MTBE: Regulations and Drinking Water Monitoring Results
Last Update: November 29, 2006
Follow this link for information about the Drinking Water Treatment and Research Fund (DWTRF). The DWTRF addresses MTBE and other oxygenates in drinking water.
MTBE Drinking Water Standards
The gasoline additive methyl tertiary butyl ether (MTBE) is a regulated drinking water contaminant in California. MTBE has:
- a primary MCL of 13 micrograms per liter (µg/L), established in 2000, that addresses health concerns. Its 1999 public health goal is 13 µg/L, corresponding to the de minimis cancer risk derived from animal studies.
- a secondary MCL of 5 µg/L, established in 1999. The secondary MCL addresses taste and odor concerns.
- a detection limit for purposes of reporting (DLR) of 3 µg/L. The DLR is the level at which CDPH is confident about the quantity being reported. Results at or above the DLR are required to be reported to CDPH; some laboratories may report results at lower concentrations.
Monitoring Results
After detections of MTBE in some drinking water sources in the early and mid-1990s, CDHS (the California Department of Health Services, now CDPH) adopted a 1997 regulation that included MTBE as an unregulated chemical for which monitoring was required to be done by certain public water systems. Subsequently, required monitoring has been associated with compliance with MTBE's MCLs.
As of November 1, 2006, the CDHS database includes MTBE analytical results reported for 14,351 sources, where "sources" may include both raw and treated drinking water wells and surface water sources, distribution systems, blending reservoirs, and other sampled entities. Active, standby, inactive, and abandoned or destroyed sources are included.
Nearly all of the results are non-detects. However, 89 sources have reported MTBE detections greater than the DLR. The sources are in 32 counties, as shown in Table 1, which also shows 32 sources with a peak detection greater than MTBE's primary MCL, and 28 sources with a peal level greater than the secondary MCL but lower than the primary MCL.
The highest values reported were 610 µg/L in Los Angeles County in 1996; 500 µg/L in San Francisco in 1990; 400 µg/L in Monterey County in 2004; 234 µg/L in Yuba County in 1999; and 112 µg/L in San Diego County in 2004.
| Table 1. Peak concentrations of MTBE reported in sources of drinking water1 |
| County |
>13 µg/L |
5.5-13 µg/L |
3-5 µg/L |
Total No. Sources |
Peak Finding (µg/L) |
| Los Angeles |
6 |
8 |
3 |
17 |
610 |
| San Diego |
5 |
3 |
3 |
11 |
112 |
| Kern |
5 |
2 |
1 |
8 |
49.2 |
| Monterey |
3 |
1 |
. |
4 |
400 |
| San Francisco |
2 |
1 |
. |
3 |
500 |
| Riverside |
2 |
. |
. |
2 |
24 |
| Sacramento |
2 |
. |
. |
2 |
28 |
| San Mateo |
1 |
2 |
1 |
4 |
35 |
| Madera |
1 |
1 |
. |
2 |
33 |
| El Dorado |
1 |
. |
4 |
5 |
68 |
| Orange |
1 |
. |
2 |
3 |
40.9 |
| Yuba |
1 |
. |
1 |
2 |
234 |
| San Benito |
1 |
. |
. |
1 |
25 |
| Siskiyou |
1 |
. |
. |
1 |
17 |
| Lake |
. |
1 |
1 |
2 |
13 |
| San Luis Obispo |
. |
1 |
1 |
2 |
13 |
| Tulare |
. |
1 |
1 |
2 |
13 |
| Tuolumne |
. |
1 |
1 |
2 |
11 |
| Merced |
. |
1 |
1 |
2 |
6.4 |
| Alameda |
. |
1 |
1 |
2 |
5.5 |
| San Bernardino |
. |
1 |
. |
1 |
11 |
| Fresno |
. |
1 |
|
1 |
9.2 |
| Mono |
. |
1 |
. |
1 |
9 |
| Shasta |
. |
1 |
. |
1 |
6.9 |
| Calaveras |
. |
. |
1 |
1 |
5.3 |
| Mendocino |
. |
. |
1 |
1 |
4.9 |
| Lassen |
. |
. |
1 |
1 |
4.3 |
| Ventura |
. |
. |
1 |
1 |
4 |
| Santa Barbara |
. |
. |
1 |
1 |
3.6 |
| Solano |
. |
. |
1 |
1 |
3.5 |
| Butte |
. |
. |
1 |
1 |
3.2 |
| Sonoma |
. |
. |
1 |
1 |
3 |
| TOTAL |
32 |
28 |
29 |
89 |
-- |
|
1Numbers of sources should should be considered draft, since they may change with subsequent updates. Data are from sources with two or more reported MTBE detections at any concentration. |
Go to Drinking Water Treatment and Research Fund (DWTRF)
(The DWTRF addresses oxygenates such as MTBE in drinking water)