The Texas Department of Health, under Cooperative Agreement with the Agency for Toxic Substances and Disease Registry
Table of Contents
FIGURES
Figure 1A. General Location and Demographics Information Chula Vista Landfill, Corpus Christi [not yet available]
Figure 1B. General Location and Demographics Information Villarreal Pit John Jones Subdivision, Corpus Christi [not yet available]
Figure 2. Location of Former Landfills and Other Features
Figure 3. Historical Soil Boring Locations at Garcia Elementary
Figure 4. Garcia Park 1998 Soil Borings and Soil Sample Locations
APPENDIX
TABLES
Table 1
Table 1. Cancers reported to the petitioners during their community survey around the Chula Vista and Greenwood Landfills
|
Benign tumor (breast, fibroid, ovary, type not specified) Bladder Bone Brain Breast Cancer, type not specified Cervical Colon Kidney Leukemia Liver Lung Lymphoma Ovary Pre-cancerous dysplasias Prostate Skin Stomach Testicular Throat Thyroid Uterus |
Table 2
| Table 2. Methane Testing in buildings near the Greenwood/Villarreal Pit |
| Building |
Date Sampled |
Areas Sampled for Methane |
Results of Methane Sampling |
Lulac Village Park Apartments 1417 Horne Road |
June 15, 2000 |
Apartments sampled: 1505B, 1513A, 1521B, and 1447A. Samples were taken in each bedroom closet, next to an outlet in each bedroom, under the bathroom sink, and in each cabinet adjacent to the kitchen sink. In apartment 1447A the bathtub had been removed exposing a hole in the slab; a sample was taken 3 feet below the slab. |
All samples non-detect (0% methane) |
Texas Department of Protective and Regulatory Services 4201 Greenwood Drive |
June 15, 2000 |
Rooms sampled: 23, 50, 55, 72, playroom, men's restroom west side, and supply and electrical room adjacent to Room 13. Rooms 23, 50, 55, 72 were sampled at the baseboard on the outside wall and at the wall jack. The men's room was sampled at a hole in the wall and in the floor drain. The supply and electrical room was sampled inside the circuit boxes. |
All samples non-detect (0% methane) |
J.A. Garcia Elementary School 4401 Greenwood Drive |
June 21, 2000 |
Portable Building #32, portable building #30, Rooms 7, 17, and 24, the copy room, the music room, the custodial room with the crawl space below the foundation, the bathroom, the mechanical room A/C closet, and the kitchen were all sampled. |
All samples non-detect (0% methane) |
Table 3
| Table 3. Methane Testing in buildings near the Chula Vista Landfill |
| Building |
Date Sampled |
Areas Sampled for Methane |
Results of Methane Sampling |
Chula Vista Academy of Fine Arts (Elementary) 1761 Hudson |
June 21, 2000 |
Portable buildings #22 and #25 were sampled. Rooms #2, 7, 9, 13, the music room, the custodial room, the bathroom, and the media room/library were sampled. |
All samples non-detect (0% methane) |
Cunningham Middle School 4321 Prescott |
June 27, 2000 |
The kitchen, the crawl space in the janitor's closet in the kitchen below the slab, the crawl space under Rooms 512, 513, 519, 522, outside the book room, outside the cafeteria and outside the band hall), the band hall, the computer room, restrooms #601 and #602, rooms # 109, 204, 311, 513, 521, the choir room and a custodial closet, including crawl space below the slab. |
All samples non-detect (0% methane) |
Mary Grett School 4402 Castenon |
June 27, 2000 |
Rooms 102, 104, 114, 116, and 120, the home management room, the mechanical room, the multi-purpose room, two storage areas, and a bathroom. Four- four foot deep holes dug for the setting of pillars for portable buildings also were sampled (no landfill waste was seen in the holes). |
All samples non-detect (0% methane) |
Table 4
Table 4. 1990 Investigation Surface Soil Samples Collected by Texas Department of Health Bureau of Solid Waste Inspector, September 20, 1990 |
| Sample Location |
Chula Vista Landfill |
Cunningham Middle School Courtyard |
Mary Grett School site |
John Jones Park (at Chula Vista) |
Screening Value (mg/kg*) |
| Lab sample # |
ESI 14 |
ESI 15 |
ESI 16 |
ESI 17 |
| Priority Pollutants Detected (mg/kg*) |
|
|
|
|
Background soil concentration for Western United States"†" |
| Metals |
Average |
Range |
| Arsenic |
2.8 |
1.6 |
0.6 |
1.8 |
5.5 |
<0.10 - 97 |
| Barium |
80 |
151 |
42 |
245 |
580 |
70 - 5,000 |
| Cadmium |
<0.5 |
<0.5 |
<0.5 |
<0.6 |
not applicable |
not applicable |
| Chromium |
9.3 |
14 |
12 |
18 |
41 |
3 - 2,000 |
| Copper |
5.2 |
9.2 |
4.9 |
12 |
21 |
2 - 300 |
| Iron |
10,600 (1.06%) |
13,700 (1.37%) |
11,300 (1.13%) |
16,800 (1.68%) |
21,000 (or 2.1%) |
0.1 - >10% |
| Lead |
15 |
29 |
16 |
46 |
17 |
<10 - 700 |
| Mercury |
0.022 |
0.030 |
<0.02 |
0.028 |
0.046 |
<0.01 - 4.6 |
| Nickel |
5.7 |
7.7 |
6.1 |
8.8 |
15 |
<5 - 700 |
| Selenium |
<0.9 |
<1.1 |
<1.0 |
<0.9 |
0.23 |
<0.1 - 4.3 |
| Silver |
<1.0 |
<0.9 |
<0.9 |
<0.9 |
not applicable |
not applicable |
| Zinc |
42 |
53 |
30 |
74 |
55 |
10 - 2,100 |
| Semivolatile Organic Compounds (all constituents below the detection limit except those listed) |
Health Assessment Comparison Values |
| Phenanthrene |
0.5 |
1.8 |
0.6 |
<3 |
none available |
| Fluoranthene |
1.6 |
3.5 |
0.8 |
<3 |
80/2,000/30,000 RMEG |
| Pyrene |
1.2 |
2.6 |
0.6 |
<3 |
60/2,000/20,000 RMEG |
| Benzo(a)anthracene |
0.6 |
1.2 |
BQL |
<3 |
none available B2 |
| Chrysene |
0.7 |
1.4 |
BQL |
<3 |
none available B2 |
| Bis(2-ethylhexyl)phthalate |
BQL |
BQL |
<0.05 |
<3 |
50 CREG B2; 40/1,000/10,000 RMEG |
| Benzo(b)fluoranthene |
0.6 |
1.1 |
BQL |
<3 |
none available B2 |
| Benzo(k)fluoranthene |
0.6 |
1.2 |
BQL |
<3 |
none available B2 |
| Indeno(1,2,3-cd)pyrene |
BQL |
0.5 |
<0.5 |
<3 |
none available B2 |
| Benzo(ghi)perylene |
BQL |
0.5 |
<0.5 |
<3 |
none available |
| Acenaphthene |
<0.5 |
BQL |
<0.5 |
<3 |
100/3,000/40,000 RMEG |
| Anthracene |
<0.5 |
BQL |
BQL |
<3 |
600/20,000/200,000 RMEG |
| Carbazole |
none detected |
0.3 |
none detected |
none detected |
none available |
| Benzo(j)fluoranthene |
none detected |
0.4 |
none detected |
none detected |
none available |
| Benzo(e)pyrene |
none detected |
0.6 |
none detected |
none detected |
none available |
| Octodecanal |
none detected |
0.4 |
none detected |
none detected |
none available |
| Hexyleicosone |
none detected |
0.9 |
none detected |
none detected |
none available |
| Benzo(a)pyrene |
none detected |
<0.5 |
BQL |
<3 |
0.1 CREG B2 |
| Pesticides |
none detected |
none detected |
none detected |
none detected |
not applicable |
* milligrams per kilogram (mg/kg) = parts per million
"†" U.S. Geological Survey 1984
BQL = reported at Below Quantitation Limits
RMEG = Reference dose based Media Evaluation Guide
CREG = Cancer Risk Evaluation Guide
Table 5
Table 5. Metals Concentrations (mg/kg) in Surface Soil Samples Hector A. Garcia Park 1998 (Figure 4) |
| Sample location |
HB-1 Field north of school and west of swimming pool |
HB-2 West of swimming pool entrance |
HB-3 Play area across from pool entrance |
HB-4 Field, top of hill, north of school |
HB-5 Greenwood Ball Park, next to yellow dugout |
HB-6 Greenwood Ball Park, next to blue dugout |
Background soil concentration for Western United States"†" |
| Average |
Range |
| Arsenic |
4.55 |
3.22 |
0.607 |
2.69 |
0.798 |
0.873 |
5.5 |
<0.10 - 97 |
| Barium |
261 |
227 |
79.9 |
125 |
46.9 |
23 |
580 |
70 - 5,000 |
| Beryllium |
0.914 |
1 |
0.667 |
0.178 |
0.344 |
0.179 |
0.68 |
<1 - 15 |
| Cadmium |
<1 |
<1 |
<1 |
<1 |
<1 |
<1 |
not applicable |
not applicable |
| Chromium |
14.9 |
20.2 |
7.89 |
12.7 |
9.18 |
9.66 |
41 |
3 - 2,000 |
| Cobalt |
7.84 |
7.45 |
3.94 |
4.86 |
<2.5 |
<2.5 |
7.1 |
<3 - 50 |
| Copper |
9.36 |
8.29 |
4.21 |
7.09 |
3.82 |
2.56 |
21 |
2 - 300 |
| Iron |
12,200 |
13,200 |
7,480 |
9,140 |
6,830 |
5,540 |
21,000 (2.1%) |
0.1 - >10% |
| Lead |
31 |
16.6 |
15.2 |
28.6 |
9.1 |
19.4 |
17"‡" (400"–"EPA action level) |
<10 - 700 |
| Magnesium |
5,400 |
5,740 |
2,340 |
4,940 |
2,230 |
1,240 |
7,400 (0.74 %) |
0.03 - >10% |
| Nickel |
12.1 |
10.8 |
6.85 |
8.15 |
4.38 |
<2.5 |
15 |
<5 - 700 |
| Silver |
<0.2 |
<0.2 |
<0.2 |
<0.2 |
<0.2 |
<0.2 |
not applicable |
not applicable |
| Vanadium |
17.3 |
17.8 |
4.98 |
10.2 |
12.4 |
8.73 |
70 |
7 - 500 |
| Zinc |
43.6 |
51.3 |
27.2 |
47 |
73.6 |
173 |
55 |
10 - 2,100 |
"†"U.S. Geological Survey 1984
"‡"chronic exposure to lead concentrations below 400 mg/kg are not likely to result in adverse health effects
Table 6
Table 6. TNRCC Soil Gas Sampling Results (ppbv¹) Exceeding ATSDR Health Assessment Comparison Values Chula Vista and Greenwood Landfills September 22, 2000 |
| Compound |
Chula Vista/Cunningham Landfill |
Greenwood Landfill/ Villareal Pit |
Open Field |
Health Assessment Comparison Values |
| CV922001 |
CV929001 |
CV929002 |
GW922001 |
GW922002 |
OF922001 |
| Benzene |
0.7 |
0.3 |
0.62 |
0.56 |
0.42 |
1.1 |
0.03 CREG*; 4 intEMEG** |
| 1,3-Butadiene |
ND |
ND |
0.43 |
0.67 |
0.76 |
1.6 |
0.001808 CREG"†" |
| Chloroform |
0.48 |
0.48 |
0.14J |
ND |
ND |
0.31 |
0.00819 CREG"†" 20 chrEMEG** |
¹ppbv = parts per billion volume
* CREG - Cancer Risk Evaluation Guide are based on EPA's chemical specific cancer slope factors and an estimated excess lifetime cancer risk of one-in-one million persons exposed for a lifetime.
** intEMEG and chrEMEGs - are intermediate and chronic Environmental Media Evaluation Guide based on ATSDR's minimal risk levels. Minimal Risk Levels are estimates of a daily exposure to a contaminant that is unlikely to cause adverse non-cancer health effects.
"†" The CREG value was converted from micrograms per cubic meter to parts per billion (ppbv) so that it could be readily compared to the site measurements.
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Last Updated September 13, 2004