Bunny
Run Web Site Note: The following document was prepared by a resident
of the Austin City Park Neighborhood, which is across Lake Austin from
Bunny Run. If you're outside that neighborhood, ignore the few specific
references to ACPNA, and this document provides an excellent explanation
of the proposed OSSF ordinance.
SUMMARY OF PROPOSED SEPTIC
ORDINANCE
Disclaimer:
This summary was prepared by Marceline Lasater, a Board member of ACPNA,
as a community service purely for the purpose of informing members of the
issues presented to this neighborhood by the proposed OSSF ordinance. No
reader should rely on any representations in the summary for anything other
than direction to the subjects addressed by the ordinance. If you have
questions pertaining to your own property rights that may be affected by
the proposed ordinance, you must retain your own personal lawyer for his/her
advice to determine to what extent the proposed ordinance affects your
property rights. Many hours have been spent preparing this summary, and
errors, while unintentional, are certainly possible.
Background:
Effective in February 1997, Texas Natural
Resource Conservation Commission (TNRCC, a State agency), promulgated a
set of comprehensive rules governing the permitting, operation and construction
of OSSFs (on site sewage facilities) across the State. TNRCC rules
allow approved municipalities to act as agents in implementing its rules.
In 1999, the City of Austin passed a simply
worded ordinance that adopted all the TNRCC rules regarding OSSFs, as well
as provisions of the Texas Health and Safety Code. See City Ordinance 990211-E;
Land Development Code 12-4-3; TNRCC rules, Texas Administrative Code, Title
30, Chapter 285; and Texas Health and Safety Code, Chapter 366. WWW links
for each authority are provided for your convenience at the end of this
summary.
This year, the City of Austin is attempting
to pass an ordinance that adopts TNRCC’s new standards as well as "more
stringent standards" than those set by TNRCC and the Health and Safety
Code. The City maintains that these "more stringent standards" were actually
in effect from 1988 through 1999, and possibly as early as 1972. The proposed
ordinance currently stands at 44 pages; the TNRCC rules and Health and
Safety Code provisions are equally voluminous.
The proposed City ordinance has been reviewed
by various agencies, and is presently under active review by Water/Wastewater,
in preparation for being submitted to TNRCC for approval (and to justify
the different standards) – prior to the City Council voting on the ordinance.
It is possible that the City Council will vote to approve a draft on August
3 for the purpose of sending it to TNRCC for approval, regardless of amendments
recommended by Water/Wastewater. If approved at TNRCC, the City Council
will vote on it as an ordinance.
The purpose of this summary is:
-
to outline TNRCC regulations currently in effect
(especially as they affect characteristics unique to our lakeside neighborhood)
and
-
to outline the proposed new ordinance, including
the aspects that are expected to directly affect our neighborhood; and
-
to allow you to evaluate the probable repercussions
to your own property before the ordinance goes into effect.
Concerns
"When a new permit is required, the system
must meet the requirements of the current rules." (TNRCC bulletin dated
9-13-99)
"Current rules" includes new separation distances
(from the lake, foundation, property line, and "other structures,") larger
lot size, and greater soil depth, among many other things. TNRCC separation/setback
requirements are attached at the end of this summary for your convenience.
According to a TNRCC bulletin, if your
system "fails" and/or is found to "pollute," your system is presently required
to satisfy current TNRCC rules. If the ordinance passes, it is anticipated
that your system will be required to also satisfy the "more stringent"
requirements of the ordinance as well.
Some existing, built-out lots may not be capable
of satisfying the new standards, due to proximity to the lake, bluffs,
rocky soil, small lot size, etc. :
"There may be lots which cannot have new
or remodeled on-site sewage facilities installed on them because they lack
the space to install it. . . . If space is not available on adjacent land,
the owner may have real difficulty. The property would not be "condemned"
but may be unusable until sewer is available. . . . Under the State rules
we cannot let people install or remodel a facility that is not sized according
to the rules – not even by variance."
from M.B. Lockhart, author/defender/proponent
of the proposed ordinance, by email 6/26/00.
Therefore, as you read through this summary,
look for applications to your property and your system TO SEE WHICH, IF
ANY, ALTERNATE SYSTEM WILL FIT ON YOUR PROPERTY IF YOUR SYSTEM SHOULD FAIL.
Other Concerns
Many citizens have objected to the vagueness
of the standards regarding inspections, "pollution" and "failure" and have
asked that standards be specific and objective (not susceptible to subjective
interpretation by an inspector).
There is grave concern that potentially expensive
decisions could be made by inexperienced and/or incompetent inspectors,
allowing the OSSF owner no recourse or appeal of those decisions
prior to incurring expense and/or being prohibited from using a system.
FIRST YEAR: POTENTIAL EXPENSE TO OSSF OWNERS
Even if you believe your system is functioning
well, the proposed City ordinance authorizes the City to do the following
in the first year the ordinance is in effect:
-
annual inspection (especially lakeside OSSFs;
others every 3 years)
-
fee for license to operate (annual for lakeside)
-
homeowner to dig up all components if installation/engineering
plans are not available to the inspector
-
homeowner to pump out system (for inspection
and maintenance)
-
if requested, to fill with water; recheck in
24 hours for rate of flow/leaks
-
annual pump-out required for some systems
-
maintenance contracts required for some systems
-
if "pollution" found, only "emergency repairs"
are allowed
-
if certain components are involved, an authorization
to construct a new or remodeled system is required (no "emergency repairs"
allowed)
-
If Authorization to Construct is required:
-
new plans must be drawn by registered engineer
or sanitarian
-
apply for variance, if needed
-
fee for construction permit
-
additional inspections during construction
-
sworn (?) declarations by engineer and installer
must be filed before a new permit will be issued
-
new or remodeled system on an existing built-out
lot must meet current standards including increased lot size, separation
distances, soil quality and depth
-
if the lot cannot meet standards, homeowner
may be required to purchase nearby land for OSSF, including a cluster system
-
OSSF owners must file an affidavit with deed
records indicating that an OSSF exists on the property, requiring periodic
inspection and permitting
-
If your system is found to "pollute" during this
process, you may be prohibited from using your system; fines for violations
may be up to $2000 per day per violation
-
No pit privies allowed in the interim, or at
any time
Types of Systems
As you read this summary, it will help to
know what kind of system you have. If you don’t know and don’t have the
installation plans, the ordinance requires you to expose your system (and
its components) so that a diagram of it can be made and filed with your
records in the first year.
Each of the following terms is used throughout
the ordinance (as well as the TNRCC regs) and each kind of system has varying
requirements for construction and/or inspection.
-
Sewage Treatment System
-
"Standard"
-
septic tank (gravity flow)
-
intermittent sand filter
-
"Proprietary" (all or part of the system is owned
by a person and has a trademark or patent)
-
Sewage Disposal System
-
Standard
-
absorptive drainfield
-
evapotraspirative drainfield
-
pumped effluent drainfield
-
Proprietary
-
gravel-less drainfield piping
-
leaching chambers
-
drip irrigation
-
Non-standard disposal process:
-
low pressure dosed drainfield
-
surface irrigation system
-
mound system
-
soil substitution drainfield
-
drainfields following approved aerobic units,
secondary treatment and disinfection
-
All others: "non-standard"
Summary of TNRCC’s Rules:
285.3 General Requirements
All aspects of planning, installation, construction,
alteration,
extension, repair, operation and maintenance
of OSSFs must be in accordance
with this chapter.
Requests for variances must demonstrate
equivalent protection of the public health and environment by alternate
means proposed. Variance requests must be accompanied by planning materials
prepared and sealed by either a registered sanitarian or registered professional
engineer.
285.4 Facility Planning
This section purports to govern planning
prior to subdivision approval.
[Some lots in ACPNA were never subdivided;
however, "subdivision" is defined as a "division of a tract of property
into two or more parts either by platting or field notes with metes and
bounds and transferred by deed or contract for deed. 285.2(71) According
to M.B. Lockhart, a paid City consultant on this ordinance, developed "illegal"
lots will not be subject to the requirements of this section, unless or
until they subdivide.]
For subdivisions on public water supply (platted
or created after 1-1-88):
Lot size: .5 acre minimum
Site specific sewage disposal plan submitted
by registered professional (engineer or sanitarian) and approved by permitting
authority
Location: in accordance withseparation distances
table http://info.sos.state.tx.us/figures/fids/30_0285_0091-10.html
Area available: two times the design area, minimum
For subdivisions served by individual water supply:
Sanitary easement: 100’ radius around well; no
subsurface sewage system
Lot size: 1 acre
Area available: two times the design area, minimum
Existing lots or tracts: if subdivided
prior to 1-1-88 and not conforming to minimum lot size requirements, may
be approved for OSSF if
-
minimum separations distances are maintained
(see Separation
Table) and
-
the site has been evaluated in accordance with
285.30
285.30 Site Evaluation Requirements:
-
Soil analysis: at least 2 soil borings to depth
of 2 feet below proposed excavation. Size and type of OSSF to be determined
on basis of most restrictive soil class.
-
Soil Texture analysis:
Ia – sandy with more than 30% gravel – unsuitable
IV – unsuitable
-
Soil structure analysis (Ib or II soils are suitable
as to structure)
-
Soil depth – suitable soils shall be at least
24 inches below bottom of proposed disposal area for standard ground absorption
systems; otherwise, unsuitable.
-
Restrictive horizons evaluation – unsuitable
if found less than 24" below bottom of proposed drainfield
-
Groundwater evaluation: unsuitable if high water
tables within 24" of bottom of proposed drainfield
-
Topography: uniform slopes under 30% -- suitable
-
Flood hazard: no new OSSFs or substantial improvements
to existing OSSFs shall be allowed in the regulated floodway (see
FEMA maps). Any sites within the 100 year floodplain shall be subject
to special planning requirements.
-
Over-all site suitability:
If suitable soils, calculate size of system
according to 285.91(Table 5).
For unsuitable sites, proprietary or non-standard
systems must be used.
285.31 Setback and Separation
Requirements
Construction of OSSFs must be isolated from
water wells, lakes, roads and other objects subject to contamination.
See Separation
Table. Other objects includes streams, ponds, lakes, rivers, foundations,
buildings, surface improvements, property lines, easements, swimming pools,
"other structures," sharp slopes, and breaks.
285.32 Criteria for Sewage
Treatment Systems
Treatment Processes
-
septic tanks (gravity flow): liquid depth
shall not be less than 30 inches
-
flowline of the inlet device shall be at least
3: higher than the flowline of the outlet device. Entry point of outlet
device shall be below the liquid level of the tank between 25-50% of the
liquid depth of the tank. All outlet devices must use a T branch fitting;
installed water tight; minimum of 3" diameter.
-
All septic tanks shall be divided into 2 or 3
compartments by use of baffles or connecting tanks (with specifications
as to volume, size, etc.)
-
All septic tanks shall have an inspection and/or
cleanout port on the tank top; opening not less than 12 ", but large enough
to provide maintenance and equipment removal. If tank buried more than
12" below ground, shall have risers over port openings (to be sealed and
capped).
-
Construction materials: steel-reinforced poured
concrete or pre-cast concrete, fiberglass, reinforced plastic polyethylene.
Specifications are given. Metal tanks are prohibited.
-
Installation:
-
provide 12" drop from bottom of outlet pipe to
bottom of disposal area
-
4" of sand, loam or pea gravel under and around
tanks
-
tanks to be left open until inspected.
-
Back-fill with sand, loam or pea gravel (free
of rock)
-
Pretreatment tanks – may be required with aerobic
treatment units.
-
Intermittent Sand filters
-
sand media specifications given
-
loading rate: no more than 1.2 gal/day/sq.ft.
-
surface area – specifications given
-
depth – min. 24" of sand media
-
filter bed containment – specifications given
-
underdrains – specifications given
-
Proprietary Treatment Processes: maintenance
contracts required; many specifications regarding electrical wiring,
approval, testing, permits, reports, monitoring period, etc.
-
Nonstandard (all others) -- to be submitted
for review by registered engineer or registered sanitarian. Permit upon
approval by permitting authority.
285.33 Criteria for Sewage Disposal
Systems
Standard – effluent from treatment
process dispersed to adjacent soil (absorptive) or into air (evaporation
and transpiration)
-
Absorptive drainfield – excavation in suitable
soils up to 3 feet; surface scarified; bottom no less than 18" wide; level
to 1" over each 25’ of excavation. Lots of specifications given.
-
Evapotranspirative drainfield – for soils classified
as "unsuitable"
(many specifications given)
-
Pumped effluent drainfield – must use low pressure
dosed drainfield specifications (1000 linear feet of perforated drain pipe
for 2BR; 400’ for each additional BR); trenches 6" wide; 3’ separation
between trenches; 2’ separation from bottom of excavation to restrictive
horizon or ground water; may not use when slopes are greater than 2.0%;
and more specifications given
Proprietary (specifications given for
each):
-
Gravel-less drainfield piping
-
Leaching chambers
-
Drip irrigation -- maintenance contracts
required for all emitter systems
Non-standard – may be reviewed "at the
option" of permitting authority; specifications given for each:
-
Low pressure dosed drainfield
-
Surface irrigation systems
-
Mound systems
-
Soil substitution drainfields
-
Drainfields following approved aerobic units,
secondary treatment and disinfection
285.34 Other requirements
-
construction of plumbing to septic tank: materials
(iron, dustile iron, PVC); slope shall be no less than 1/8" fall per foot
of pipe; two-way cleanout plug between building and septic tank; additional
cleanout plug every 50’; min. inside diameter of 3"
-
pump tanks may be necessary when tank outlet
is lower than disposal field; construction criteria given
-
Grease interceptors – for discharge of large
amounts of greases and oils to OSSFs
-
holding tanks – where no other methods of sewage
disposal are feasible; specs given; must have scheduled pumping contract
285.35 Emergency Repairs
Repairs may be made to abate an immediate,
serious and dangerous health hazard, if it does not alter the system’s
planning materials and functions. Emergency repairs includes such items
as replacing tank lids, inlet and outlet devices, and repair of solid lines.
Written notice must be given to the
permitting authority (city) within 72 hours of the repair, with
a detailed description of methods and materials used in the repair.
Inspection by permitting authority may be required.
[Comment: This is the only kind of repair
explicitly authorized in the TNRCC rules. Presumably, one could repair
and/or maintain one’s system before "failure" without having to report
it.]
285.39 Maintenance and Management
Practices
(Pointers on "How to Love and Care for your
OSSF")
285.70 Agency Enforcement of
OSSFs
-
the executive director may investigate any matter
concerning OSSFs and take appropriate enforcement action.
-
If the executive director determines that an
OSSF is creating a nuisance, the OSSF must be brought into compliance to
abate the nuisance. He may require a property owner to initiate repair
no later than 30 days after notified.
285.80 Treatment and Disposal
of Greywater
Modification associated with a structure must
be carried out in accordance with requirements of State Board of Plumbing
Examiners; outside a structure, must be carried out in accordance with
provisions of this chapter.
Comments: The TNRCC separation distance
required for lakeside OSSF owners is 50’ for sewage treatment
tanks or holding tanks; 75’ for soil absorption systems; 50’
for lined evapotranspiration systems, etc. Now compare the requirements
of the City’s proposed ordinance, noting especially the DWPZ distances
and references peppered throughout.
Critical Water Quality Zones (CWQZs)
and Drinking Water Protection Zones (DWPZs) in watershed areas are
defined and regulated in the Land Development Code (LDC). Familiarity
with these terms and concepts may be useful in understanding the ordinance:
DWPZ is defined in LDC at 25-1-21(30)
as "areas within the Barton Springs Zone, the Barton Creek watershed, all
water supply rural watersheds, and all water supply suburban watersheds,
as described in Section 25-8-2 (Descriptions Of Regulated Areas), that
are in the planning jurisdiction." This term is used throughout the ordinance;
within the DWPZ, more stringent standards are required by the ordinance.
CWQZ: Generally, for a major waterway,
the boundaries of the critical water quality zone are located not less
than 200 feet and not more than 400 feet from the centerline of the waterway.
For a minor waterway, the boundaries of the critical water quality zone
are located not less than 50 feet and not more than 100 feet from the centerline
of the waterway.
For Lake Austin, the shoreline boundary
of the CWQZ (Critical Water Quality Zone) is the 492.8 foot
contour. LDC 25-8-92(B)(1)(b). The width of a critical water quality zone,
measured horizontally inland, is appears to be an additional 75 feet for
a detached single-family residential use, and 100 feet, otherwise, except
that a CWQZ does not extend beyond the crest of a bluff.
Note: The term CWQZ is not used in the proposed
ordinance; however, the distances for CWQZ appear to be used, without
the bluff exceptions.
Summary of Proposed Ordinance
Provisions
Jurisdiction/Applicability:
-
all properties within the full purpose
limits of the City of Austin, TX 78730
-
existing or proposed OSSFs within the limited
purpose boundaries, "where the area has been annexed for the purpose
of applying the City’s health and safety ordinances"
Full purpose boundaries ("city limits"):
in ACPNA, anything below the 504.9 contour (annexed many years ago, perhaps
as early as 1928).
Limited purpose boundaries (LPA):
All territory within 500’ of the 504’9 contour surrounding Lake Austin
was annexed for limited purposes of "planning and zoning" and "sanitation
and health protection" in 1982, citing an emergency concerning the "safe,
orderly and healthful growth and development of the City. . . . to assure
the immediate preservation of the public peace, health, safety and general
welfare both of the public residing within the City and the public residing
adjacent to the City."
This ordinance does not purport to regulate
areas lying in the ETJ (extra-territorial jurisdiction), although
apparently a municipality has the authority to do so. The ETJ is governed
by the TNRCC rules. If you have questions about whether your property
lies outside the LPA, please refer to the jurisdictional maps provided
at Bunny Run’s website, referenced at the end of this summary.
-
More stringent regulations are proposed for OSSFs
in the DWPZ (Drinking Water Protection Zone). See comments above
Comments:
As you read the following summary of the proposed
ordinance, keep in mind that "failure" of an OSSF is not defined anywhere
in the ordinance, but seems to be inherent in the definitions of pollution
and/or nuisance and/or hazard to public health. TNRCC defines nuisance
as:
sewage, human excreta, or other organic waste discharged or exposed in
a manner that makes it a potential instrument or medium in the transmission
of disease to or between persons; or an overflowing septic tank
or similar device, including surface discharge from or groundwater
contamination by a component of an OSSF, or a blatant discharge from
an OSSF.
Also, if you feel inclined to skip the sections
regarding "construction," please reconsider, as it appears that construction
provisions will apply to systems that fail and/or do not qualify for emergency
repairs.
That is the most dangerous part of this ordinance
in my estimation, because some of the developed lots in our neighborhood
cannot qualify under the new construction provisions. We have been told
that the TNRCC rules require upgrade to new standards upon failure. That
is not explicit in the language of the proposed ordinance, as the TNRCC
rules are simply adopted and incorporated by reference.
"Greywater" is not specifically addressed
in the proposed ordinance; however, it is specifically addressed in the
TNRCC rules and may well be included in the annual inspections required
by this proposed ordinance.
The following is a section by section summary
of the proposed ordinance. For a comprehensive understanding of the ordinance,
you must read the actual document, as well as the relevant authorities
incorporated by reference. Links to all relevant authorities are appended
to this summary.
Summary of provisions:
-
An owner must hold a permit to construct,
alter,
repair,
extend
or operate an OSSF.
-
An owner of an OSSF within 200 feet (measured
horizontally) of the 492.8 contour (CWQZ shoreline boundary of Lake Austin)
must obtain a license to operate annually. An annual license is also required
for facilities that use (1) holding tanks, (2) disinfection, or (3) surface
irrigation. Other OSSF owners have up to 5 years to obtain each such license.
-
If the permitting authority (City) determines
that the age, type, condition or location of the facility presents
a risk to public health, they may require a new license to operate sooner
than otherwise required. If you have a proprietary or non-standard treatment
method, the permitting authority may specify the expiration date of the
license.
-
Owners of OSSFs shall notify prospective buyers
and shall file an affidavit in the deed records stating that the
property is served by an OSSF.
-
Authorizations to Construct:
-
A building permit may not be issued unless an
authorization to construct an OSSF has been applied for (or has been found
not to be required). Certificates of occupancy may not be issued unless
the license to operate an OSSF has been issued.
-
If remodeling or alteration of an OSSF
involves a modification or if it takes place on or over a component of
the OSSF, the owner must apply for an authorization to construct (which
expires one year after application)
-
Before issuing Authorization to Construct, but
within 30 days of application, the City shall conduct preliminary site
inspection including topography, geology, and hydrology, to confirm the
submitted site evaluation and shall make a finding regarding whether construction
may begin.
-
If denied Authorization to Construct, notice
shall be given.
-
A person may not install or cover an OSSF until
inspections have been made and approval obtained for each particular stage
of installation, construction or modification.
-
Upon completion of construction or modification,
the engineer or sanitarian must certify that the facility was inspected
and installed as designed, and must provide an accurate set of as-built
plans and specs to the City. The installer must also certify installation
according to plans.
-
The City must find that the facility is in compliance
and that the facility will not cause pollution, injury to the public health,
or nuisance conditions; only then may a license to operate be issued.
-
Licenses to operate for existing OSSFs
may be issued if:
-
the OSSF is in compliance with this chapter (the
whole ordinance)
-
the use of the OSSF will not cause pollution,
injury to public health, or nuisance conditions AND
-
At the time of construction, it was approved
by the regulating agency, OR
-
Inspection shows it to have functional treatment
and disposal units.
-
City may require the owner to uncover all or
part of the facility if
-
no accurate as-built diagram of the facility
is on file or
-
for an inspection
-
If license to operate is denied, the owner shall
be notified in writing of the reasons the permit is denied or revoked.
-
Variances may be requested of the City in writing,
demonstrating that proposed methods provide "equivalent protection" to
public health and environment (prepared and sealed by registered sanitarian
or professional engineer).
-
All appeals of City denials and revocations are
made to City Council.
-
Enforcement and Penalties
-
City may periodically inspect to assure compliance.
-
City may require owner to provide professional
reports or testing reports to help determine whether a system is in compliance.
-
City may require uncovering of components.
-
City may enter cease-work orders and bring suit
for injunctive relief
-
City may revoke a permit for failure to comply
-
fines of $2000 per day per offense
-
Definition of offense: "if a person operates
or allows the operation of an OSSF in a manner that causes, or that
may tend to cause, pollution, injury to the public health, or nuisance
conditions."
-
Subdivision planning:
-
a residential site must:
-
provide enough usable land for at least one repair
or replacement of a system
-
ensure that an OSSf is an adequate distance from
another OSSF, steep slope, floodway, and water well
-
meet minimum lot size requirements (if not cluster
or surface irrigation)
-
inside DWPZ, residential, 1 acre per dwelling
-
outside DWPZ, residential, ¾ acre per
dwelling
-
each lot must have area for effluent disposal
that is the greater of
-
7200 square feet per dwelling unit or
-
two times the design area
-
Slope (for effluent disposal) may not
exceed
-
15% for standard or proprietary disposal
(but not drip irrigation or
lined ET)
-
30% for drip, lined ET or non-standard disposal
-
For existing small lots:
-
if subdivided prior to date of ordinance, must
comply with lot size, area, and slope requirements in effect at the time
of preliminary plat filing
-
if plat submission was required but was not made
at time of subdivision, each lot must comply with lot size, area, and slope
requirements in effect at the time of first sale of any lot in the subdivision
-
Submittal requirements/planning materials must
be:
-
prepared and submitted by registered professional
engineer or sanitarian if:
-
low pressure dosing on slope less than 15%
-
lined ET (without leak monitor)
-
iii. non-standard disposal
-
prepared and submitted by a professional engineer
if
-
intermittent sand filtration
-
lined ET with structural stabilization or leak
monitor
-
non-standard treatment process
-
concrete tank, not precast
-
surface irrigation
-
low pressure dosing on slope of 15% or more
-
secondary treatment and disinfection
-
Cluster systems
-
must have management authority
-
may not be located in floodway or 25-year floodplain
-
specific requirements for 100 yr floodplain
-
each owner connected to the system must be party
to the agreement required by TNRCC
-
Maintenance contracts are required for:
-
systems using sand filtration
-
systems using non-standard or proprietary treatment
process
-
Site Evaluation
-
for standard systems (but not sand filtration):
-
soil profile hole excavated with backhoe
-
in DWPZ, each profile hole excavated to four
feet below bottom of proposed excavation
-
outside DWPZ, profile holes to three feet below
-
Percolation testing may be required in the DWPZ
to establish effluent floating rates to the soil (with specific perc test
rates cited)
-
If 36 inches of suitable soil (without
restrictive horizon) is not available below bottom of proposed drainfield,
the site is unsuitable
-
In DWPZ, if high water tables are
within 48 inches below bottom of proposed drainfield, site is unsuitable;
outside
DWPZ, 36 inches
-
Setback and separation requirements
-
soil absorption system or unlined ET bed
-
100’ from water supply lake
-
75’ if low pressure dosing is used
-
50’ if low pressure dosing with secondary treatment
or nitrogen reduction followed by disinfection
-
lined ET bed
-
100’ from water supply lake
-
50’ if leak monitor is used
-
spray irrigation
-
150’ from water supply lake
-
75’ from stream or pond
-
25’ from dwelling
-
10’ from up-slope property line
-
25- from down-slope property line
-
100’ from sharp slope or break
-
Criteria for Sewage Treatment Systems
-
Each inspection/clean-out port must be located
to allow direct surface access to tank components
-
Before being covered, tank shall be tested for
leaks according to manufacturer’s specifications and being filled with
clean water and checked for drop in water level over 24-hour period.
-
Intermittent sand filters – special requirements
(12-4-66)
-
Criteria for Sewage Disposal Systems
-
no chipped tires
-
ET liner material specified (PVC; 30 mils thick),
etc.
-
Pumped effluent - lateral lines range 1.5 to
2.5 feet deep
-
Pumped effluent in DWPZ, specifications for min.
vertical separation, depending on soil type (different outside DWPZ)
-
drip irrigation: various specifications (12-4-68
(B))
-
in DWPZ: 3’ min. vertical distance for standard
treatment
-
but 2’ if secondary treatment; 1’ if secondary,
disinfection and nitrogen (etc. depending on the soil)
-
non-standard disposal:
-
low pressure dosed in DWPZ (depending on soils)
-
4 foot min. vertical distance if standard treatment
-
3 foot min. using secondary treatment
-
2 foot if secondary/disinfection/nitrogen reduction
-
mound disposal (same min. vertical separation
distance as for low pressure dosed)
-
surface irrigation ("cluster"):
-
effluent criteria, pH, fecal coliform, chlorine
biochemical oxygen demand, total suspended solids specifications are given
-
no rock outcroppings
-
piping to be below ground
-
sprinkler application to be controlled by commercial
irrigation timers
-
may be conducted only at night (or just before
sunrise)
-
must have electronic monitoring, automatic notice
of failure
-
must prevent from effluent from crossing property
lines
-
if multi-family, are must have posted warning
signs in English and Spanish
-
surface runoff to be prevented from leaving
-
Connection to Organized Sewage Disposal
System (such as city sewer) is required if sewer comes within 100 feet
of a lot containing an OSSF, and use of OSSF is prohibited (with
some exceptions).
-
Other
-
composting toilets – disposal regulations
-
Abandoned OSSFs: crush or remove lid of tank
and have it inspected
-
For installed OSSF but not to be used immediately,
pump, secure and have it inspected
-
Septic tank must be pumped out at least once
every 3 years.
-
Water softener back flush is not permitted
to enter any part of OSSF
-
Use of explosives to construct/alter/repair/extend
OSSF is prohibited.
Relevant Authorities and Other Commentaries:
-
Health and Safety Code:
Index: http://capitol.tlc.state.tx.us/statutes/hstoc.html
Chapter 366 (On-Site Sewage Disposal Systems):
http://capitol.tlc.state.tx.us/statutes/codes/HS000105.html
-
TNRCC rules, Chapter 285 of Title 30 of the Texas
Administrative
Code:
http://info.sos.state.tx.us/pub/plsql/readtac$ext.ViewTAC?tac_view=4&ti=30&pt=1&ch=285
Relevant sections of Chapter 285:
-
Subchapter D (OSSFs):
http://info.sos.state.tx.us/pub/plsql/readtac$ext.ViewTAC?tac_view=5&ti=30&pt=1&ch=285&sch=D&rl=Y
-
Subchapter I: Appendices/Tables:
http://info.sos.state.tx.us/pub/plsql/readtac$ext.TacPage?sl=R&app=9&p_dir=&p_rloc=&p_tloc=&p_ploc=&pg=1&p_tac=&ti=30&pt=1&ch=285&rl=91
-
Subchapter A: General Provisions:
http://info.sos.state.tx.us/pub/plsql/readtac$ext.ViewTAC?tac_view=5&ti=30&pt=1&ch=285&sch=A&rl=Y
-
Texas Water Code
http://capitol.tlc.state.tx.us/statutes/watoc.html
-
Proposed City ordinance governing OSSFs
http://www.ci.austin.tx.us/news/sewage_ordinance.htm
-
City of Austin Land Development Code
-
Bunny Run Neighborhood website:
http://www.main.org/bunnyrun/
Click on their links for:
-
maps showing
jurisdictional areas,
-
their summaries of the OSSF ordinance, and
-
Ordinance 820506-D (creating limited purpose
annexation areas in 1982)
-
Amstar Engineering website: "Battlefield" (comments
on proposed OSSF ordinance):
http://www.amstarengineeringinc.com/battlefield.htm)
-
City Memo on Recurring Licensing (6-7-00)
http://www.main.org/bunnyrun/ossf/city_licensing.htm