(a) 
The following rules and regulations governing the control of erosion and sedimentation within the jurisdiction of the Town of Double Oak are hereby adopted under the authority of the Constitution of Texas, and pursuant to the general laws of the state.
(b) 
Private property owners, developers, or builders shall be accountable for any erosion of their property or construction site which results in measurable accumulation of sedimentation in dedicated streets and ditches. No person shall allow an accumulation of sedimentation resulting from erosion deeper than one inch in any street, alley or other private property. Any person in violation hereof shall be punished as provided hereinafter.
(c) 
All persons who own, occupy or are in control of real property within the town limits comply with the following standards:
(1) 
Maximum use shall be made of vegetation to minimize soil loss.
(2) 
Natural vegetation should be retained wherever possible.
(3) 
Where inadequate natural vegetation exists, or where it becomes necessary to remove existing natural vegetation, temporary controls must be installed promptly to minimize solid loss and insure that erosion and sedimentation does not occur.
(4) 
An erosion control plan must be submitted to the town for approval by the building inspector or city engineer prior to actual construction. The review and inspection fee as provided for in the fee schedule in the appendix of this code will be due on submission.
(5) 
Wastes or disposal areas and construction should be located and constructed in a manner that will minimize the amount of sediment entering streams and drainage ditches.
(6) 
When work areas or material sources are located in or adjacent to live streams, such area shall be separated from the stream by a dike or other barrier to keep sediment from entering a flowing stream. Care shall be taken during the construction and removal of such barriers to minimize the sediment transport into a stream.
(7) 
Should preventive measures fail to function effectively, the applicant shall act immediately to bring the erosion and/or siltation under control by whatever additional means are necessary.
(8) 
Rainfall and storm water runoff shall be diverted away from construction areas as much as possible.
(9) 
Developers, builders or owners of property shall permanently stabilize all disturbed areas prior to final acceptance of the subdivision, project and/or structure. Stabilization shall be accomplished through the use of perennial vegetative cover or other permanent means, such as channel lining, retaining wall, etc.
(Ordinance 41 adopted 11/16/97)
Permanent erosion controls shall be installed at or near the end of the construction project when no further disturbance of the area will occur. The purpose of these controls is to permanently minimize soil loss by such methods as restoring ground cover, building retaining walls for steep slopes, or reducing wave or water action by lining channels or shorelines with gabions, jute mats, vegetation or similar materials. Examples of typical permanent measures are vegetation cover using perennial plants, headwalls, stilling basins, riprap, tree wells, gabions, matting along channels, retention lakes, terracing and retaining walls.
(Ordinance 41 adopted 11/16/97)
Temporary erosion control methods shall be used to abate sediment runoff from construction sites. The application of control devices can yield significant water quality and drainage benefits at a minimal cost to the developer. The erosion control measures can be grouped as barriers, filter devices or routing devices.
(Ordinance 41 adopted 11/16/97)
(a) 
The erosion control methods classified as acceptable barriers include:
(1) 
Straw bale sediment barrier;
(2) 
Sandbag sediment barrier;
(3) 
Check dam; and
(4) 
Sediment trap.
(b) 
The foregoing measures trap sediment and prevent high runoff velocities which cause erosion. Barrier devices are illustrated in the erosion control barriers figures. The straw bale and the sandbag sediment barriers can reduce sediment loads significantly. A sandbag barrier is more durable and should be used to withstand more intense storm events. Siltation berms and check dams are not as effective for sediment removal as the other types of barriers and operate best in storm events of limited intensity.
(Ordinance 41 adopted 11/16/97)
(a) 
Filtering methods may be used in place of barriers. Filter devices allow runoff to pass through but retain sediment by filtration. The types of acceptable filters available are:
(1) 
Filter berm;
(2) 
Filter fence;
(3) 
Filter inlet; and
(4) 
Vegetation filter strip.
The erosion control filters figures are on file in the office of the city secretary and show typical erosion control filters.
(b) 
Excellent sediment removal can be achieved using a filter berm, fence or inlet. The filter berm is constructed of rock and therefore is capable of withstanding heavier storm events than the filter fence or filter inlet. In general, the vegetation filter strip will operate less effectively than the other devices.
(Ordinance 41 adopted 11/16/97)
(a) 
Only one method, the flexible downdrain, is classified strictly as a routine device. Schematic of a downdrain is shown on file in the office of the city secretary. The purpose of the device is to convey waters down steep slopes or across highly erodible soils.
(b) 
Some of the methods classified under erosion control barriers can be used as routing devices to protect erodible areas. Sandbag sediment barriers and straw bale sediment barriers are both suitable for this purpose.
(c) 
A routing device is an erosion prevention tool that can eliminate erosion problems on steep slopes and other critical areas. It is not deigned to capture any solids already moving with the water.
(Ordinance 41 adopted 11/16/97)
(a) 
Erosion from construction sites can be a significant water quality problem. Developing areas are cleared of vegetation during construction, leaving the soil exposed and susceptible to erosion. Runoff then transports eroded sediment from these areas and deposits it downstream. The accumulation of silt in streams and ponds is a form of water pollution that is unattractive and impedes drainage. No person shall cause, suffer, allow or permit an excessive accumulation of silt, sediment or soil in any stream or pond which originates on property owned or controlled by that person where such accumulation is caused by erosion.
(b) 
Prevention is a key aspect of erosion control. Many of the control methods presented herein can be placed in a manner that will protect highly erodible areas, such as steep slopes. The prevention of erosion requires prior planning to ascertain the placement of selected control methods. The rewards of this planning will be a significant reduction in soil loss. Not only can soil loss be prevented, but eroded soil can be recovered on the construction site and used for fill.
(c) 
The particulate material in construction site runoff is generally heavier and larger than particulate material in urban runoff. These attributes facilitate the removal of the material whether the removal is by settling in a sediment trap or by filtration through a filter fence. Temporary sediment traps, filters and routing devices can effectively control erosion for construction sites if properly applied. These methods are used in an effort to control temporary increases in sediment loads.
(d) 
A quantifiable assessment of performance is difficult because the nature of erosion control is more preventative than corrective. A rough assessment of performance can be conducted by comparing the soil loss from a site with controls to the loss from a comparable site without controls.
(Ordinance 41 adopted 11/16/97)
(a) 
Sediment traps and flexible drains are flow collection devices that will require hydraulic design. An estimate of the peak design flow rate and runoff volume is necessary for proper sizing of these management methods. Runoff volume and peak flow are calculated based on the design storm. Design storms for temporary erosion control structures shall be based on the ten year return frequency.
(b) 
The design storm frequency for construction sites should consider several factors, including:
(1) 
The length of time and size of construction activity;
(2) 
The severity of damage that could result to downstream waters if the design storm is exceeded; and
(3) 
Local concerns toward environmental protection.
(Ordinance 41 adopted 11/16/97)
(a) 
The town shall have a right of entry onto property to conduct such inspections as may be necessary to confirm that proper and effective erosion control measures have been constructed, implemented and installed. It shall be a violation of this article for any person to refuse such entry or to fail to call for such inspection in a timely manner. An inspection fee as set forth in the fee schedule in the appendix of this code shall be paid by the property owner or developer for each lot or tract of real property upon which a structure is to be built prior to the commencement of construction.
(b) 
Should proper erosion controls not be implemented, or should such controls fail or become inoperative, the town shall notify the person, owner, builder or developer of the violation in writing. The person, owner, builder or developer shall begin correcting the problem within five (5) days after delivery of written notice. Should the person, owner, builder or developer fail to commence and implement corrective measures within this five (5) day period, the town may, in addition to any other remedies provided by law, revoke the development permit, building permit, certificate of occupancy or withhold the issuance of any of the foregoing or the issuance of final acceptance.
(c) 
Any person violating any of the provisions of this article shall be deemed guilty of a misdemeanor and upon conviction thereof shall be fined in a sum in accordance with the general penalty provision set forth in Section 1.109 of this code. Each separate offense may be punished separately and each day during which such violation occurs or continues shall be deemed to constitute a separate offense.
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(Ordinance 41 adopted 11/16/97; Ordinance 12-09 adopted 10/15/12)