PUBLIC HEALTH ASSESSMENT
ORDNANCE PRODUCTS, INCORPORATED
NORTHEAST, CECIL COUNTY, MARYLAND
TABLES
METALS | Highest Concentration | Concentration Range | Comparison Value | # SamplesExceededCV's |
|---|---|---|---|---|
| Antimony | 29 | <12-29 | 20 RMEG | 1 |
| Cadmium | 35 | <1.1-35 | 40 EMEG | 0 |
| Chromium (VI) | 200 | 22-200 | 300 RMEG | 0 |
| Copper | 150 | 12-150 | NA | NA |
| Lead | 2070 | <6-2070 | NA | NA |
| Nickel | 330 | 7-330 | 1000 RMEG | 0 |
| Zinc | 15,000 | 20-15,000 | 20,000 RMEG | 0 |
| Arsenic | 6.1 | 1.8-6.1 | 0.4 CREG | 29 |
| Mercury (inorganic) | <0.5 | <0.5 | NA | 0 |
| Silver | <1.4 | <1.1-<1.4 | 300 RMEG | 0 |
| Selenium* | <6.7 | <0.55-<6.7 | 200 EMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentration | Concentration Range | Comparison Value | # Samples ExceededCV's |
|---|---|---|---|---|
| Antimony | <12 | <12-<15 | 20 RMEG | 0 |
| Cadmium | <1.5 | <1.2-<1.5 | 40 EMEG | 0 |
| Chromium(VI) | 55 | 12-55 | 300 RMEG | 0 |
| Copper | 29 | 15-29 | NA | NA |
| Lead | 310 | 13-310 | NA | NA |
| Nickel | 36 | 12-36 | 1000 RMEG | 0 |
| Zinc | 130 | 44-130 | 20,000 RMEG | 0 |
| Arsenic | 7.4 | 1.7-7.4 | 0.4 CREG | 18 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <1.5 | <1.2-<1.5 | 300 RMEG | 0 |
| Selenium* | 2.0 | <0.67-<6.6 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentrations | Concentration Range | Comparison Value (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | <14 | <13-<14 | 20 RMEG | 0 |
| Cadmium | <1.4 | <1.3-<1.4 | 40 EMEG | 0 |
| Chromium(VI) | 57 | 31-57 | 300 RMEG | 0 |
| Copper | 70 | 13-70 | NA | NA |
| Lead | 35 | 9-35 | NA | NA |
| Nickel | 23 | 8-23 | 1000 RMEG | 0 |
| Zinc | 150 | 18-150 | 20,000 RMEG | 0 |
| Arsenic | 5.7 | 2.7-5.7 | 0.4 CREG | 12 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <1.4 | <1.3-<1.4 | 300 RMEG | 0 |
| Selenium* | <6.6 | <0.61-<6.6 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
AREA C - Surface (21) and Subsurface (2) Soil Sampling (ppm)
METALS | Highest Concentrations | Range | Comparison Values (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | <14 | <11-<14 | 20 RMEG | 0 |
| Cadmium | <1.4 | <1.1-<1.4 | 40 EMEG | 0 |
| Chromium(VI) | 530 | 28-530 | 300 RMEG | 1 |
| Copper | 29 | 10-29 | NA | NA |
| Lead | 53 | <6-53 | NA | NA |
| Nickel | 670 | <6-670 | 1000 RMEG | 0 |
| Zinc | 850 | 11-850 | 20,000 RMEG | 0 |
| Arsenic | 5.0 | <0.64-5 | 0.4 CREG | 23 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <1.4 | <1.1-<1.4 | 300 RMEG | 0 |
| Selenium* | 4.1 | <0.54-4.1 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentrations | Concentration Range | Comparison Value (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | <17 | <11-<17 | 20 RMEG | 0 |
| Cadmium | <1.7 | <1.1-<1.7 | 40 EMEG | 0 |
| Chromium(VI) | 89 | 25-89 | 300 RMEG | 0 |
| Copper | 27 | 7-27 | NA | NA |
| Lead | 52 | 9-52 | NA | NA |
| Nickel | 41 | 8-41 | 1000 RMEG | 0 |
| Zinc | 330 | 32-330 | 20,000 RMEG | 0 |
| Arsenic | 9.3 | 1.2-9.3 | 0.4 CREG | 9 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <1.7 | <1.1-<1.7 | 300 RMEG | 0 |
| Selenium* | <7.0 | <0.69-<7.0 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentrations | Concentration Range | Comparison Value (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | <13 | <11-<13 | 20 RMEG | 0 |
| Cadmium | 15 | <1.1-15 | 40 EMEG | 0 |
| Chromium (VI) | 1900 | 20-1900 | 300 RMEG | 5 |
| Copper | 92 | 6-92 | NA | NA |
| Lead | 3300 | <5.5-3300 | NA | NA |
| Nickel | 3700 | 8-3700 | 1000 RMEG | 3 |
| Zinc | 2800 | 12-2800 | 20,000 RMEG | 0 |
| Arsenic | 3.6 | 0.99-3.6 | 0.4 CREG | 33 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | 5 | <1.1-5 | 300 RMEG | 0 |
| Selenium* | <6.5 | <0.55-<6.5 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentrations | Concentration Range | Comparison Values (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | 25 | <13-25 | 20 RMEG | 1 |
| Cadmium | 4.2 | <1.3-4.2 | 40 EMEG | 0 |
| Chromium (VI) | 94 | 27-94 | 300 RMEG | 0 |
| Copper | 38 | 13-38 | NA | NA |
| Lead | 76 | 7-76 | NA | NA |
| Nickel | 58 | 10-58 | 1000 RMEG | 0 |
| Zinc | 1500 | 31-1500 | 20,000 RMEG | 0 |
| Arsenic | 4.7 | 1.1-4.7 | 0.4 CREG | 20 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <2.0 | <1.3-<2.0 | 300 RMEG | 0 |
| Selenium* | <7.2 | <0.62-<7.2 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
METALS | Highest Concentrations | Concentration Range | Comparison Values (CV) | # Samples Exceeded CV's |
|---|---|---|---|---|
| Antimony | <14 | <11-<14 | 20 RMEG | 0 |
| Cadmium | <1.4 | <1.1-<1.4 | 40 EMEG | 0 |
| Chromium (VI) | 82 | 22-82 | 300 RMEG | 0 |
| Copper | 14 | 7-14 | NA | NA |
| Lead | 47 | 6-47 | NA | NA |
| Nickel | 17 | <6-17 | 1000 RMEG | 0 |
| Zinc | 400 | 7-400 | 20,000 RMEG | 0 |
| Arsenic | 5.5 | 1.6-5.5 | 0.4 CREG | 16 |
| Mercury | <0.5 | <0.5 | NA | 0 |
| Silver | <1.4 | <1.1-<1.4 | 300 RMEG | 0 |
| Selenium* | <6.9 | <0.56-<6.9 | 200 RMEG | 0 |
Source: O'Brien and Gere, June 1990.
*The detection limit for selenium was elevated due to matrix interferences.
CONTAMINANTS | Area E | Area F | Area H1 | Area H2 | Comparison Value |
|---|---|---|---|---|---|
| Vinyl Chloride | <16 | <13 | <20 | <13 | 1000 EMEG |
| t-1,2-Dichloroethene | <16 | <13 | 490 | <13 | 1,000,000 RMEG |
| Trichloroethene | <16 | <13 | 1600 | 13 | 60,000 CREG |
| Tetrachloroethylene | <16 | 15 | 77 | 560 | 10,000 CREG |
| Toluene | <16 | <13 | <20 | <13 | 10,000,000 RMEG |
| Xylenes | 18 | <13 | <20 | <13 | 100,000,000 RMEG |
Source: O'Brien and Gere, June 1990.
| CONTAMINANTS | Maximum Levels in Impoundments (11/89) | Maximum Levels in Impoundments (6/91) | Maximum Levels in Streams (11/89) | ComparisonValues |
|---|---|---|---|---|
| METALS (ppm) | ||||
| Antimony | 140 | <16 | <19 | 20 RMEG |
| Cadmium | 900 | 140 | <1.9 | 30 RMEG |
| Chromium (VI) | 39,000 | 1700 | 99 | 300 RMEG |
| Lead | 820 | 32 | 380 | NA |
| Nickel | 73 | 33 | 32 | 1000 RMEG |
| Zinc | 51,000 | 1900 | 140 | 20,000RMEG |
| Arsenic | <18.3 | 2 | 4.1 | 0.4 CREG |
| ORGANICS (ppb) | ||||
| Vinyl Chloride | <67 | <19 | 1000 EMEG | |
| t-1,2-Dichloroethene | 66 | <19 | 1x106RMEG | |
| Trichloroethene | 83 | <19 | 60,000CREG | |
| Tetrachloroethylene | <67 | <19 | 10,000CREG | |
| Toluene | 200 | 3 | 1x107RMEG |
Source: O'Brien and Gere, June 1994.
CONTAMINANTS | Stream Samples | Impoundment Samples | Surface Water Samples (Area D) | Drinking Water Comparison Value |
|---|---|---|---|---|
| Vinyl Chloride | <1 | <1 | <1 | 0.2 EMEG |
| t-1,2-Dichloroethene | 6 | 18 | 65 | 200 RMEG |
| Trichloroethene | 19 | 6 | 79 | 3 CREG |
| Tetrachloroethylene | 7 | <1 | 320 | 0.7 CREG |
| Toluene | 3 | 3 | <1 | 2000 RMEG |
| Xylenes | <1 | <1 | <1 | 20,000 RMEG |
Samples also analyzed for antimony, beryllium, cadmium, chromium, nickel, thallium, mercury,lead, selenium, silver, zinc, copper and arsenic - no samples exceeded ATSDR drinking watercomparison values.
Source: O'Brien and Gere, June 1994.
CONTAMINANTS | Maximum Concentration found in Monitoring Wells | MaximumConcentration found in Monitoring Wells | Maximum Concentration found in Supply Wells | Comparison Value |
|---|---|---|---|---|
| Date | 1989 | 1992 | 1989 | |
| Inorganics | ||||
| Arsenic | 7 | 0.02 CREG | ||
| Organics | ||||
| 1,2-Dichloroethene (total) | 260 | 820 | 100 | 70 MCL |
| Tetrachloroethylene | 1900 | 4300 | 38 | 0.7 CREG |
| Trichloroethene | 2800 | 980 | 97 | 3 CREG |
| Vinyl Chloride | 11 | 2 | 57 | 0.2 EMEG |
*Detection limits for sampling above comparison values
Source: O'Brien and Gere, June 1994.
CONTAMINANTS | RW 1 | RW 14 on-site | RW 45 | RW 46 | RW 47 | RW 48 | Comparison Value |
|---|---|---|---|---|---|---|---|
| 1,1-Dichloroethene | 2 | 0.06 CREG | |||||
| t-1,2-Dichloroethene | 200 | 2 | 200 RMEG | ||||
| Tetrachloroethylene | 68 | 0.7 CREG | |||||
| Trichloroethene | 2 | 160 | 1 | 10 | 46 | 3 CREG | |
| Vinyl Chloride | 90 | 0.2 EMEG |
Source: O'Brien and Gere, April 1993, Table 13.
| CONTAMINANTS | RW 1 | RW 45 | RW 46 | RW 47 | RW 48 | RW 53 | Comparison Value |
|---|---|---|---|---|---|---|---|
| Acetone | 59,500 | 1000 RMEG | |||||
| Benzene | 2 | 1 | -- | ||||
| Chloroform | 22 | 6 CREG | |||||
| t-1,2 Dichloroethene | 1 | 2 | 2 | 21 | 31 | -- | 200 RMEG |
| Ethyl Acetate | 35 | 9000 RMEG | |||||
| Ethyl Benzene | 32 | 1000 RMEG | |||||
| Methylene Chloride | 2 | 2 | 2 | 5 | 1800 | 5 CREG | |
| Methyl Ethyl Ketone | 16,600 | 6000 RMEG | |||||
| 2-Propanol | 12,234 | ||||||
| Tetrachloroethylene | 1 | -- | 0.7 CREG | ||||
| Toluene | 2 | 4 | 1 | 2 | 2 | 40 | 2000 RMEG |
| Trichloroethene | 3 | 29 | 57 | 120 | 145 | -- | 3 CREG |
| Xylenes (total) | 111 | 20,000 RMEG |
Source: O'Brien and Gere, April 1993, Table 14.
CONTAMINANTS | RW 1 | RW 45 | RW 46 | RW 47 | RW 48 | RW 53 | Comparison Value |
|---|---|---|---|---|---|---|---|
| Methylene chloride | 2 | 5 | 5 CREG | ||||
| Trichloroethene | 14 | 3 CREG |
Source: O'Brien and Gere, April 1993, Table 14b.
| CONTAMINANTS | Maximum Concentrations from Little Northeast Creek | Maximum Concentrations from Off-site Surface Water | Drinking Water Comparison Values | Ambient Water Quality Criteria |
|---|---|---|---|---|
| 1987 | 1993 | |||
| 1,2-Dichloroethene (total) | 2.0 | 4.0 | 70.0 MCL | NA |
| Tetrachloroethylene | <1.0 | 5.0 | 0.7 CREG | 8.0 |
| Trichloroethene | 5.0 | 17.0 | 3.0 CREG | 27.0 |
sampling locations for 1987 Sampling:
1. near 411 Stevenson Rd (5 ppb TCE)
2. drainage ditch near 22 Deans Lane (2 ppb TCE/2 ppb DCE)
sampling locations for 1993 Sampling: refer to map
Source: O'Brien and Gere, April 1993, Table 15.
| CONTAMINANTS | Maximum Concentration | Number of wells exceeding CV's | Comparison Value |
|---|---|---|---|
| Trichloroethene | 2800 | 3 (MW-2S, MW- 3S,MW-3D) | 3 CREG |
Source: O'Brien and Gere, June 1994, Table 11
| Pathway | Source | Environmental Media | Point of Exposure | Route of Exposure | Exposed Population | Time |
|---|---|---|---|---|---|---|
| Air | Ordnance Site | Air | Residences Ordnance Site | Inhalation | Nearby Residents and Employees at Ordnance | Past |
| Private Wells | Ordnance Site | Ground Water | Residences (tap) | Ingestion Inhalation Skin Contact | Residents along Mechanics Valley Road | Past Present Future |
| Surface Soil | Ordnance Site | Surface Soil | Ordnance Site | Ingestion | Employees of MVTC and trespassers | Past Present Future |
| Pathway | Source | Environmental Media | Point of Exposure | Route of Exposure | Exposed Population | Time |
|---|---|---|---|---|---|---|
| Sediment | Ordnance Site | Sediment | Impoundments, On-Site Streams, Little Northeast Creek | Ingestion | Children, Employees at MVTC and trespassers | Past Present Future |
| Ground Water | Ordnance Site | Ground Water | Residences, Businesses at MVTC | Ingestion | Residents, Employees at MVTC | Past Present Future |
| Surface Water | Ordnance Site | Impoundments and Streams | Impoundments and Streams | Ingestion | Children, Employees at MVTC and Trespassers | Past Present Future |
| Soil (off-site) | Ordnance Site | Runoff and overflow from the Impoundments | Residential Soil or Soil on or around Road | Inhalation/Ingestion | Residents | Past Present Future |
| Ordnance | Ordnance Site | Shallow Buried Ordnance | On-Site Areas Where Ordnance is Known to be Buried | Explosion | Employees at MVTC, Trespassers | Past Present Future |
| Fish | Ordnance Site | Little Northeast Creek | Residence | Ingestion | Little Northeast Creek Fisheaters | Past Present Future |
FIGURES

Figure 1. Site Location Map

Figure 2. Areas of Concern

Figure 3. Sediment and Surface Water Sample Location Map

Figure 4. Surface Water Samples

Figure 5. Groundwater Monitoring Well Location Map
1.
1Sentinel birth defects are immediately evident at birth. The World Health Organizationdevised the list of sentinel defects years ago. It was adopted by the 1981 Maryland law thatestablished Maryland's birth defect registry.

