 B-00|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106240|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|06-AUG-2019|19:08|610|Ammonia-N|0.11||mg N/L|0.0020|0.0050|||||EPA 350.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106240|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|30-JUL-2019|10:53|630|NO2NO3-N|0.038||mg N/L|0.0040|0.010|||||EPA 353.2 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106240|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|01-AUG-2019|08:11|665|Total-P|0.17||mg P/L|0.0050|0.050|365.1 (MARCH 1983)|Automated, ascorbic acid|30-JUL-2019|12:01|EPA 365.1 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106240|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|31-JUL-2019|09:59|625|Kjeldahl Nitrogen|1.5||mg N/L|0.080|0.20|351.2 (MARCH 1983)|Preparation of samples for total kjeldahl nitrogen analysis|30-JUL-2019|11:45|EPA 351.2 Rev. 2.0|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106240|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|29-JUL-2019|18:22|680|Organic Carbon|24||mg C/L|0.50|1.0|||||SM 5310 B-00|Miranda Carroll|
RQ-2019-07-22-19|TLH-2019-07-26-01|2106241|Drainage Ditch@CR850|G1SD0061|24-JUL-2019|10:20|26-JUL-2019|11:20|671|O-Phosphate-P|0.041|Q|mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Miranda Carroll|O-Phosphate-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample. The sample expired upon receipt.
RQ-2019-07-22-19|TLH-2019-07-26-01|2106242|C-139Annex@DeerFenceRd|G1SD0076|24-JUL-2019|11:50|26-JUL-2019|11:18|671|O-Phosphate-P|0.12||mg P/L|0.0040|0.010|||||EPA 365.1 Rev. 2.0|Miranda Carroll|O-Phosphate-P:  Batch matrix spike recoveries are unavailable because of high analyte concentration in the QC sample.