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LAND APPLICATION SYSTEMS

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Title: LAND APPLICATION SYSTEMS


1
LAND APPLICATION SYSTEMS
2
OUTLINE OF PRESENTATION
  • Types of Land Applications Brief Overview.
  • Definitions Basic Terminology
  • 3. Subsurface, Shallow Systems In Depth
  • a. Leachfields
  • b. Mound Systems
  • c. Seepage Pits
  • 4. Land Disposal Systems In Depth Coverage
  • a. Slow Rate (SR) Infiltration Systems
  • b. Rapid Infiltration (RI) Systems
  • c. Overland Flow Systems
  • d. Planning and design
  • d. Comparison

3
DEFINITIONS
  • Effluent Flow going out of or leaving a process.
  • Influent Flowing into
  • BOD Biological oxidation demand
  • TSS Total suspended solids
  • TN Total nitrogen
  • TP Total phosphorous
  • FC Fecal Coliform
  • AWT Advanced water treatment
  • SAR Soil absorption rate
  • SR Slow rate
  • RI Rapid infiltration
  • OF Overland flow

4
Types of Land Application Systems Three Basic
Types
  • SUBSURFACE, SHALLOW AND DEEP SYSTEMS
  • Used in single dwellings and small clusters of
    dwellings
  • LAND DISPOSAL SYSTEMS
  • Used for pretreated municipal effluents
  • IRRIGATION AND LANDSCAPE USES
  • Used for final treatment and discharge of
    wastewater on vegetated plots

5
Types of Land Application Systems
  • The greater the waste strength, the larger the
    system must be.
  • This is true for all system types, and although
    each type of system introduces water into the
    soil differently, sizing for the system you
    choose is critical.
  • At some point the soil will not accept any more
    wastewater, causing failure.

6
SUBSURFACE, SHALLOW SYSTEMS
7
SUBSURFACE, SHALLOW SYSTEMS
  • Used for single dwelling or small clusters of
    dwellings
  • In California theres about 1 million households
    currently being served by these systems

8
SUBSURFACE, SHALLOW SYSTEMS
  • Three most common shallow subsurface systems
  • Leachfields (a.k.a. Leaching Chambers)
  • Mound Systems
  • Seepage Pits

9
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
10
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
  • Used to dispose of previously treated effluents
    (usually originally treated by means of septic
    tank)

11
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
  • Usually set of leaching chambers in trenches
  • Connected to primary treatment system by a pipe
  • Effluent is distributed into the soil

12
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
13
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
  • ADVANTAGES
  • Easy and economic to construct
  • Soil in trenches not likely to be compacted
  • Extended useful life low intrusion on soil and
    silt
  • Small footprint

14
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
  • DISADVANTAGES
  • Not well suited for soils with high percolation
    rates (e.g. sandy soils)
  • Not well suited for soils with high groundwater
    levels

15
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
Setback distances
16
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
Soil Acceptance Rate
17
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
Preliminary Cost Estimate
18
SUBSURFACE, SHALLOW SYSTEMS LEACHFIELDS
The seat under the old oak tree in a leachfield
at Brookmans Park
19
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
20
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
  • Used to further treat pre-treated effluents
  • Comprised of pressure-dose sand filters that lie
    above the ground
  • Discharge directly to the soil

21
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
22
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
  • Suited for sites with restriction such as
  • Slow or fast permeability
  • Shallow soil cover over creviced or porous
    bedrock
  • Elevated water table

23
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
24
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
25
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
  • ADVANTAGES
  • Accommodate sites that otherwise are not suitable
    for in-ground or at-gate onsite disposal
  • Do not discharge directly to surface water bodies
  • Can be used in most climates
  • Little excavation required

26
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
  • DISADVANTAGES
  • Relatively high construction costs
  • Mound location can affect surface drainage
    pattern
  • Require pumping/siphon systems
  • Aesthetically obtrusive
  • Seepages/Leakages can affect mount integrity

27
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
Criteria for Design
28
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
Cost Estimate for Mound Systems
29
SUBSURFACE, SHALLOW SYSTEMS MOUND SYSTEM
Picture of a typical on-site mound system 
30
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
31
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
  • Used for disposal of treated wastewater effluents
  • Brick, block, or precast chambers placed in deep
    excavations surrounded by gravel of crushed rocks
  • Effluents enter the chamber where its contained
    until it seeps through the walls and goes into
    the excavation wall

32
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
33
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
  • ADVANTAGES
  • Easy to construct
  • Requires little maintenance
  • Able to treat on sites with inadequate land
    resources for a standard absorption field

34
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
  • DISADVANTAGES
  • Danger of groundwater contamination
  • Effluent is concentrated at one point, rather
    than large area
  • Small flow able to be treated

35
SUBSURFACE, SHALLOW SYSTEMS SEEPAGE PITS
36
LAND DISPOSAL SYSTEMS
37
LAND DISPOSAL SYSTEMS
  • Used to dispose of pretreated municipal effluents
  • Not widely used due to large land requirements,
    exacerbated by code-required setbacks (often
    including buffer areas and fencing)
  • Also used less frequently due to requirement of
    significant pretreatment before application

38
LAND DISPOSAL SYSTEMS
  • Three main land disposal systems used for
    pretreated municipal effluents
  • Slow-Rate Systems (SR)
  • Rapid Infiltration Systems (RI)
  • Overland Flow (OF)

39
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
40
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • The oldest and most widely used form of land
    treatment, requires largest land area compared to
    the other land disposal systems
  • Used to further treat wastewater effluent via
    contact with the soil-vegetation system
  • Used when stringent requirements are placed on
    nutrients, pathogens, metals, and organics
  • Used in agricultural, turf (e.g., golf courses,
    parks), and forest systems

41
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • SR type 1- chosen to maximize amount of water to
    the minimum area of land
  • SR type 2- chosen to optimize hydraulic loading
    for irrigation purposes

42
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS Type 1
  • Intended for wastewater treatment and hydraulic
    loading
  • Limited by the hydraulic capacity of soil
    (nitrogen removal ability, etc.)
  • Vegetation covers usually include perennial
    grasses due to the high nitrogen uptake ability,
    long WW application season, and low maintenance

43
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS Type 2
  • Primarily intended for providing water and
    nutrients to agricultural, turf, and forest
    system
  • Can not be applied to products consumed by humans

44
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS Type 2
Treatment Plant and Golf Coarse
45
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
Slow Rate Spray Irrigation
46
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
Harvesting Forage
47
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
Spray Irrigation in Forest
48
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
Drip Irrigation
49
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
50
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • Organics are removed mainly within the first 1 to
    2 cm by biological oxidation, filtration, and
    adsorption
  • OXIDATION e.g.
  • Organic matter O2 bacteria -----gt new cells
    CO2 NO3- H2O

51
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
52
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • Particulate material is filtered through the soil
    matrix

53
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • Nitrogen is removed by
  • Vegetation uptake
  • Biological denitrification
  • Ammonia volatilization
  • Retention within soil matrix

54
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
55
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • Phosphorus removal via crop uptake and fixation
    processes in the soil matrix.

56
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
  • SR Systems are very effective at removing harmful
    wastewater constituents

57
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
ADVANTAGES Significantly reduced operational,
labor, chemical, and energy requirements compared
to conventional wastewater treatment systems.
Economic return from the use and re-use of water
and nutrients to provide marketable crops.
Little or no disposal of effluent production.
Recycling and reuse of water reduces water
distribution and treatment costs for crop
irrigation.
58
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
DISADVANTAGES Large land requirements Specific
problems associated with poor site selection
include Soil structure dispersion resulting
from high dissolved salts concentration. Runoff
and erosion for sites with steep slopes or lack
of adequate erosion protection. Inadequate soil
or groundwater characterization resulting in
operational hydraulic problems.
59
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
General design parameters for SR system
60
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
Flowchart For The Design Of A Slow Rate System
61
LAND DISPOSAL SYSTEMS SLOW-RATE SYSTEMS
A preliminary estimate of costs for planning
purposes
62
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
63
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Usually used for
  • Ground water recharge
  • Surface water recharge
  • Recovery of renovated water (by wells or
    underdrains) for reuse
  • Temporary storage of treated waters

64
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Wastewater percolates through the soil and is
    treated through downward flow
  • Vegetation is NOT a part of the treatment

65
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
Hydraulic pathways for RI systems
66
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Most RI failures are due to improper soil
    elevations.
  • Soil depth, soil permeability, and depth to
    groundwater are the most important factors in
    site evaluation.

67
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Removal rates are dependent on
  • Wastewater characteristics
  • Soil characteristics
  • Travel distance
  • Climatic and seasonal variables

68
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • BOD, Suspended Solids, and Fecal Coliforms are
    almost completely removed
  • Nitrogen removal is about 50-99
  • Phosphorus removal is about 70-99

69
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Advantages
  • Gravity distribution methods consume no energy.
  • No chemicals are required.
  • RI is a simple and economical treatment.
  • The process is not constrained by seasonal
    changes.
  • Effluent is of excellent quality.

70
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Advantages

The process is very reliable with sufficient
resting periods. The process is suitable for
small plants where operator expertise is
limited. RI provides a means for groundwater
recharge, controlling
groundwater levels, recovering renovated water
for reuse or discharge to a particular surface
water body, and temporary storage of renovated
water in the aquifer.
71
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Disadvantages
  • Usually wont meet nitrogen levels required for
    drinking water aquifer discharge.
  • Requires long term commitment of significant land
    area
  • Requires annual removal of accumulated deposits
    of organic matter
  • May require occasional removal and disposal of
    the top few inches of soil
  • Clogging can occur when influent is received at
    high application rates from algal laden lagoons
    and ponds

72
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
  • Flowchart For The Design Of A Rapid Infiltration
    System

73
LAND DISPOSAL SYSTEMS RAPID INFILTRATION
Estimating Costs for Rapid Infiltration
Systems (OM includes the annual tillage of
infiltration surfaces, and the repair of dikes,
fences, and roads every 10 years.)
74
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
75
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Used to achieve secondary treatment effluent
    quality when applying effluents comming from
    primary treatment facilities.
  • High removal of Nitrogen, BOD, and Suspended
    Solids

76
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Applying of previously treated wastewater
    effluents to a vegetation-covered, graded land
  • Applied via grated pipes or nozzles at top of
    slope or by sprinkler systems within the site

77
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
78
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Best suited for sites with relatively impermeable
    soils

79
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Land Requirements
  • Low permeability soils
  • Grading within 2-8

80
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Perennial grasses used for
  • Erosion control
  • Slope stability
  • Effluent treatment

81
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Removal mechanisms for BOD and Suspended Solids
  • Biological Oxidation
  • Sedimentation
  • Filtration

82
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Removal mechanisms for Nitrogen (typically
    removes 75-90)
  • Plant uptake
  • Denitrification
  • Ammonia Volatilization

83
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Removal mechanisms for Phosphorus (typically
    removes 50-70- can increase by addition of alum
    of ferric chloride prior to land application)
  • Fixation processes in the soil matrix
  • Crop uptake

84
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Effluent is collected in ditches and can be
    reused or discharged to a surface water body
  • If discharged to surface body NPDES permit
    required

85
LAND DISPOSAL SYSTEMS OVERLAND FLOW SYSTEMS
  • Flowchart For the Design Of Overland Flow Systems

86
LAND DISPOSAL SYSTEMS COMPARISON
87
LAND DISPOSAL SYSTEMS COMPARISON
  • Desirable characteristics, not rigorous standards

88
LAND DISPOSAL SYSTEMS COMPARISON
  • Terrestrial treatment units, design features, and
    performance (Reed et al, 1995)

89
LAND DISPOSAL SYSTEMS COMPARISON
  • Expected water quality function of hydraulic
    loading, available soils for treatments,
    vegetation.

90
LAND APPLICATION SYSTEMS
91
LAND APPLICATION SYSTEMS
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