Total Maximum Daily Load (TMDL)
Total maximum daily load is part of the Clean Water Act and refers both to the legislation and regulatory documents which require assessment and listing of "impaired" waterbodies (section 303 d), and calculations for numeric standards to meet water quality standards required.
Total maximum daily loads set upper limits on how much of a pollutant can enter a waterbody within a day (Waste Load Allocation--WLA) as well as how much each polluter may add to that waterbody (Load Allocations--LAs).
Total maximum daily loads (TMDLs) are a regulatory tool created by the US EPA to meet water quality goals for impaired water bodies under Section 303(d)(1)(A) of the Clean Water Act (CWA). Water quality goals include "beneficial uses" (BUs) which include water contact recreation, wildlife habitat, and others.
Total maximum daily loads also refer to the specific Load and Waste Load Allocations (LAs and WLAs respectively) for each pollutant load, plus a margin of safety. These load allocations are the calculated amount of a given pollutant that a given waterbody can receive while still preserving and improving water quality .
Under the 1972 Federal Clean Water Act, all waterbodies within the US must be evaluated for water quality by States, territories and authorized tribes. Those waterbodies not meeting water quality standards must be classified as "impaired". The impairment list is known as the 303d list, which requires that total maximum daily loads (TMDLs) be established for any pollutants identified to be causing these impairments. An updated list of impaired waterbodies (303d list)must be submitted every two years.
Again, along with listing impaired waterbodies, states and other authorized bodies must identify stressors causing the impairment (i.e. pollutants) on the 303d list as well. Responsible parties must then develop and implement a remediation plan for each 303d-listed water body. These TMDLs must be created with the goal of defining and achieving a total maximum daily load for each pollutant which will help achieve water quality goals within each 303d-listed waterbody.
The list also identifies where TMDLs have been approved by the Environmental Protection Agency (EPA) and implemented but where water quality standards have not yet been met, and further action beyond TMDLs are needed address impairment.
General overview of TMDL development process
TMDL development involves many stages from problem identification and problem statement development, through development of numeric standards to restore water quality goals, source assessments and linkage analysis, to load allocations, monitoring/evaluation, and finally implementation.
Beneficial uses are those uses which XXXXX
TMDLs establish the concentration or daily load of nutrients a body of water can contain while continuing to support its defined beneficial uses. TMDLs can be defined in terms of a mass load or can be set as a unit of concentration. During TMDL development, it is necessary to consider secondary indicators of water quality, such as dissolved oxygen levels, transparency and algal biomass, that are linked to the beneficial uses for the water body. A modeling tool can be used to link secondary indicators to concentrations in the water column and predict levels of nutrients that would impair specific beneficial uses.
Numeric targets are concentrations of specified nutrients that would not impair designated beneficial uses of a given water body. Water quality objectives given in the Basin Plan . Water quality objectives for the Basin Plan are attempts to quantify the allowable nutrient concentrations, objectives listed in the Plan are used as a starting point during TMDL development and adoption.
The protocol document suggests that monitoring plans describe the timing, location, responsible parties, and quality assurance and control procedures.
The level of rigor required for a monitoring plan is dependent on confidence in the TMDL analysis. A greater level of uncertainty requires more rigorous monitoring actions and must allow room for future revision. Since watershed process drivers are not identical before and after implementation, models are useful for evaluating results of monitoring. Models can be calibrated to pre or post-implementation to better compare results of monitoring actions. Coordination with other existing or planned monitoring activities can be particularly helpful for long-term monitoring programs, large study areas, or if the water quality agency’s monitoring resources are limited. It is also important to choose the type of monitoring that will be most appropriate to yield desired goals and then develop a quality assurance plan to ensure the data can support future analysis.
Overall a monitoring plan is created to evaluate the effectiveness of the implementation strategies and TMDL elements such as numeric targets and pollutant estimates.
Examples of key questions:
- Are selected indicators capable of detecting impacts to designated use and responding in a measurable way to control actions?
- Have baseline or background conditions been adequately characterized?
- Are numeric targets set at levels that reasonably promote desired water quality for designated uses of concern?
- Have important pollutant sources been identified?
- Have important pollutant sources been accurately estimated?
In a TMDL document, the aim of the linkage analysis is to link pollutant loads to water quality. This link supports TMDLs (loading capacity per day) specified to meet the numeric target (overall load concentration).
Margin of Safety
The margin of safety (MOS) for the Lower Salinas River Watershed is still being developed. A MOS is used to account for the uncertainty in the linkage between nutrient loads and nutrient pollutant concentrations in the receiving water body.
There are two methods to approach the margin of safety in a TMDL report. One incorporates uncertainties implicitly by using conservative estimates in the model. The other option for incorporating uncertainty (MOS) is to quantify a portion of the total TMDL, leaving the remainder as sources (allocations are important here). It is important to not only make conservative assumptions about the parameters, but the thresholds as well. Uncertainties that would be useful to take into consideration in regards to the LSRW include:
- finite data availability
- concentrations are discrete values that have been estimated based on a specific amount of parameters and do not necessarily account for the interactions of parameters
- the model may not be representative of the actual environmental conditions
- rain patterns vary from one year to the next so dilutions vary
- nutrients bioavailability to macrophytes
In order to develop a proper margin of safety it is useful to reference other TMDL reports(ELABORATE..).
Some reports employ conservative estimates within their water quality objectives, thus implicitly accounting for the margin of safety. An important factor to consider when using conservative estimates in lieu of quantitative margins is to explicitly address the individual assumptions that are being accounted for. An efficient way to make conservative assumptions on a in an efficient way is to assume low flow conditions.
The MOS for the XXXXX is dependent on the assumptions put into the INN benthic biomass modeler.
If all sources of variability have been accounted for in the model by incorporating conservative assumptions, then that may be stated as the margin of safety. However, if any significant uncertainties have not been incorporated in the model, an explicit margin of safety should be identified. The typical margin of safety that has been accepted in California is about 20%, but this can vary depending on land uses and other variables affecting nutrient loading into water bodies.
Load allocations (LAs)
TMDLs include the total concentration of nutrients allowed to be discharged into a water body by all possible sources. The allocations are typically comprised of Load Allocations (LAs) from nonpoint sources and Waste Load Allocations (WLAs) from point sources and also includes a Margin of Safety (MOS) to account for unexpected sources of a particular contaminant, as a formula:
TMDL = LC* = LAs + WLAs + MOS
- Loading Capacity (LC) is the total amount of a pollutant load a waterbody can receive without exceeding water quality standards.
The 2012 draft TMDL report suggests that, "SWRCB, California Coastal Commission and other State agencies have identified management measures (MMs) to address agricultural sources of nutrient pollution that affect State waters."
On August 8, 1997, the Environmental Protection Agency (EPA) issued a memorandum  , “New Policies for Establishing and Implementing Total Maximum Daily Loads (TMDLs),” which directs EPA regions to work in partnership with states to achieve nonpoint source load allocations established for 303(d)-listed waters impaired solely or primarily by nonpoint sources.
To this end, the memorandum asks that regions assist states in developing implementation plans that include reasonable assurances that the nonpoint source load allocations established in TMDLs for waters impaired solely or primarily by nonpoint sources will in fact be achieved; a public participation process; and recognition of other relevant watershed management processes. Although implementation plans are not approved by EPA, they help establish the basis for EPA’s approval of TMDLs.
The purpose of an Implementation Plan is to describe the steps necessary to reduce pollutant loads to achieve these TMDLs. Implementation Plans identify the following: 1) actions expected to reduce pollutant loading; 2) parties responsible for taking these actions; 3) regulatory mechanisms by which the Central Coast Water Board will assure these actions are taken; 4) reporting and evaluation requirements that will indicate progress toward completing the actions; 5) a timeline for completion of implementation actions. Implementation Plans also address economic considerations to achieve compliance.
Public participation is a requirement  of the TMDL process and is vital to a TMDL’s success. The August 23, 1999, proposed regulation states that the public must be allowed at least 30 days to review and comment on a TMDL prior to its submission to the EPA for review and approval. In addition, with a TMDL submittal, the EPA must be provided with a summary of all public comments received regarding the TMDL and staff response to those comments, indicating how comments were considered in the final decision.
Typically a TMDL report may go through one or more cycles where staff receive public comments and revise the report to reflect those comments appropriately. The figure (right) is an example of the iterative development process (Factsheet).
Previous TMDLs in the Monterey Bay Region of California have not included critical conditions. The 2003 Santa Clara River Nitrogen TMDL included critical conditions. Although the climate around the Santa Clara River is drier, that water body is similar to the Lower Salinas River in seasonal flow and the effects of the first large storm ("first-flush").
Although not an ideal approach, the Santa Clara River TMDL makes an attempt to incorporate the increased impairment hazard presented by seasonal variation . Specifically, critical conditions were evaluated on the basis of those conditions that would cause an increase in inorganic nitrogen species due to either (1) low flow conditions, (2) the effects of the first big storm of the season (first flush), or, (3) rising groundwater effects.
- Clean Water Act
- The 303d list of Impaired Waterbodies in the Monterey Bay Region
- TMDL for Nutrients in Lower Salinas River Watershed, Monterey County, California
- Monterey Bay Area TMDL Listings - Priorities, Progess, and Documents
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
<ref> tags exist, but no
<references/> tag was found