The proposed interim agreement for the Cornwall Landfill could have a harmful impact on humans and the environment.  As I previously noted, the Port, the Department of Ecology (DOE,) and the City of Bellingham have not advised the public of the most controversial and legally questionable aspects of the proposal.  This involves reducing the level of site cleanup through application of reduced standards.  The interim action may involve dumping and leaving dioxin, in excess of normal cleanup levels, on site.  Referred to as “containment,” and sometimes permissible under the Model Toxic Control Act (MTCA,) it is not appropriate for the Cornwall Landfill, as discussed below.

Cleanup Level

Method B is the cleanup level applicable under state law.  WAC 173-340-740(4) states that Method B is the only method available for establishing soil cleanup levels at a MTCA site, with the exception of qualifying industrial properties. Cornwall Landfill does not meet the characteristics of an industrial site under WAC 173-340-745(1)(a)(i.)  Therefore, cleanup levels must be determined based on Method B.

However, as noted in the interim agreement, the sediment dredged from Gate 3 can not meet this cleanup level.  The Port is requesting approval to use Method C.  This is not authorized under the MTCA and beneficial reuse of Gate 3 sediment is not a viable option.  It appears that DOE will nevertheless allow this because the interim action has been allowed to reach the public comment stage after months of internal discussion.

The large discrepancy in the dioxin cleanup levels under Method B and Method C, as reflected in the interim report, should be noted.  Under Method B, the TEQ measurement (a method of quantifying dioxin) is 11.  Under Method C, the TEQ is 1500.  In other words, Method C increases the human risk of developing cancer from exposure to dioxin a hundred fold.  I do not think the residents of Bellingham would willingly agree to accept this increased cancer risk.  Cancer rates are already quite high in Whatcom County.

The Port notes that Gate 3 sediment exceeds the Method B cleanup level by a small amount.  There is no such thing as exceeding soil cleanup levels for dioxin “by only a little.”  The Method B dioxin level is based on the reasonable maximum exposure scenario.  Any amount above this level exposes humans to unsafe levels of dioxin, a known carcinogen which is classified under state law as both a “priority contaminant of ecological concern” and a “persistent, bioaccumulative toxin.” WAC 173-340-7494 and WAC Chapter 173-333.  Either you meet human safety standards or you do not.  In this case, the interim action does not. 

On-Site Containment of Hazardous Soils

Nor is it appropriate, as indicated by the Port, for the interim action to include containment of soils with hazardous substances above cleanup levels.  This is not containment of a hazardous substance currently found at the Landfill. Rather, it is containment of a persistent, bioaccumulative toxin that is first being dumped at the Landfill as part of the interim action.  This appears to violate the purpose of the MTCA, which is to protect the public by reducing hazardous contamination at identified sites.

Under WAC 173-340-700(4)(c), containment is appropriate only when the compliance monitoring program is designed to ensure the long-term integrity of the containment system (and other requirements of the WAC are met.)  

The design plans for the interim agreement lacks long term integrity.  First, as reflected in the interim agreement, containment of soils with hazardous substances is not the primary purpose of the interim action.  It is, primarily, a stormwater proposal.  This fact was emphasized by the Port to justify the low height of the berms that will surround the project area.  Second, the waterproof sheet that will cover the Gate 3 sediment has a limited useful life of 4-5 years.  There is no approved and funded cleanup plan that ensures proper handling of the dioxin contaminated soil within 4-5 years of the interim action. 

Terrestrial ecological evaluation of the Cornwall Landfill should be required prior to considering the on-site containment of dioxin. Dioxin is a persistent, bioaccumulative toxin that enters the food chain, in part, through vegetation.  For this reason, the MTCA requires a terrestrial ecological evaluation establishing site-specific cleanup standards for the protection of terrestrial plants and animals, WAC 173-340-7490.  The Landfill will be developed as a park and shoreline trail, and will contain areas of grass and vegetated buffers.  The interim report discusses on-site containment, but does not discuss standards for terrestrial protection.

The redeveloped site will also include commercial and residential buildings. Residential land use is generally the site use requiring the most protective cleanup levels. Because of this future land use, and the toxicity and persistence of dioxin, it would be appropriate for the Port to provide alternative proposals to on-site containment, WAC 173-340-430(7)(b)(ii.)  However, they have failed to do so.

Background Levels of Dioxin

The argument that background levels of dioxin justify on-site containment of hazardous substances overlooks a crucial point.  Although we are measuring the dioxin level of Gate 3 sediment, this is sediment that is underwater, and therefore, the affected media is water. Once the sediment is placed on top of the Cornwall Landfill, it has been brought on land and the affected media is soil (with a new possibility of impacting both water and air.)  An interim action must be denied where it results in contamination of a new media.

A Sediment Site Characterization Evaluation of Bellingham Bay was conducted by DOE on June 26, 2007. See https://fortress.wa.gov/ecy/gsp/DocViewer.aspx?did=3287.  Surface sediment dioxin concentrations in Bellingham Bay have decreased by a factor of 10 compared to previously reported concentrations. The decrease is the result of high rates of sedimentation deposition from the Nooksack River.  If Gate 3 sediment is used to cap the Landfill, then, over time, this site’s dioxin contamination will exceed the background level because it will not longer benefit from additional sediment deposition.

Foreclosure of Reasonable Alternatives

Pursuant to WAC 173-340-430(3,) where there is no final cleanup action, an interim action may not foreclose reasonable alternatives. The placement of Gate 3 sediment over 3.6 acres of the Landfill, at the cost of 3 million dollars, is clearly not a temporary action.   Removing the cap after it is in place would increase the chance of environmental contamination and is not prudent.  Moreover, safely removing the temporary cap would also be expensive.  As a practical matter, once the sediment cap is placed on the Landfill, this will force the results of the final cleanup plan.