| Hydrogeology & Hydrology Program | |
| Piedmont Region Water Quality |
contact: David Bolton (dbolton@mgs.md.gov) |
[Project Objectives | Purpose | Tasks | Constituents | Quality Assurance | Reference | Location Map]
Reevaluation of Ground-Water Quality in the Piedmont Region of Baltimore County, Maryland
| Project Objectives: |
| Purpose: |
A study of ground-water quality in the Piedmont region of Baltimore County, Maryland was conducted between 1994 and 1996 in a cooperative project between the Baltimore County Department of Environmental Protection (DEPRM), the Maryland Geological Survey (MGS), and the U.S. Geological Survey (USGS) (Bolton, 1998). That study provided (1) an evaluation of ground-water quality with respect to Federal drinking-water standards, land use, well characteristics, aquifer lithology, and other factors, and (2) baseline data to which future water-quality data can be compared to assess changes in ground-water quality over time. This project will resample the wells and springs to determine what changes, if any, have occurred in ground-water quality, and to identify factors associated with observed changes.
| Tasks: |
Objective #1: Data collection:
Objective #2: Data evaluation:
| Water-Quality Constituents: |
Water-quality constituents to be analyzed are listed in table 1. The constituent list, which includes major ions, selected pesticides, volatile organic compounds (VOCs), and radionuclides, was developed after many discussions between DEPRM and MGS personnel. Gross alpha-particle and beta-particle activity, which was not analyzed in the initial study, will provide an inexpensive screening method for radium and other radionuclides. Both short-term (analyzed within three days of sample collection) and long-term (analyzed again after 30 days) measurements of gross alpha and beta will be made. Samples containing more than 15 picocuries per liter gross alpha-particle activity will be resampled and analyzed specifically for radium-226 and radium-228. Pesticides will be analyzed using the same analytical method as in the initial study; approximately 10 additional samples will also be analyzed by USEPA Method 507 for comparison. It is anticipated that bacteriological samples will be collected by DEPRM personnel and analyzed for total coliform bacteria and E. coli.
| Quality Assurance: |
Quality assurance (QA) procedures will be established to ensure data quality. Prior to sample collection, a QA project plan will be written that describes all aspects of the project, including a project description, sampling procedures, QA objectives, analytical procedures, QA samples, and corrective action to be taken. QA samples will be collected in order to (1) ensure there is no sample contamination from sampling equipment; (2) document the effectiveness of decontamination procedures; and (3) document precision of measurements. QA samples will consist of trip blanks, field blanks, and field duplicates. Data from the QA samples will be analyzed immediately in order to take any corrective actions that may be necessary. Other QA activities will include (1) comparison of field and laboratory values of pH, alkalinity, and specific conductance; (2) comparison of analytical values of total dissolved solids to residue-on-evaporation; and (3) evaluation of charge-balance errors and selected parameter ratios.
| Reference: |
Bolton, D. W., 1998, Ground-water quality in the Piedmont region of Baltimore County, Maryland: Maryland Geological Survey Report of Investigations No. 66, 191 p.
| CATIONS, ANIONS, AND INDICATORS: | |||
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VOLATILE ORGANIC COMPOUNDS:
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RADIONUCLIDES |
RADIONUCLIDES
(samples with gross alpha-particle activity greater than 15 picocuries per liter): |
BACTERIOLOGICAL CONSTITUENTS:
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| PESTICIDES (All samples): | PESTICIDES (EPA Method 507; selected samples): |
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*Long-term measurements will be made only in samples for which the short-term measurements were greater than the minimum reporting levels (3 picocuries per liter for gross alpha; 4 picocuries per liter for gross beta).
updated 10/6/04
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