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Portage Bay Projects

Portage Bay is part of the tribal fishing grounds of Lummi Nation. The bay is restricted to shellfish harvest (60 acres in 1997 and 90 additional acres in 1999) due to declines in water quality seen over the beds. In order to get the beds re-opened to harvesting, we must document on-the-ground efforts that are occurring to improve water quality throughout the shellfish protection district. To help track our progress, different groups throughout the watershed conduct water quality monitoring. A database, housed at Whatcom County Water Resources, has been created to provide a central point for all of the information- freshwater and marine data, municipal sewer discharge data and even rainfall data. Graphs and data summaries are generated from this data.

Comprehensive Water Quality Monitoring

Water quality monitoring and data management are important tasks for the shellfish district. Monitoring water quality throughout the district provides guidance for determining priority areas for pollution control projects. Monitoring also provides information on what the current levels of pollution are, which helps determine where work still needs to be done and how close we are to achieving the desired levels for fecal coliform bacteria necessary to re-open the shellfish beds.

Data/Maps

As part of this process, numerous agencies have agreed to share their water quality data. The data is consolidated into one comprehensive database, which allows for easy access of all information relevant to the entire shellfish protection district.

Graphs and maps are developed based on these datasets to help visually display where samples are taken and what the current water quality status is at the various sample locations. Figures 1 and 2 provide a visual display of the shellfish protection district and the sample locations within the district where water quality data is currently collected and compiled.
Figure 1: Portage Bay Shellfish Protection District
Figure 2: Portage Bay Water Quality Sample Locations

Washington Department of Health

Prior to July of 2002, the State Department of Health (DOH) monitored Portage Bay for fecal coliform bacteria on a monthly basis. Water quality in the bay appears to be improving over the past few years and at the request of the Lummi Nation, DOH agreed that water quality was showing enough positive improvement to increase sampling in the bay from once per month to twice per month through the end of 2002 with the hope that the bay’s water quality might improve enough by the end of 2002 to allow for re-classification. However, due to high counts over the beds in August and again in September, the water quality was not good enough to allow for a re-classification by DOH.

There are nine sites within Portage Bay that DOH uses for classification purposes (Figure 3). The two-part National Shellfish Sanitation Program standard for approved shellfish harvest requires that the geometric mean for fecal coliform bacteria be <14 MPN/100mL (MPN= most probable number) and the estimated 90th percentile for fecal coliform bacteria be <43 MPN/100mL. DOH classifies shellfish growing areas based on a minimum of the last 30 water quality samples collected. At the end of 2002, all but one of the sites was meeting the two-part National Shellfish Sanitation Program standard (Figure 4).

Site #52 has the poorest water quality of the nine sites used for classification. Sites #53 and #58 show the best water quality. The graphs and tables below illustrate the water quality history of each of the various sites currently monitored over the shellfish beds in Portage Bay.

Station 48
Station 49
Station 50
Station 51
Station 52
Station 53
Station 54
Station 55
Station 57
Station 58

 

Northwest Indian College

The Northwest Indian College (NWIC) currently samples over 50 sites in the Nooksack watershed (Figure 5). Many of the creeks monitored do not meet the two-part fecal coliform bacteria standard for a freshwater Class A waterbody (geometric mean <200 and <10% of the samples >400) based on the last 30 samples collected. A lot of work has, however, gone on throughout the watershed over the past several years, and water quality is improving in many of the streams. The Nooksack River has a TMDL (total maximum daily load) for fecal coliform bacteria. A detailed implementation plan (DIP) has been developed and target fecal coliform levels set for various tributaries in the Nooksack drainage. Each quarter a report is generated to document various agencies’ progress toward meeting their goals for the DIP. The fourth quarter of 2002 was the first time that all eight monitored streams for the TMDL met their target fecal coliform goals. The figure below illustrates the target fecal coliform TMDL for each of the listed creeks and shows what the actual fecal coliform value was for that stream during that quarter.


On-site Septic Systems
Municipal Sewer Systems
Agricultural Practices
Stormwater Runoff
Education and Community Involvement
Data Management/Water Quality Monitoring
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