BEST MANAGEMENT PRACTICE (BMP) BASICS

BMP Basics provides a description of agricultural, urban, mixed open, resource, and
septic system best management practices that are credited in the Chesapeake Bay
Watershed Model (Phase 4.3). For each BMP, BMP Basics provides a description, a
photograph, and, where appropriate, a short list of examples. The nitrogen,
phosphorus, and sediment pollutant removal efficiencies for each BMP can be found at
http://www.chesapeakebay.net/pubs/waterqualitycriteria/CBWS model BMP.doc.
Additional tributary strategy tools and information can be found on the web site at
www, chesapeakebay. net/tribtools. htm


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AGRICULTURAL BMPs

BMP:	Conservation Tillage

Description: Conservation tillage involves planting and growing crops with
minimal disturbance of the surface soil. Conservation tillage
requires two components, (a) a minimum 30% residue coverage at
the time of planting and (b) a non-inversion tillage method. No-till
farming is a form of conservation tillage in which the crop is seeded
directly into vegetative cover or crop residue with little disturbance
of the surface soil. Minimum tillage farming involves some
disturbance of the soil, but uses tillage equipment that leaves much
of the vegetation cover or crop residue on the surface.6

Source: USDA, NRCS


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BMP:

Riparian Forest Buffers (Agriculture)

Description: Agricultural riparian forest buffers are linear wooded areas along
rivers, stream and shorelines. Forest buffers help filter nutrients,
sediments and other pollutants from runoff as well as remove
nutrients from groundwater. The recommended buffer width for
riparian forest buffers (agriculture) is 100 feet, with a 35 feet
minimum width required.6

Source: USDA. NRCS


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BMP:	Riparian Grass Buffers (Agriculture)

Description: Agricultural riparian grass buffers are linear strips of grass or other
non-woody vegetation maintained between the edge of fields and
streams, rivers or tidal waters that help filter nutrients, sediment
and other pollutant from runoff. The recommended buffer width for
riparian forests buffers (agriculture) is 100 feet, with a 35 feet
minimum width required.6


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BMP:	Wetland Restoration (Agriculture)

Description: Agricultural wetland restoration activities re-establish the natural
hydraulic condition in a field that existed prior to the installation of
subsurface or surface drainage. Projects may include restoration,
creation and enhancement acreage. Restored wetlands may be
any wetland classification including forested, scrub-shrub or
emergent marsh.13

Source: USDA, NRCS


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Land Retirement (Agriculture)

Agricultural land retirement takes marginal and highly erosive
cropland out of production by planting permanent vegetative cover
such as shrubs, grasses, and/or trees. Agricultural agencies have
a program to assist farmers in land retirement procedures. Land
retired and planted to trees is reported under "Tree Planting".6


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BMP:

Description:

Examples:

Tree Planting (Row Crop)

The tree planting (row crop) BMP includes any tree planting on
agricultural lands, except those used to establish riparian forest
buffers, targeting lands that are highly erodible or identified as
critical resource areas. Tree planting is also called afforestation
because it involves growing trees and converting the land use from
agricultural to forest. This BMP results in a landuse conversion
from row crop to forest. It is assumed that the density of the
plantings is sufficient to produce a forest like condition over time.3,6

Conservation Reserve Program land, converted from row crop to
forest.

Source: USDA, NRCS


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BMP:

Nutrient Management Plan Implementation (Crop)

Description: Nutrient management plan (NMP) implementation (crop) is a

comprehensive plan that describes the optimum use of nutrients to
minimize nutrient loss while maintaining yield. A NMP details the
type, rate, timing, and placement of nutrients for each crop. Soil,
plant tissue, manure and/or sludge tests are used to assure optimal
application rates. Plans should be revised every 2 to 3 years.6

Source: USDA, NRCS


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BMP:

Description:

Examples:

Cereal Cover Crops

Cereal cover crops reduce erosion and the leaching of nutrients to
groundwater by maintaining a vegetative cover on cropland and
holding nutrients within the root zone. This practice involves the
planting and growing of cereal crops (non-harvested) with minimal
disturbance of the surface soil. The crop is seeded directly into
vegetative cover or crop residue with little disturbance of the
surface soil. These crops capture or "trap" nitrogen in their tissues
as they grow. By timing the cover crop bum or plow-down in
spring, the trapped nitrogen can be released and used by the
following crop.5

Early and Late Season Cover Crops:

Early: To be eligible for level 1-reduction credits, the cover crop
must be planted earlier than 7 days prior to the long-term published
average date of the first killing frost in the fall.

Late: To be eligible for level 2-reduction credit, the cover crop must
be planted within 7 days after the long-term published average date
of the first killing frost in the fall.

Source: USDA, NRCS


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Commodity Cover Crops

Commodity cover crops differ from cereal cover crops in that they
may be harvested for grain, hay or silage and they may receive
nutrient applications, but only after March 1 of the spring following
their establishment. The intent of the practice is to modify normal
small grain production practices by eliminating fall and winter
fertilization so that crops function similarly to cover crops by
scavenging available soil nitrogen for part of their production cycle.

This practice can encourage planting of more acreage of cereal
grains by providing farmers with the flexibility of planting an
inexpensive crop in the fall and delaying the decision to either kill or
harvest the crop based on crop prices, silage needs, weather
conditions, etc."


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BMP:	Conservation Plans

Conservation plans are reported as total acres or on a specified

landuse. The following landuse categories are associated with

Conservation Planning.

Farm Plans on Conventional Till

Farm Plans on Conservation Till

Farm Plans on Hay

Farm Plans on Pasture

Description: Farm conservation plans are a combination of agronomic,

management and engineered practices that protect and improve
soil productivity and water quality, and to prevent deterioration of
natural resources on all or part of a farm. Plans may be prepared
by staff working in conservation districts, natural resource
conservation field offices or a certified private consultant. In all
cases the plan must meet technical standards.5

Source: USDA, NRCS


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Animal Waste Management Systems

Animal waste management systems are practices designed for
proper handling, storage, and utilization of wastes generated from
confined animal operations and include a means of collecting,
scraping or washing wastes and contaminated runoff from
confinement areas into appropriate waste storage structures.
Lagoons, ponds, or steel or concrete tanks are used for the
treatment and/or storage of liquid wastes. Storage sheds or pits
are common storage structures for solid wastes. Controlling runoff
from roofs, feedlots and "loafing" areas are an integral part of these
systems.5

Lagoons, ponds, steel tanks and storage sheds


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BMP:	Phytase Feed Additives

Description: Phytase can be injected into poultry feeds by the integrator or other
feed suppliers. Manure phosphorous reductions occur because
less phosphorous needs to be blended into feed rations, resulting in
a phosphorous source reduction. A reduction up to approximately
30% in manure phosphorus may be possible under optimum
conditions.2


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BMP:

Yield Reserve

Description: Yield reserve is a reduction in nitrogen applied to cropland beyond
the nutrient management recommendation. The reduction
percentage is currently defined at 15%. Based on research, the
nutrient management rates of nitrogen application are set
approximately 35% higher than what a crop needs to ensure
nitrogen availability under optimal growing conditions. In a yield
reserve program, the farmer wouid reduce the nitrogen application
rate by 15%. An incentive or crop insurance is used to cover the
risk of yield loss.2

Source: USDA, NRCS


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BMP:

Description:

Examples:

Alternative Uses Of Manure/Manure Transport

Alternative uses of manure/manure transport is the practice of
reducing or eliminating excess nutrient applications within the
Chesapeake Bay by either transporting the manure outside of the
Chesapeake Bay watershed or finding an alternative use for the
excess manure. Excess manure is defined as manure nutrients
produced within an area that exceeds the recommended
application rates associated with the crops grown.3

Fertilization of commercial tree plantations, research and
development of new fuel technologies, peptizing for fertilizer,
transport out of the watershed to other areas that need it, and
electric generation.

Source: USDA. NRCS


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BMP:

Stream Protection With Fencing With Off Stream Watering

Description: Stream protection with fencing with off stream watering

incorporates both alternative watering and installation of fencing
that involves narrow strips of land along streams to exclude
livestock. The fenced areas may be planted with trees or grass, but
are typically not wide enough to provide the benefits of buffers.
The implementation of stream fencing should substantially limit
livestock access to streams, but can allow for the use of limited
hardened crossing areas where necessary to accommodate access
to additional pastures or for livestock watering."

Examples:	Stream fencing, alternative water sources, stream crossings


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BMP:

Description:

Examples:

Off Stream Watering In Pasture Without Fencing

Off stream watering in pasture without fencing requires the use of
alternative drinking water troughs or tanks away from streams. The
BMP may also include options to provide shade for livestock away
from streams. Limited research has been conducted for this
practice that documents changes In livestock behavior resulting in
significantly less time spent near streambanks and in streams. The
net effectiveness of the practice must reflect partial removal of
livestock from near stream areas and relocation of animal waste
deposition areas and heavy traffic areas surrounding water sources
to more upland locations.^

Alternative water sources, tree plantings away from the stream,
stream crossings

Source: USDA, NRCS


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BMP:

Off Stream Watering With Stream Fencing And
Rotational Grazing (Pasture)

Description: Off stream watering with stream fencing and rotational grazing
(pasture) combines stream fencing and alternative watering with
cross fencing systems to create paddocks to enable rapid grazing
of small areas in sequence. Once an area is intensively grazed of
most vegetative matter, the animals are moved to another paddock
to enable recovery of the pasture grasses. This BMP is beneficial
in removing animals from stream areas, but may be offset by an
increased animal stocking rate per acre. This increases the
concentration of animal manure per acre and may adversely impact
the quality of surface water runoff."

Examples:	Managing forage height through mechanical means, stocking rates,

supplemental feeding and other methods

Source: USDA, NRCS


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URBAN AND MIXED OPEN BMPs

BMP:

Description:
Examples:

Wetponds arid Wetlands

Wetponds and wetland practices collect and increase the settling of
pollutants and protect downstream channels from frequent storm
events. Wetponds retain a permanent pool of water.

Wetpond, wet extended detention pond, retention pond and
constructed wetlands

Source: MDE Water Management Administration


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BMP:

Description:

Examples:

Dry Detention Ponds and Hydrodynamic Structure

Dry detention ponds and hydrodynamic structure practices are
used to moderate flows and remain dry between storm events.
These are storm water design features that provide a gradual
release of water in order to increase the settling of pollutants and
protect downstream channels from frequent storm events. A variety
of products for these storm water inlets known as swirl separators,
or hydrodynamic structures, are modifications of the traditional oil-
grit separator and include an internal component that creates a
swirling motion as storm water flows through a cylindrical chamber.
These designs allow sediment to settle out as storm water moves in
this swirling path. Additional compartments or chambers are
sometimes present to trap oil and otherfloatables.6

Dry pond, underground dry detention facility

Source: MDE Water Management Administration


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BMP:

Description:

Examples:

Dry Extended Detention Ponds

Dry extended detention ponds are storm water design features that
provide a gradual release of a specific volume of water in order to
increase the settling of pollutants and protect downstream channels
from frequent storm events. Dry extended detention ponds are
often designed with small pools at the inlet and outlet of the pond.
These BMPs can also be used to provide flood control by including
additional detention storage above the extended detention level.6

Dry extended detention pond, extended detention basin and
enhanced extended detention

Source: MDE Water Management Administration


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BMP:

Description:

Infiltration Practices

Infiltration practices are used to capture and temporarily store the
water quality volume before allowing it to infiltrate into the soil,
promoting pollutant treatment and groundwater recharge.6

Examples:

Infiltration trench, infiltration basin, porous pavement

Source: MDE Water Management Administration


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BMP:

Description:

Filtering Practices

Filtering Practices capture and temporarily store the water quality
volume and pass it through a filter of sand, organic matter and
vegetation, promoting pollutant treatment and recharge.

Examples:

Surface sand filter, swale, bioretention areas (raingardens)

Source: Mike Herrmann


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BMP:

Description:

Examples:

Impervious Surface Reduction

Impervious surface reduction includes practices that reduce the
total area of impervious cover and practices that capture storm
water and divert it to pervious areas, subsequently encouraging
storm water infiltration.

Natural area conservation, disconnection of rooftop runoff, rain
barrels

Source: www.composters.com	Source: Unknown


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BMP:

Stream Restoration in Urban Areas

Description: Stream restoration in urban areas is used to restore the urban
stream ecosystem by restoring the natural hydrology and
landscape of a stream. Stream restoration in urban areas is used
to help improve habitat and water quality conditions in degraded
streams. Typically, streams in need of restoring have watershed
conditions that have destabilized the stream channel and eroded
stream banks. The objectives for stream restoration in urban areas
include, but are not limited to, reducing stream channel erosion,
promoting physical channel stability, reducing the transport of
pollutants downstream, and working towards a stable habitat with a
self-sustaining, diverse aquatic community. Stream restoration
activities in urban areas should result in a stable stream channel
that experiences no net aggradation or degradation over time.4

Source: Harrington and Hoyle Ltd., Landscape Architects


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BMP:

Description:

Examples:

Erosion and Sediment Control

Erosion and sediment control practices protect water resources
from sediment pollution and increases in runoff associated with
land development activities. By retaining soil on-site, sediment and
attached nutrients are prevented from leaving disturbed areas and
polluting streams.6

Silt fence, slope drain, permanent vegetation

Source: Photo Courtesy of Mike Herrmann


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BMP:

Description:

Examples:

Nutrient Management (Urban)

Urban nutrient management involves the reduction of fertilizer to
grass lawns and other urban areas. The implementation of urban
nutrient management is based on public education and awareness,
targeting suburban residences and businesses, with emphasis on
reducing excessive fertilizer use.D

Public notices on fertilizer bags, community brochures on fertilizer

use

Source: Photo Courtesy of MDE Water Management Administration


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Forest Conservation (Urban)

Urban forest conservation applies only to Maryland at this time.

This BMP in Maryland is the implementation of the Maryland Forest
Conservation Act that requires developers to maintain at least 20%
of a development site in trees (forest condition). This is actually a
preventative type of BMP which alters the rate of urban conversion.
The acreage is calculated from the annual urban increase
(population based). The 20% is specific to the Maryland Act and
could be different for each jurisdiction or various locations within a
jurisdiction.0

Use of assessments, conservation easements, purchase or transfer
of development rights, ordinances, and acquisition programs


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BMP:

Description:

Examples:

Riparian Forest Buffers (Urban)

Urban riparian forest buffers are linear strips of maintained woody
vegetation that buffer streams, rivers or tidal waters from urban and
suburban activity. Forest buffers help filter nutrients, sediments
and other pollutants from runoff, as well as remove nutrients from
groundwater. The recommended width for riparian forest buffers
(urban) is 50 feet with a 35 feet minimum. "6

Buffer strips

Source: MD DNR, Forest Service


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BMP:	Riparian Forest Buffers (Mixed Open)

Description: Mixed open is a combination of low intensity development,

recreation areas, battlefields, golf courses, school recreation areas
and other large tracts of herbaceous lands that are not easily
associated with impervious acres, but are clearly not available as,
or associated with, agricultural land. Mixed open riparian forest
buffers are areas of trees usually accompanied by other vegetation,
that are adjacent to a body of water and which: maintain the
integrity of stream channels; reduce the impact of upland pollution
sources by trapping, filtering, and converting sediments, nutrients,
and other chemicals; and supply food, cover, and thermal
protection to fish and other wildlife. The recommended width for
riparian forest buffers (mixed open) is 100 feet with a 35 feet
minimum.13


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BMP:

Tree Planting (Mixed Open)

Description: Mixed open is a combination of low intensity development,

recreation areas, battlefields, golf courses, school recreation areas
and other large tracts of herbaceous lands that are not easily
associated with impervious acres, but are clearly not available as,
or associated with, agricultural land. Mixed open tree planting
includes any tree plantings on any site except those along rivers
and streams, which are considered forested buffers and are treated
differently. The definition of tree planting does not include
reforestation.3

Source: Joseph Murray


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BMP:

Tree Planting (Urban)

Description: Urban tree planting is planting trees on urban pervious areas at a
rate that would produce a forest-like condition over time. The intent
of the planting is to eventually convert the urban area to forest. If
the trees are planted as part of the urban landscape, with no
intention to covert the area to forest, then this would not count as
urban tree planting."3

HMHB1

Source: Joseph Murray


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BMP:

Description:

Examples:

Nutrient Management (Mixed Open)

Mixed open is a combination of low intensity development,
recreation areas, battlefields, golf courses, school recreation areas
and other large tracts of herbaceous lands that are not easily
associated with impervious acres, but are clearly not available as,
or associated with, agricultural land. Mixed open nutrient
management involves the reduction of fertilizer to non-agriculture,
herbaceous areas. Implementation of mixed open nutrient
management is based on public education and awareness, with
emphasis on reducing excessive fertilizer use in areas including,
but not limited to, golf courses and large institutional grounds.3

Nutrient management on golf courses, playing fields and/or rights of
way.

Source: Civil War Battlefields, http://www.cwbattlefields.com/marvland.html


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BMP:

Description:
Examples:

Abandoned Mine Reclamation

Abandoned mine reclamation stabilizes the soil on lands mined for
coal or affected by mining, such as wastebanks, coal processing, or
other coal mining processes

Land grading, re-vegetation, tree planting, wetland development
and the installation of surface water control measures such as
diversions, waterways, and retention ponds

BEFORE

AFTER

Source: Office of Surface Mining


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RESOURCE BMPS

BMP:	Forest Harvesting Practices

Description: Forest harvesting practices are a suite of BMPs that minimize the
environmental impacts of road building, log removal, site
preparation and forest management. These practices help reduce
suspended sediments and associated nutrients that can result from
forest operations.

Examples:	Innovative road design, bridged stream crossings, preservation of

stream and wetland buffers, soil stabilization, water bars, logging
mats, road surfacing, broad-based dips and avoiding operations
when very wet.6

Source: US Forest Service


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BMP:

Description:

Examples:

Structural Tidal Shoreline Erosion Control

Structural tidal shoreline erosion control is designed to protect
eroding shorelines by armoring the shoreline to dissipate incoming
wave energy while protecting unconsolidated bank sediments.
These practices are applicable in areas of higher erosion rates or
where wave energy is too strong for vegetation alternatives. These
projects are rigid, barrier-type structures that result in a "hardening"
of the shoreline to protect against the action of waves, currents,
tides, wind driven water, runoff storms, and/or groundwater
seepage that erodes shorelines.0

Bulkheads (timber or metal), concrete or masonry walls, stone
revetments, stone reinforcements, stone breakwaters, jetties and
groins.

Source: Torn Darden


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BMP:

Non-Structural Tidal Shoreline Erosion Control

Description: Non-structural tidal shoreline erosion control projects are

bioengineering techniques that create vegetated wetlands for
protection of the shoreline. The controls are designed to protect
eroding shorelines by creating vegetated wetlands, which dissipate
incoming wave energy while protecting unconsolidated bank
sediments. A transition zone is created between the erodible
uplands and open water. These wetlands help prevent nutrient-
laden sediments from entering the waters,b

Examples:	Non-structural projects consist of placing clean sandy fill in the

intertidal zone and planting the area with native marsh grasses
such as smooth cordgrass and saltmeadow hay. Placement of
some stone may also be necessary to protect the newly created
fringe marsh. Non-structural projects are designed to create
shallow water habitat for aquatic species and waterfowl. They also
promote water quality by filtering upland runoff and trapping
sediments and nutrients. Non-structural control practices are most
applicable in tidal areas where erosion rates are 2 feet per year or
less.6

Source: Tony Allred


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SEPTIC BMPS

BMP:	Septic Connections/Hookups

Description: Septic connections/hookups represent the replacement of

traditional septic systems with connection to and treatment at
wastewater treatment plants (WWTPs).

Source: Vic Giordano


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BMP:

Septic Denitrification

Description:

Septic denitrification represents the replacement of traditional
septic systems with more advanced systems that have additional
nitrogen removal capabilities. Traditional septic systems usually
consist of a large tank designed to hold the wastewater allowing
grits and solids time for settling and decomposition. Wastewater
then flows to the second component, the drainfield. An enhanced
septic system like that shown can provide further treatment of
nitrogen through processes that encourage denitrification of the
wastewater.6

Aerobic
Unit

Treated

Wastewater

	 Effluent

Tank :¦$

Box

Air Compressor—i chamber

Source: MDE


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BMP:

Septic Pumping

Description: Septic systems achieve nutrient reductions through several types of
management practices, including frequent maintenance and
pumping. On average, septic tanks need to be pumped once every
three to five years to maintain effectiveness. The pumping of septic
tanks is one of several measures that can be implemented to
protect soil absorption systems from failure. When septic tanks are
pumped and sewage removed, the septic system's capacity to
remove settable and floatable solids from wastewater is increased.0


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FOOTNOTES

Center for Watershed Protection and Maryland Department of the Environment.
(2000). 2000 Maryland Stormwater Design Manual Volumes I & II.

Chesapeake Bay Program Agriculture Nutrient Reduction Workgroup. (11/3/03).
"Agricultural BMP Descriptions."

Chesapeake Bay Program Tributary Strategy Workgroup. (2003). Best Management
Practices - Questions and Answers. Retrieved December 11, 2003, from
Chesapeake Bay Program Web Site.

http://www.chesapeakebav.net/pubs/wateraualitvcriteria/doc-bmp Q and A.pdf

Chesaepake Bay Program Urban Storm Water Workgroup. (2003). "Stream
Restoration In Urban Areas: Crediting Jurisdictions for Pollutant Load
Reductions."

Conservation Plan (n.d.). Retrieved December 12, 2003, from WebRef.Org Web Site.
http://www.webref.Org/aariculture/c/conservation plan.htm

Technical Reference for Maryland's Tributary Strategies: Documentation for \

Data Sources and Methodologies Used in Developing Nutrient Reduction and
Cost Estimates for Maryland's Tributary Strategies (January 2003). Retrieved
December 12, 2003, from Maryland Department of Natural Resources Web
Site, (http://www.dnr.state.md.us/bav/tribstrat/tsdw/technical reference.pdf)

U.S. Department of the Interior, Office of Surface Mining, (n.d.). Retrieved December
22, 2003, from The Office of Surface Mining Web Site, (http://www.osmre.gov/)


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