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1 - paducah environmental information center

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Paducah Site<br />

Field Sampling Quality Control<br />

Data Quality Objectives and Sample<br />

Planning<br />

From the point of conception of any<br />

sampling program, DQOs play· an important<br />

role. The number of samples, location of<br />

sampling sites, sampling methods, sampling<br />

schedules, and coordination of sampling and<br />

analytical resources to meet critical completion<br />

times were part of the. DQOs and are documented<br />

in the Environmental Monitoring Plan (BJC<br />

1998).<br />

Each sample location and sample collected<br />

was assigned a unique identification number<br />

which consists of an alphanumeric sequence.<br />

Each segment . of the sequence was used to<br />

designate <strong>information</strong> concerning the location<br />

from which a sample was collected. In order to<br />

progress from planning to ,implementing the<br />

DQOs, an. analytical statement of work (SOW)<br />

for the analytical laboratory was generated from<br />

a system'within, the Paducah Integrated Data<br />

System. ,From . this system, the Project<br />

Environmtmtal Measurements System (PEMS),<br />

an electronic 'database used for streamlining<br />

fidd-generated and laboratory-generated data,<br />

was populated with sample identification<br />

numbers, sampling locations, sampling methods,<br />

analytical parameters, analytical methods, and<br />

container and preservative requirements. This<br />

<strong>information</strong> was used to produce sample bottle!<br />

jar labels and chain-of-custody forms for the<br />

sampling event.<br />

,Field Measurements<br />

Field measurements for the groundwater<br />

and surface water monitoring program were<br />

collectedreal.:.time in, the field and consisted of<br />

water ievet measurements, pH, conductivity,<br />

flow rates, . turbidity, temperature, dissolved<br />

oxygen, total residual chlorine, and barometric<br />

pressure. Environmental conditions· such as<br />

temperature and weather were also recorded.<br />

Field measurements were taken and downloaded<br />

electronically or recorded on appropriate field<br />

forms or in logbooks, and input into PEMS on a<br />

weekly or other appropriate basis.<br />

Sampling Procedures<br />

Samples were collected using mediaspecific<br />

procedures which are written according<br />

to EPA-approved sampling methods. Sample<br />

media consisted of surface water, groundwater,<br />

sediment, and biota, such as fish or deer. Sample<br />

<strong>information</strong> collected during the sample event<br />

consisted of the following: sample identification<br />

number, station (or location), data collected,<br />

time collected, person who performed the<br />

sampling, etc. This <strong>information</strong>. was recorded in<br />

the logbooks and on the chain-of-custody form<br />

and sample container label, arid input directly<br />

into PEMS on a weekly or other appropriate<br />

basis. Chain-of-custody forms, were maintained<br />

from the point of sampling, and samples were<br />

properly protected until they were placed in the<br />

custody of an analytical laboratory.<br />

Field Quality Control Samples<br />

The QC program for both groundwater and<br />

<strong>environmental</strong> monitoring activities specified a<br />

minimum target rate of 5%, or one per 20<br />

<strong>environmental</strong> samples, on field QC samples.<br />

Table 11.1 shows the types of QC samples<br />

collected and analyzed. Analytical results of<br />

field QC samples were evaluated to determine if<br />

the sampling event had, in some way, affected<br />

the sample results.<br />

Analytical Laboratory Quality<br />

Control<br />

Analytical Procedures<br />

When available and appropriate for the<br />

sample matrix, SW -846 methods were used for<br />

sample analysis. When SW -846 methods were<br />

11-2<br />

Quality Assurance

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