Difference between revisions of "TMDL for Nutrients in Lower Salinas River Watershed, Monterey County, California"

Revision as of 16:24, 6 April 2011

This summary page is based on the Regional Water Quality Control Board Central Coast Region progress report on Total Maximum Daily Load for Nutrients and other TMDL projects for the Lower Salinas River Watershed, in Monterey County, California. This summary was prepared by the Spring 2011 ENVS 560/L Watershed Systems class at CSUMB.

Project Definition

The California Regional Water Quality Control Board for the Central Coast Region (CCRWQCB) is currently developing a Total Maximum Daily Load (TMDL) project for nutrients in the Lower Salinas River Watershed in Monterey County. The CCRWQCB presented a progress report in June 2010 that contains background information, provisional nutrient targets, and a compilation of water quality data of water bodies in the region. Although the progress report identifies potential sources of nutrient loads, the source analysis portion of the TMDL project is still pending.

This TMDL project will address the nutrient related impairments in the 303(d) listed water bodies of the Lower Salinas River watershed. The 2006 303(d) List of Impaired Waterbodies is the current and active list for the California Central Coast. In 2010 the CCRWQCB presented an updated list in its 2010 Integrated Report, but this report is still waiting for approval by the USEPA. The following table contains the water bodies and the nutrient-related reason for their listing in both the 2006 active list and in the 2010 list:

Problem Statement

Shaelyn

Data Analysis

Shaelyn

Numeric Target

Kathy

Linkage Analysis

Kathy

TMDL Development

Natalie

• target concentration

The TMDL target for nutrients for the lower Salinas valley is identified as a numeric target. The target concentrations vary based on what the location of the water bodies withing the Salinas Valley. These preliminary target concentrations are based on the 95th percentile of CCAMP reference sites. These reference sites might not be representative of "valley floor streams, sloughs and water conveyance structures"(progress report), which are more commonly found in the Salinas Valley.

The target allowable concentrations are established for phosphorus and nitrogen. The allowable numeric targets were calculated using the NNE (nutrient numeric endpoints) benthic biomass predictor tool. This tool predicts biological responses based on nutrient conditions present in the water body. The numeric targets for nutrient concentration are temperature dependent. The classifications for water temperature are either warm or cold. Parameters that are included in the predictor tool include nutrients (natural and anthropogenic), canopy closure, water temp, latitude, flow velocity and depth.

• goal
• allowable levels
  • The provisional target concentrations are -table on page 107
• example

Margin of Safety

Natalie

A margin of safety is used to account for the uncertainty in the linkage between nutrient loads and nutrient the nutrient pollutant concentrations in the receiving water body.

• SLO calculated nutrient TMDL margin of safety "based on the difference between the total maximum daily load and the allocated load"
• Uncertainties accounted for in the margin of safety include...
  • limited data(how many years do we have?)
  • these discrete values have been estimated based on a specific amount of parameters and categorized primarily based on temperature and does not necessarily account for compounding factors including dissolved oxygen availability, light availability etc
  • model may not be represnetative of the actual environmental conditions
• rain patterns vary from one year to the next so dilutions vary

Critical Conditions and Seasonal Variation

Roger

TMDL Allocations

Roger

Public Participation

• Central Coast Water Board often present TMDL project reports at public meetings to solicit comments during different stages and to present preliminary findings of the report.
• Public comments should be incorporated into the report where appropriate.
• California Environmental Quality Act (CEQA) issues will likely need to be addressed. Staff should prepare documents to demonstrate any potential impacts and present alternative schemes and implementation strategies.

Implementation and Monitoring

Michelle

Implementation

Monitoring

References

Links

• TMDLs in the Monterey Bay Region of California

• Central Coast Ambient Monitoring Program

• Central Coast Watershed Studies Team

• Beneficial uses

Disclaimer

This page may contain student work completed as part of assigned coursework. It may not be accurate. It does not necessary reflect the opinion or policy of CSUMB, its staff, or students.