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Pre-Application Meeting PRE2021-000
Comprehensive Plan Amendment – Mineral Resource Land Overlay
Ch: 18.15 JCC
Mineral Resource Lands (MRL).
(a) Mineral Resource Lands Overlay District (MRL). The mineral resource land district is to
provide for the conservation of mineral lands of long-term commercial significance (Article VI-C
of this chapter). The intent of this district is to aid in sustaining and enhancing mineral
extraction and processing activities of long-term commercial significance by protecting
designated lands from incompatible development and to allow for the continued contribution of
mineral lands to the Jefferson County economy. [Ord. 8-06 § 1]
18.15.170 Designation procedures.
A mineral resource land (MRL) overlay district may be applied based upon the following criteria, only
upon acceptance by the county of a complete application from a property owner and upon approval
of a redesignation in accordance with Chapter 18.45 JCC and processed as a Comprehensive Plan
amendment. MRLs of long-term commercial significance are those lands from which the commercial
extraction of minerals (sand, gravel, rock, and other valuable aggregate or metallic substances) can
be anticipated within 20 years and which are characterized by all of the following:
(1) Have a known or potential extractable resource in commercial quantities verified by submittal of a
geologic and economic report prepared by a qualified professional;
(2) The parcel is a minimum of 10 acres in size;
(3) The subject property is surrounded by parcels no smaller than five acres in size on 100 percent
of its perimeter;
(4) The current or future land use designation will not exceed a residential density of one dwelling
unit per five acres;
(5) Are not within any shoreline designation, urban growth area or rural village center or within one-
half mile of any established or potential urban growth area or rural village center boundary, as shown
on the official maps of the Comprehensive Plan; and
(6) Are not within a regulated wetland or fish and wildlife habitat area pursuant to
Chapter 18.22 JCC. [Ord. 14-18 § 4 (Exh. B); Ord. 8-06 § 1]
18.15.180 Nuisance and disclosure provisions.
(1) Nuisance. The following shall not be considered a nuisance: mineral resource extraction and
processing activities, operations (except between 7:00 p.m. and 7:00 a.m. and on weekends),
facilities or appurtenances thereof, conducted or maintained for commercial mineral resource
extraction and processing purposes on land designated as mineral resource land (MRL), regardless
of past or future changes in the surrounding area land use or land use designation.
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(2) Disclosure. The disclosure statement in subsection (2)(b) of this section shall be used under the
following circumstances and in the following manner:
(a) Approval of any land division, land use, building, or development of lands adjacent to or
within 500 feet of lands designated as mineral resource land (MRL) shall be conditioned on the
execution by the applicant of a statement of acknowledgment containing the disclosure
statement on forms provided by the department of community development. However, if a
disclosure conforming to the provisions of this section has been provided for a prior permit,
subsequent disclosures shall not be required.
(b) The required disclosure statement is as follows:
If your real property is within five hundred (500) feet of real property within an area designated as
Mineral Resource Land (MRL), you may be subject to inconveniences or discomforts arising from
such operations, including but not limited to noise, tree removal, odors, fumes, dust, smoke, the
operation of machinery, and the storage and disposal of aggregate products. One or more of the
inconveniences described may occur as a result of extraction and processing operations which
are in conformance with existing laws and regulations. Jefferson County has determined that the
use of certain real properties for mineral resource extraction and processing activities is
necessary to ensure resource availability in the County. The County will not consider to be a
nuisance those inconveniences or discomforts arising from extraction and proc essing operations,
if such operations are consistent with commonly accepted best management practices and
comply with local, state, and federal laws.
[Ord. 8-06 § 1]
18.15.155 Established.
Overlay districts provide regulations in addition to those of other sections in this code for certain land
areas and for uses which warrant specific recognition and management. See the official maps for the
location of the overlay districts. Except as otherwise provided in this Article VI, the provisions of an
overlay district shall prevail over any conflicting provisions of this code for the duration of the overlay
district, subject to RCW Title 36. All other provisions of this code shall remain in full force and effect
within the overlay district.
18.20.240 Mineral extraction, mining, quarrying and reclamation.
(1) In addition to meeting all other applicable requirements of this code, including this section, all new
mineral extraction and mineral processing activities located outside of an approved mineral resource
land (MRL) overlay district designation (as specified in Article VI-C of Chapter 18.15 JCC) shall be subject
to the following standards:
(a) New mineral extraction and mineral processing activities in rural residential districts shall require a
conditional use permit subject to a Type III permit approval process.
(b) The total disturbed area of mineral extraction, mining and quarrying sites (excluding access roads)
and any associated mineral processing activities shall not exceed 10 acres. Any proposed mineral
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extraction which would create disturbed areas in excess of 10 gross acres shall require an MRL
designation in accordance with Article VI-C of Chapter 18.15 JCC.
(2) The following standards apply to all surface mining and reclamation activities:
(a) All surface extraction shall be performed in full compliance with the Washington State Surface
Mining Act (Chapter 78.44 RCW). Other extraction must conform with all applicable Washington State
laws.
(b) Applications for development permits for extraction shall be accompanied by a report prepared by a
professional geologist which shall include at least the following information:
(i) Types of materials present on the site;
(ii) Quantity and quality of each material;
(iii) Lateral extent of deposit(s);
(iv) Depth of deposit(s);
(v) Depth of overburden; and
(vi) Method of extraction.
(c) All extraction, surface mining, and reclamation operations must, to the extent possible, employ best
management practices (see Chapter 18.30 JCC) for drainage and erosion and sedimentation control,
buffer zones, and other precautionary measures as appropriate to protect adjoining lands, surface and
groundwater quality and quantity, natural drainage systems, critical areas, wildlife habitat, and scenic
resources from adverse impacts resulting from the extraction operations and to meet the standards of
this code and other applicable county, state, and federal codes and regulations.
(d) Topsoil or other overburden having value for agriculture or other beneficial uses shall not be
removed or disposed of in a manner which will reduce its value or prevent its future use.
(e) Spoils shall be placed outside of critical areas and their buffers, and shoreline areas. Final slope angle
shall be no steeper than 1.5:1. Best management practices shall be employed for drainage and other
controls so that: (i) spoils are properly drained and do not cause ponding; (ii) runoff water meets the
requirements and standards of this code and other applicable county, state and federal codes and
regulations; and (iii) mass soil movement is prevented.
(f) All extraction and reclamation activities that create a noise disturbance must take place between 7:00
a.m. and 7:00 p.m. on weekdays, unless extended hours of operation are authorized for emergency
purposes by the administrator. No use shall be made of equipment or material which produces
unreasonable vibration, noise, dust, smoke, odor, electrical interference to the detriment of adjoining
property or the persons having the quiet use and enjoyment of that adjoining property.
(g) The alteration, intensification, and expansion of existing gravel pits and surface mining operations is
allowed subject to reasonable performance standards to ensure that alteration, intensification, and
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expansion of such uses have minimal adverse impacts on surrounding areas and uses; and provided,
that:
(i) If increased off-site impacts (noise, vibration, dust, traffic) would result from expansion,
intensification, or modification, a conditional use permit shall be required.
(ii) Modification to include a new use or operation (e.g., a rock crusher) shall require a conditional use
permit subject to a Type III permit approval process.
(h) The following performance standards are required for mining, quarrying and asphalt/concrete batch
operations located within a designated susceptible aquifer recharge area or special aquifer recharge
protection area. Mining, quarrying and asphalt/concrete batch operations in such areas must also
comply with the best management practices identified in JCC 18.30.170 for those activities. Asphalt
batch plants are prohibited in special aquifer recharge protection areas (JCC 18.15.250(1)(b)).
(i) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plants located within a
designated critical aquifer recharge area shall, prior to approval and operation, submit a site evaluation
report to Jefferson County for review and approval. Prior to preparation of a site evaluation report, the
applicant shall prepare and submit a scope of work for the report to Jefferson County for review and
approval.
(ii) At a minimum, the site evaluation report shall contain the following elements: (A) permeability of the
unsaturated zone, (B) location of nearby sensitive areas (wellhead protection areas, special protection
areas, etc.), (C) groundwater depths and flow direction, (D) location, construction, and use of existing
wells within one-quarter mile of the subject site, (E) site map at one inch to 2,000 feet scale, (F) activity
characterization, (G) proposed best management practices, and (H) a contingency plan. In addition, the
following detailed information about the hydrogeologic characteristics of the site and a prediction of the
behavior of a contaminant may be required: (A) background water quality compiled over at least a one-
year period, (B) contaminant transport modeling based on potential releases to groundwater, (C)
modeling of groundwater withdrawal effects, (D) geologic and hydrogeologic characteristics including,
but not limited to, surface water on-site and with the subbasin or watershed that may have interactions
with groundwater or surface contaminants, and (E) groundwater monitoring plan provisions.
(iii) Gravel mining and rock quarrying operations located within a designated critical aquifer recharge
area shall, prior to approval and operation, obtain a National Pollutant Discharge Elimination System
and State Waste Discharge Individual General Permit (NPDES) for process water, stormwater, and mine
dewatering water discharges from the Washington State Department of Ecology, Water Quality
Program.
(iv) Cement concrete batch plants, and asphalt concrete batch plants located within a designated critical
aquifer recharge area shall, prior to approval and operation, obtain a National Pollutant Discharge
Elimination System and State Waste Discharge Individual Permit from the Washington State Department
of Ecology, Water Quality Program.
(v) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plants located within a
designated critical aquifer recharge area shall demonstrate that the proposed activities shall not cause
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degradation of the groundwater quality below the standards described in Chapter 173-200 WAC (Water
Quality Standards for Ground Water of the State of Washington).
(vi) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plants located within a
designated critical aquifer recharge area shall, pursuant to JCC 18.30.170(1), implement the Washington
State Department of Ecology’s Storm Water, Water Quality, Hazardous Waste, Wetland, and Solid
Waste Program BMPs and relevant BMPs from the Departments of Health, Agriculture, Transportation,
and State Conservation District Office or demonstrate through a best management practices report
pursuant to JCC 18.30.170(2), how they will integrate other necessary and appropriate mitigating
measures on the design, installation, and management of the proposed facility or use.
(vii) Provide a written agreement to the county providing that all employees at mining, quarrying,
cement concrete batch plants, or an asphalt batch plant site, will be notified that the operation lies
above an aquifer recharge area and providing annual training regarding all measures set forth by the
BMPs established in JCC 18.30.170 (1).
(viii) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plants located within
a designated critical recharge area shall at all times comply with Olympic Air Pollution Control Authority
permit requirements.
(ix) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plant operations
located within a designated critical area aquifer recharge area shall engage a third party, selection of
which is approved in advance by the county, to monitor compliance with regulations and conditions
pertaining to their NPDES/state waste discharge permit. Reports shall be prepared and distributed as
required in the NPDES/state permit with copies to the county each month unless the permit requires
quarterly reporting, in which case copies will be provided to the county quarterly.
(x) Mining, quarrying, cement concrete batch plants, and asphalt concrete batch plant operations
located within a designated critical area aquifer recharge area shall submit an annual report to the
county evaluating implementation of the Department of Natural Resources approved reclamation plan.
A qualified, independent consultant approved by the county shall prepare the report. The report shall
identify how restoration of the site compares to the approved reclamation plan and whether any
corrective action is contemplated by the applicant or required by the Department of Natural Resources.
[Ord. 14-18 § 4 (Exh. B); Ord. 8-06 § 1]
18.30.170 Mining, quarrying and asphalt/concrete batch plant
best management practices in critical aquifer recharge areas.
The following shall be considered minimum development standards necessary only for mineral
extraction, quarrying and asphalt/concrete batch plant operations located in susceptible aquifer
recharge areas or special aquifer recharge protection areas as defined in Article VI-E of
Chapter 18.15 JCC. See also the performance and use-specific standards requirements of
JCC 18.20.070 (Asphalt and Concrete Batch Plants) and JCC 18.20.240 (Mineral Extraction, Mining,
Quarrying and Reclamation) for general mining, quarrying and asphalt/concrete batch plant
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operations. Asphalt batch plants are prohibited in special aquifer recharge protection areas
(JCC 18.15.250(1)(b)).
(1) Best Management Practices.
(a) Concrete and Asphalt Production at Stationary Sites. This activity applies to any activity
that mixes raw materials on-site to produce or enhance concrete or asphalt. It also applies to
subsequent activities such as pouring concrete structures, and making other concrete and
asphalt products. Mishandling of raw materials on concrete production can introduce
suspended solids and heavy metals to stormwater runoff and cause pH increases in receiving
waters. In addition, stormwater pollution can result from washing of waste concrete from
trucks, forms, wheelbarrows, buckets, and other equipment in the work area. The loose
chunks of aggregate resulting from washing of equipment can easily reach storm drains, either
in the wash water itself or in stormwater runoff. Asphalt emulsion and chunks of aggregate can
easily wash off of equipment used in mixing and production in a similar manner as concrete.
Mobile concrete pouring and asphalt application are covered under a separate activity in these
administrative rules. Concrete production at mining sites is also covered by this activity.
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods, or
practices, are required if you are engaged in concrete and asphalt mixing and production:
(A) Discharge all process water from production, pouring, and equipment cleaning
activities to a sump, process water treatment or recycling system, or sanitary sewer
system.
(B) Contain the production and pouring area to prevent stormwater from entering the
area and carrying pollutants away.
(C) Routine maintenance.
(I) Sweep the production and pouring areas weekly, if it is paved, to collect
loose chunks of aggregate and raw material particles for recycling or proper
disposal.
(II) Do not hose down area to a storm drain.
(ii) Additional BMPs. The following BMPs, intended to provide improved pollution control,
may be required of an applicant by the administrator in a manner consistent with
Chapter 18.40 JCC:
(A) Use an oil control device in the catch basins to treat stormwater runoff.
(B) Cover the production area with provisions for prevention of stormwater run on.
(C) Pave the mixing, production and/or pouring area(s) with a slope to a central
collection area. For concrete production and pouring activities, a sump drain should
not be provided because it would be quickly clogged with hardened concrete. It may
not be wise to segregate the mixing and pouring area from the curing area because
wastewater from curing applications could be collected by a drain. By sloping the
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pavement to a central location, loose chunks of concrete or asphalt aggregate can
be collected more easily and recycled or disposed of properly.
(b) Storage of Liquid Materials in Stationary Tanks. This section applies to any activity that
stores any type of liquid chemicals, waste oils, solvents, or petroleum products in above-
ground storage tanks. Leaking tanks on these sites can contribute toxic compounds, oils and
greases, heavy metals, abnormal pH, and nutrients to stormwater runoff. In addition, spills may
occur during liquid transfer operations to and from the tanks.
This activity does not apply to underground storage tanks or to businesses permitted by the
Washington State Department of Ecology to treat, store, or dispose of dangerous wastes.
Storage of reactive, combustible, or flammable liquids must comply with the fire code
requirements and may need to comply with the Washington State Department of Ecology
regulations.
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods or
practices are required if you are engaged in storage of liquid materials in stationary tanks:
(A) Store and contain liquid materials in such a manner that if the tank is ruptured,
the contents will not discharge, flow or be washed into the storm drainage system,
surface waters, or groundwater.
OR
(B) If the liquid is oil, gas or other material that separates from and floats on water,
install a spill control device (such as a tee section) in the catch basins that collect
runoff from the storage tank area.
(C) Routine Maintenance.
(I) Place drip pans or absorbent materials beneath all mounted taps, and at all
potential drip and spill locations during filling and unloading of tanks. Any
collected liquids or soiled absorbent materials must be reused/recycled or
properly disposed.
(II) Store and maintain appropriate spill cleanup materials in a location known
to all near the tank storage area; and ensure that employees are familiar with
the site’s spill control plan and/or proper spill cleanup procedures.
(III) Sweep and clean the storage area monthly if it is paved; do not hose down
the area to a storm drain.
(IV) Check tanks (and any containment sumps) daily for leaks and spills.
Replace tanks that are leaking, corroded, or otherwise deteriorating with tanks
in good condition. Collect all spilled liquids and properly dispose of them.
(c) Storage of Any Liquid Material in Portable Containers. This section applies to any activity
that stores any type of liquid chemicals, waste oils, solvents or petroleum products in portable
containers (such as drums). This activity covers permanent storage as well as temporary
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storage areas at temporary sites. Spills and drips of these liquids, or overtopping of storage
containers, can contribute toxic compounds, oils and greases, heavy metals, abnormal pH,
and nutrients to stormwater runoff.
This section does not apply to businesses that are permitted by the Washington State
Department of Ecology to treat, store, or dispose of dangerous waste. Storage of reactive,
combustible, or flammable liquids must comply with the Washington State Department of
Ecology regulations.
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods, or
practices, are required if you are engaged in storage of liquid materials in portable
containers:
(A) Place tight-fitting lids on all containers.
(B) Enclose or cover the containers where they are stored. The local fire district
must be consulted for limitations on clearance of roof covers over containers used to
store flammable materials.
(C) Raise the containers off the ground by use of pallet or similar method, with
provisions for spill control.
OR
(D) Contain the material in such a manner that if the container leaks or spills, the
contents will not discharge, flow, or be washed into the storm drainage system,
surface waters, or groundwater.
(E) Place drip pans or absorbent materials beneath all mounted container taps, and
all potential drip and spill locations during filling and unloading of containers. Any
collected liquids or soiled absorbent materials must be reused/recycled or properly
disposed.
(F) Routine Maintenance.
(I) Store and maintain appropriate spill cleanup materials in a location that is
known to all employees near the tank storage areas, and ensure that
employees are familiar with the site’s spill control plan and/or proper spill
cleanup procedures.
(II) Sweep and clean storage area monthly if it is paved; do not hose down the
area to a storm drain.
(III) Check containers (and any containment sumps) daily for leaks and spills.
Replace containers that are leaking, corroded, or otherwise deteriorating with
ones in good condition. If the liquid chemicals are corrosive, containers made
of compatible materials must be used instead of metal drums. New or
secondary containers must be labeled with the product name and hazards.
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(IV) Collect all spilled liquids and properly dispose of them.
(d) Storage of Soil, Sand, Salt and Other Erodible Materials. This section applies to stockpiling
erodible raw materials such as soil, sawdust, gravel, sand and road de-icing salts. It covers
permanent sites as well as temporary construction sites and other temporary locations. Raw
material stockpiles can easily erode due to wind or precipitation and contribute suspended
solids, nutrients, heavy metals, and abnormal pH to stormwater runoff.
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods, or
practices, are required if you are engaged in the storage or stockpiling of erodible
material on a normal or temporary basis:
(A) Site and contain the stockpiles of raw material in such a manner so as to prevent
off-site impacts of surface water runoff, erosion, and sedimentation.
(B) Routine Maintenance.
(I) Sweep paved storage areas monthly for collection and disposal of loose
solid materials; do not hose down the area to a storm drain or conveyance
ditch.
(II) Stock cleanup materials, such as brooms, dust pans, and vacuum
sweepers (if desired) near the storage unit.
(ii) Additional BMPs. The following BMPs, intended to provide improved pollution control,
may be required of an applicant by the administrator in a manner consistent with
Chapter 18.40 JCC:
(A) A catch basin insert, configured for sediment removal, may remove some of the
pollutants in runoff from this activity. (Catch basin inserts require frequent
maintenance to be effective. Carefully consider this when making your decision.)
(e) Engine Repair and Maintenance. This activity applies to operations that conduct engine
repair and maintenance in vehicles and other equipment. It also applies to mobile vehicle
maintenance operations, such as at construction sites. This common activity can lead to
immediate stormwater contamination if it is not done in a controlled manner. This activity can
contaminate stormwater with toxic hydrocarbons, other toxic organic compounds, oils and
greases, abnormal pH, and heavy metals. Related vehicle maintenance activities are covered
under the following activity headings in these administrative rules: “Painting, Finishing, and
Coating of Vehicles, Products and Equipment,” “Vehicle Washing and Stream Cleaning,”
“Fueling Operations, and Vehicle and Equipment Parking and Storage.”
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods, or
practices, are required if you are engaged in engine repair and maintenance:
(A) If temporary work is being conducted outside, use tarp, ground cloth, or drip
pans beneath the vehicle or equipment to capture all spills and drips. The collected
drips and spills must be disposed of, reused, or recycled properly.
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(B) If the work is done on a regular basis at a stationary business location, move the
activity indoors.
(C) Routine Maintenance.
(I) Employees must be educated on proper handling and disposal of engine
fluids.
(II) Store and maintain appropriate spill clean up materials in a location known
to all; and ensure that employees are familiar with the site’s spill control plan
and/or proper spill cleanup procedures (reusable cloth rags can be used to
clean up small drips and spills instead of disposables; these can be washed by
a permitted industrial laundry; do not clean them at home or a coin-operated
laundry business).
(III) Sweep the maintenance area weekly, if it is not paved, to collect loose
particles, and wipe up all spills with rags and other absorbent material
immediately; do not hose down the area to a storm drain.
(ii) Additional BMPs. The following BMPs, intended to provide improved pollution control,
may be required of an applicant by the administrator in a manner consistent with
Chapter 18.40 JCC:
(A) Absorbent material such as pillows or brooms can be used around storm drains
or in catch basins to absorb oil and other substances. A qualified disposal contractor
must pick up used absorbent material containing oil or other engine fluids.
(B) A catch basin insert, configured for oil removal, may remove some of the
pollutants in runoff from this activity. (Catch basin inserts require frequent
maintenance to be effective. Carefully consider this when making your decisions.)
(f) Vehicle Washing and Steam Cleaning. This activity applies to operations that receive
shipments of bulk liquid materials by truck or rail and transfer those liquids into storage tanks
or containers or handle the truck or rail loading of liquid materials from tanks. Spills and drips
of these liquids can potentially contribute toxic organic compounds, oils and greases, nutrients,
heavy metals, and abnormal pH to stormwater runoff.
(i) Minimum Requirements. The following BMPs, or equivalent measures, methods, or
practices, are required if you are engaged in vehicle washing and steam cleaning:
(A) It is allowable to rinse down the body of a vehicle, including the bed of a truck,
with just water without doing any washwater control BMPs.
(B) If you wash (with mild detergents) on an area that infiltrates water, such as
gravel, grass or loose soil, it is acceptable to let the washwater infiltrate as long as
you only wash the body of the vehicles.
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(C) However, if you wash on a paved area and use detergents or other cleaners, or
if you wash/rinse the engine compartment or the underside of the vehicles, you must
do one of the following options:
(I) Designate and pave wash area to wash all vehicles in. Discharge wash
water from vehicle cleaning operations to a sanitary sewer, holding tank, or
process treatment system or process through an enclosed recycling system.
The local sewer authority may have limits on the types and amounts of
pollutants, such as oil and heavy metals that can be discharged to a sanitary
sewer. Absolutely no untreated wash water can enter storm drains.
OR
(II) Designate and pave wash area to wash all vehicles in. Use a storm drain
cover or other effective method of preventing all wash and rinse water from
entering a storm drain or other drainage system feature. All runoff from the
activity must be collected from proper disposal to a sanitary sewer. A wet
vacuum or pump can be used for this. There are several products commercially
available that enable collection of runoff. This requirement also applies to
mobile vehicle washing services.
OR
(III) Take the vehicles to a commercial car wash or use a mobile washing
service that complies with either of the previous options.
(D) Designated wash area must be well-marked with signs indicated where and how
washing must be done.
(E) Oil changes and other engine maintenance cannot be conducted in the
designated washing area.
(g) Optional BMPs. The BMPs listed below are measures that should be considered at all
times for improving pollution control. While these BMPs are not mandatory, applicants are
encouraged to incorporate them in their plan for implementing BMPs, and the administrator
may, in a manner that is consistent with Chapter 18.40 JCC, require that an applicant
implement one, several or all of the BMPs listed in this section. Implementing one, some or all
of these BMPs may reduce or eliminate the need to implement other more complex or costly
BMPs.
(i) Locate activities as far as possible from surface drainage paths. Locating activities on
high ground, far from drainage paths, ditches, gutters and storm drains allows more time
to recognize spills and act to prevent water contamination.
(ii) Avoid the activity or reduce its occurrence. Often an alternative production process or
material application process can be used to substitute for another, more polluting,
process. Ideally, a polluting activity can be avoided altogether, or its frequency of
occurrence reduced. An example is washing vehicles less often or taking vehicles to
commercial car washes or detail shops rather than washing on-site.
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(iii) Use less material. Improper disposal of excess material or increased application of
materials simply because excess is available can cause pollution. Purchase only the
amount of material that will be needed for foreseeable use. In most cases you will see
cost savings in both purchasing and disposal.
(iv) Use the least toxic materials available. All applications of solid and liquid materials
should use the least toxic products and raw materials available, whether in production;
cleaning; pesticide applications; or other uses.
(v) Create and/or maintain vegetated areas near activity location. Grass and types of
vegetation can filter out many pollutants in stormwater runoff. Vegetated areas should be
maintained around areas where polluting activities occur, especially down slope of activity
areas. Routine maintenance will keep vegetated areas healthy and capable of filtering
pollutants.
(vi) Recycle as much as possible. Recycling is always preferable to disposal of unwanted
materials. Leftover paints, finishes, cleaning materials, building materials, etc., may be
used by someone else, so don’t throw them away. Contact a neighbor, friend, school,
church, community group, theater group, etc., to see if your leftover materials can be
used. Many empty containers and other common items are recyclable. Contact the
Jefferson County Recycling Center for recycling options.
(vii) Educate others about stormwater pollution prevention. Educate your employees,
business associates, contractors, family, and friends about stormwater pollution control.
Encourage others to find solutions to stormwater pollution problems, and to continue
learning about pollution control techniques.
(viii) Implement treatment BMPs. Treatment BMPs are used to remove pollutants from
stormwater before being discharged from a site. These include oil separators and other
catch basin inserts that control pollutants in the piped system and as well as numerous
biological systems such as a biofiltration swales, infiltration, and constructed wetlands.
These BMPs may be a preferred option in certain circumstances.
(2) Best Management Practices (BMP) Report Criteria. The following criteria shall apply when
preparing a best management practices (BMP) report:
(a) The report shall be prepared by, or done under the direction of or designed by, a qualified
person with demonstrated expertise in the industry or field as demonstrated by a statement of
qualifications.
(b) The report will identify appropriate BMPs and how they will be employed to prevent
degradation of groundwater. Examples of BMPs are found in subsection (1) of this section. All
necessary technical data, drawings, calculations, and other information to describe application
of the BMPs must be supplied.
(c) The report shall identify how the applicant will satisfy the requirements of the Dangerous
Waste Regulations, Chapter 173-303 WAC, in the event that hazardous material is released
into the ground or groundwater.
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Pre-Application Meeting PRE2021-000
Comprehensive Plan Amendment – Mineral Resource Land Overlay
(d) The report shall be reviewed by the department of community development or a consultant
hired by the county, at the applicant’s expense, for this review. The county may consult with
the Jefferson County health department, State of Washington Departments of Health or
Ecology, independent reviewer, or any parties as it sees fit. [Ord. 8-06 § 1]