Build a Watershed Nutrient Source-Control and Shoreland Action Program

Create a charter identifying the receiving-water objective, geographic scope, current watershed plan or TMDL, participating governments and organizations, Tribal jurisdiction, landowner roles, decision rules, conflict process, records, and accountability. Separate voluntary assistance, grant eligibility, regulatory decisions, and public claims.

Use respectful participation and minimum-necessary data. Do not publish property-level source allegations or assume that one government can authorize work on another jurisdiction's or a private party's land.

Sources: [1], [23]

Sources: [1], [2]

• Source and pathway evidence is sufficient for the proposed mechanism
• Affected landowners, operators, communities, and jurisdictions have a lawful participation path
• Site reconnaissance supports feasibility without replacing design
• Permit, certification, consultation, property-right, procurement, and funding pathways are identified
• Operation, maintenance, inspection, repair, and replacement owners accept their roles
• Baseline, implementation, and effectiveness evidence can be collected ethically and safely

Sources: [1], [2]

Define the no-action baseline and compare operational prevention, source substitution, inspection or repair, flow reduction, infiltration where appropriate, erosion control, treatment, restoration, acquisition or easement, outreach, policy, and further monitoring. Evaluate effectiveness evidence, site fit, risk, cost, lifecycle effort, equity, co-benefits, adverse effects, reversibility, and uncertainty.

Select systems of complementary practices when one measure cannot control the full source and transport chain. Do not transfer runoff, erosion, flooding, exposure, maintenance burden, or cost to another community or resource.

Sources: [2], [1]

Begin with runoff disconnection, soil protection, native or locally appropriate vegetation, minimized disturbance, stabilized access, and maintenance. Minnesota DNR and Extension examples illustrate principles, but their dimensions and plant guidance are not universal outside the applicable setting.

Do not prescribe a universal buffer width or assume a planted strip can compensate for concentrated flow, failing infrastructure, unstable banks, or an untreated upslope source. Resolve shoreline, grading, wetland, floodplain, easement, and local approvals before work.

Sources: [16], [17], [18]

Use current health, environmental, and local requirements to identify the responsible authority and qualified provider. Records, inspections, setbacks, soils, groundwater, hydraulic loading, components, maintenance, and receiving-water pathways may all matter. Protect household privacy and communicate findings through authorized channels.

Pumping is maintenance, not proof of treatment performance and not a repair for every failure mode. Never direct residents or volunteers to open, enter, sample, reroute, or repair septic or sewage components themselves.

Sources: [6], [7]

Prioritize source prevention, housekeeping, fertilizer and organic-material control, erosion prevention, runoff reduction, disconnection, green infrastructure, conveyance repair, treatment, and maintenance according to local conditions. Include roads, parking, municipal operations, development, and construction where evidence supports them.

Construction stormwater requirements and municipal, industrial, or other permits vary by activity and jurisdiction. Resolve applicability with responsible authorities; do not treat a national web page as authorization or a complete local specification.

Sources: [8], [9], [10], [19]

Work with producers and qualified conservation professionals to assess nutrient sources, timing, placement, rate, soil and crop conditions, erosion, runoff, drainage, livestock areas, storage, and connected pathways. Protect confidential operational data and distinguish voluntary technical assistance from regulatory functions.

NRCS national Conservation Practice Standards describe purposes and criteria, but implementation must use the current state Field Office Technical Guide and applicable laws, contracts, permits, and professional judgment. Standard 590 is not a universal fertilizer prescription and does not authorize a site plan by itself.

Sources: [11], [12], [13]

Define the inflow, pollutant form, hydrology, sediment and nutrient mechanism, bypass conditions, capacity, vegetation, pretreatment, outlet, inspection, and failure response. A filter strip and riparian forest buffer serve defined purposes under current criteria; neither has a universal width or efficiency.

Model the expected reduction as a scenario with uncertainty, then preserve it as modeled evidence. Do not report that expectation later as a measured reduction unless the effectiveness design supports that inference.

Sources: [14], [15], [2]

Record current survey and site data, design criteria, responsible designer, calculations, geotechnical or ecological needs, property rights, utilities, access, procurement, safety, permit and certification determinations, consultation, inspection hold points, and approval owners. Confirm requirements again if scope or conditions change.

Section 401 certification, Section 404 authorization, construction stormwater coverage, shoreline or wetland rules, and other approvals may apply depending on facts and jurisdiction. A pesticide label is legally enforceable; the program must not recommend use inconsistent with the current label or applicable law.

Sources: [20], [21], [19], [22]

Use a documented matrix for pathway fit, evidence, feasibility, lifecycle cost, operation and maintenance, monitoring, co-benefits, adverse effects, climate resilience, participation, accessibility, and distributional impacts. Record who participated, who decided, and how conflicts or new evidence are handled.

Fund inspection, sediment or vegetation management, repairs, replacement, training, recordkeeping, and access, not only construction. A project without a capable maintenance owner is not ready.

Sources: [1], [2]

• Approved design, revisions, approvals, and georeferenced or otherwise controlled as-built record
• Materials, dimensions, elevations, vegetation, drainage, connectivity, capacity, and deviations
• Commissioning, stabilization, initial performance checks, photographs, and inspector acceptance
• Operation, maintenance, inspection, repair, replacement, training, and record owners
• Participation, adoption, operational change, access, downtime, bypass, and failure history

Sources: [1], [3]

Define implementation endpoints and environmental outcomes separately. Before outcome data, register the comparison design, baseline and follow-up periods, stations, event and seasonal coverage, discharge or other covariates, parameters, methods, laboratories, QA/QC, missing-data rules, analysis, uncertainty, confounders, decision thresholds, and publication commitments.

Use designs proportionate to the decision, such as paired, upstream-downstream, before-after, or control-impact approaches when feasible. A trend at one station can be affected by flow, weather, upstream change, legacy stores, sampling, and unrelated actions.

Sources: [3], [4]

Report implementation fidelity, operation, maintenance, participation, modeled reduction, edge-of-practice or pathway outcomes, watershed loads, lake condition, uncertainty, and attribution strength as distinct results. Never relabel a modeled reduction as measured or project completion as effectiveness.

No detected response can reflect inadequate implementation, insufficient coverage, low power, an unsuitable indicator, lag, weather, groundwater, legacy stores, internal cycling, or a wrong conceptual model. It is not automatically failure. Likewise, a favorable change is not automatically caused by the program. Update the model, monitoring, maintenance, coverage, or alternative only through a documented review.

Sources: [3], [1]