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HomeMy WebLinkAbout549 Big Dipper Rd - 194134102001 - 194134102002EAGLE C( )NTY DEPARTMENT OF ENV RONM1( 'AL HEALTH �
... ERMIT MUST BE POSTED
ON PROPE iY
Box 811 6th & Broadway PLEBE
CALL FOR FINAL INSPECTION
Eagle, Colorado 81631
D� jasit
/o/��
(this does
PERMITv 3 4
not constitute
•
a building or use permit)
Owner DOUGLAS
TEWS/ROBERT DUERSTEN
DEFENDAPIT'S
;EXHIBIT
System Location LOT 27 - BELLYACHE
RIDGE SUBDIVISION - FILING #2
� �� �
Licensed fbztmft=,Installer: ARNOLD NOTTINGHAM
* Conditional Construction approval is hereby granted for a 1000 gallon . _w
XXX Septic Tank or Aerated treatment unit.
Absorption area (or dispersal area) computed as follows:
Perc rate 1 inches in 30 minutes sq. ft.
absorption area per bedroom
# of bedrooms x sq. ft. minimum requirement
May we suggest
Date July 11, 1979
FINAL APPROVAL OF SYSTEM:
SIZING:' 1000 gallon septic tank foi
ach unit of duple
00 sq. ft. absorption
area per unit @ 300 sq. ft
per bedroom
NOTE: We recommend installing
2 dry wells, each 10'x10'x
10' (one dry well for each
unit, leading from each of
the tanks).
An alternative absorption
Inspecto lief
J Ann ighan leach field of 1200 sq. ft.
combined for both units..
No system shall be deemed to be in compliance with the Sewage Disposal Laws until the assembled system
is approved rior to covering any part.
Septic Tank cleanout to within 12>> of final grade or aerated access ports above grade.
roper materials and assembly. A FINAL INSPECTION of the
system MUST be arranged
Adequate absorption (or dispersal) area. 24 hours before backfillin€
The call for inspection
equate compliance with permit requirements, may be made as installatior
is in progress.
Adequate compliance with County and State regulations/requirements.
Date _1� `� Inspector
JJ
RETAIN WITH RECEIPT RECORDS AT CONSTRUCTIO SI�j
*CONDITIONS:
1. All .installation must comply with all requirements of the County Individual Sewage Disposal Regulations,
adopted pursuant to authority granted in 25-10-104, CRS 1973 amended 25-1-614, CRS 1973
2. This permit is valid only for connection to structures which have fully complied with County Zoning and
building requirements. Connection to or use with any dwelling or structures not approved by the building
and Zoning office shall automatically be a violation of a requirement of the permit and cause for both
legal action and revocation of the permit.
3. Section III, 3.24 requires any person who constructs, alters, or installs an individual sewage disposal
system in a manner which involves a knowing and material variation from the terms or specifications con-
tained in the application of permit commits a Class I, Petty Offense ($500.00 fine - 6 months in jail or
both.
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'PERCOLATION TEST
FEE : $ 50 . G -C /0 K to /Q
Application. No. Permit No.
0►iner: ✓e
Legal Description: ZeZ
Type of Dwelling: �� ���G�G No. of Bedrooms:
Date of Test:
Depth of. Holes:
.Diameter: Type of -Soil:
J,
Location of Test Holes:�_e-�'
Test Holes Presoaked:
Yes: No:
a /1, 3/�
TIME
WATER DEPTH
INCHESOF FALL
RATE
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'ERCOLATf ON RAT Mr'I C (i��/
APPROVED: DISAPPROVED: DATE: (� ,
ENVIRMIL.NTAL' HEALTH OFFICER �.;� 61/UI
600 le - "-e& 16-e�
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EAGLE COUNTY ENVIRONMENTAL HEALTH
ROUTE FORM
T�s .d ee,-,,s��
NAME
DATE REFERRED
APPLICATION NO.
Please review the attached application and return it and this completed form
to the Environmental Health Office.
MR-mo4 mK#
Comments:
_BUILDING•
Other
Comments:
-ENGINEER:
Comments:
Set Backs
Site
Access
Recommend Approval
l_-\_:_/,,_,l
(not always necessary)
Roads
Grading
Drainage
Recommend Approval
1 1)-11-7 9
Jaime and Vicki Brehmer
October 14, 1987
Page Two
If you have any further questions concerning this inspection
or any other matter, please feel free to contact this office.
Sincerely,
Erik Edeen
Environmental Health Officer
Department of Community development
EE/cb
xc: Jan Livergood, Century 21 Realty
Ed Schmidt, Form Mortgage, Inc.
Files
LOAN INSPECTION REQUEST FORM
PROPERTYPARCEL NO: 1,4 C
• •
• •' OW 1
DATE RECEIVED:
COPIES TO:
W VEQ4000 Ce r a Il i 105
EOP-m ev ri Ca �d�3s" �d sc
2Su f 4-c l a7
***********************
r-
ISDS PERMIT NO: NO ISDS RECORD FOUND:
INSPECTION INFORMATION: , 4',pcc ir,5 112,
VISUAL INSPECTION OF PREMISES: GL,,FrSVo
DATE:
NOT FEASIBLE DUE TO WEATHER CONDITIONS:
APPARENTLY FUNCTIONING SATISFACTORILY:
NOT FUNCTIONING OR NOT EXPECTED TO FUNCTION SATISFACTORILY AS
EVIDENCED BY: /L-G �5
LOAN INSPECTION REQUEST FORM
LOCATION:
AQ0 z 7
PARCEL NO:
PROPERTY OWNER: ic
REQUESTOR:
DATE RECEIVED:
COPIES TO:
y (� - l © S!7 EG�c..LS C d
Sr�3�
ISDS PERMIT NO: -7 NO ISDS RECORD FOUND:
INSPECTION INFORMATION:
VISUAL INSPECTION OF PREMISES:
DATE: �" - ,=? /--
NOT FEASIBLE DUE TO WEATHER -CONDITIONS:
APPARENTLY FUNCTIONING SATISFACTORILY: �S
NOT FUNCTIONING OR NOT EXPECTED TO FUNCTION SATISFACTORILY AS
EVIDENCED BY:
F +f: gym,
x
-TOLL FREE NUMBERS:
9f_
Vail - 949-5?_57Basal
DEi'ART� iENT OF
PLANNING & DEVELOPMENT
t - 927-3823
EAGLE, COLORADO 81c)o1
TELEPHONE 303/328-7311
June 25, 1979
BOARD OF COUNTY
COMMIISSIONERS
Ext 241
Rob Duersten/Douglas Tews
ADMINISTRATION
BOX 2442
Ext241
Vail, Co. 81657
ANItv1AL SHELTER
949-4292
RE: Application for Building
Permit in Eagle County
ASSESSOR
Ext202
Lot 27, Bellyache Sub. -
Denied
BUILDING IN
INSPECTION
The Eagle County Building Dept. requires
that applications for Building
Ext 226or229
Permits in Eagle County be routed to
the Eagle County Planning, Engineering,
CLERK &
and Environmental Health Departments
for their comments prior to issuance
RECORDER
of the permits. Your application was
routed on 6/12/79.
Ext
COUNTY
Listed below are the Comments and recomitiendations which were made by the
ATTORNEY
Ext242
above departments during the routing procedure. If you have any questions
or wish to get a further explanation, please contact the appropriate dept.
ENGINEER
Ext 236
PLANNING: Not approved. Show % of slope of lot. Parking must be shown
ENVIRONMENTAL
at 2.5 per unit and 10'X20' outside spaces.
HEALTH
Ext 238
EXTENSION
AGENT
Jim Williams, Zoning Inspector
Ext 247
LIBRARY
ENGINEERING: Not approved. Please show grading and drainage on site
Ext255
plan to allow drainage away from foundation.
PUBLIC HEALTH
Ext
Eagle 252
Vail476-5844
Melton E. Atwell, Co. Engineer
PLANNING
Ext 226or229
HEALTH: Not approved. Septic tank application has not been returned
PURCHASING/to
the Env. Health office and -fees have not bpen paid.
PERSONNEL
Ext 245
�4A
ROAD & BRIDGE
Erik Edeen, Env. Health Officer
Ext 257
SHERIFF
Eagle Ext 211
Basalt 927-3244
Gilman 827-5751
SOCIAL SERVICES
328-6328
It would be to your advantage if you begin to resolve any problems and/or
TREASURER
requirements as soon as ossible so as not to delay the issuance Of your
q p
Ext 201
building permit any longer than necessary.
is
('
Les Douglas
Eagle County Building Official
LD/J k
'
t
f-
cc: Env. Health, Co. Engineer
f
EAGLE COUNTY
Communit Developpment
.Post Office Box 179
EAGLE, COLORADO 81631
TELEPHONE 303/328-7311
BOARD OF COUNTY
November 20, 1979
COMMISSIONERS
Ext241
Robert Duersten
ADMINISTRATION
.z
Douglas Tews
Ext 241
P. 0. Box 2442
ANIMAL SHELTER
Vail, Colorado 81657
949-4292
ASSESSOR
Dear Mr. Duersten and Mr. Tews:
Ext 202
BUILDING IN
The individual sewage disposal systems on the duplex
INSPECTION
lot of Lot 27, Bellyache Ridge Subdivision, Filing #2,
Ext 226or229
were installed according to specifications of this
CLERK &
department. Two 1,000-gallon septic tanks were
RECORDER
( p installed one for each unit of the duplex) and
Ext 217
two 800 sq. ft. leach fields were installed (one for
COUNTY
each unit of the duplex).
ATTORNEY
ATTOR
Ext 242
Final approval was granted for these systems on
ENGINEER
Ext236
October 17, 1979. The systems appear to be.functioning
properly.
ENVIRONMENTAL
HEALTH
Ext238
Potable water is provided by the Bellyache Ridge
Homeowners Association Community Water Supply System,
EXTENSION
AGENT
which is tested and inspected by the Colorado Department
Ext247
of Health. Test results for bacteriological analysis
LIBRARY
can be obtained from Colorado Department of Health;
Ext255
515 Patterson Road; Box 10,000; Grand Junction, CO 81501.
PUBLIC HEALTH
Eagle Ext 252
Vai1476-5844
Sincerely,
c
PLANNING
C���
Ext 226 or 229
PURCHASING/
Erik W. Edeen
PERSONNEL
Eagle County
Ext245
Environmental Health
ROAD & BRIDGE
Ext 257
ncm
SHERIFF
Eagle Ext 211
Basalt 927-3244
Gilman 827-5751
SOCIAL SERVICES
32$-6328
TOAMSURER
Ex) 201
EAGLE COUNTY
551 Broadway
Eagle, Colorado 81631
(303) 328 7311
August 11, 1987
Vicky and Jamie Brehmer
4284 Columbine #8
Vail, Colorado 81657
Dear Vicky and Jamie,
This letter will confirm for you the results of our
dye test on your septic system on July 31, 1987. The dye
did show up in the seepage area at the northeast corner
of the septic drain field. The seepage is most likely
due to a settlement of the ground or a weakness in the
northeast corner of the drain field. Should the repair
work cost over $100.00, a Repair Permit will be necessary.
The simplest solution might be to construct a clay dike.
in the northeast corner and raise the level of the drain
field approximately one foot. Please contact our office
when the repairs have been made or when you need a repair
Permit.
If you have any questions regarding this letter,
please feel free to contact this office.
Sincerely,
Erik Edeen
Environmental Health Officer
EE/cb
xc: Susan Vaughn, Director
Files
Board of County Commissioners Assessor Clerk and Recorder Sheriff Treasurer
P.O. Box 850 P.O. Box 449 P.O. Box 537 P.O. Box 359 P.O. Box 479
Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631
EAGLE COUNTY
551 Broadway
Eagle, Colorado 81631
(303) 328 7311
October 14, 1987
Jaime and Vicki Brehmer
Post Office Box 3663
Vail, Colorado 81658
RE: Water supply and sewage disposal inspection for property
located at: 0459 Big Dipper Road, Wolcott, Colorado
Dear Mr. and Mrs. Brehmer,
All loan inspections are completed under the authority of the
Eagle County Building Resolution, Section 2.09.03, A (7), adopted
by the Eagle County Commissioners on October 8, 1985.
On October 13, 1937, this department conducted a site inspection
of the above referenced property. The inspection was requested by
Jan Livergood of Century 21 Realty in Vail for the purpose of evaluating
the existing condition of the on -site wastewater disposal and water
supply systems.
A review of the County records indicates that the sewage disposal
system was permitted under Permit Number 374, inspected and approved
in accordance with County Individual Sewage Disposal Regulations. A
visual inspection of the ground surface indicated that the sewage
disposal system was apparently functioning satisfactorily at the time
of the inspection. Minor repair of the drain field pipe was completed
on October 9, 1987.
The water supply to this residence is from a community water system
and is tested on a regular basis by the Colorado Department of Health.
The Bellyache Ridae water system test results are available from the
Upper Eagle Valley Consolidated Water and Sanitation District at
846 Forest Road in Vail, Colorado.
Board of County Commissioners Assessor Clerk and Recorder Sheriff Treasurer
P.O. Box 850 P.O. Box 449 P.O. Box 537 P.O. Box 359 P.O. Box 479
Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631
EAGLE COUNTY
551 Broadway
Eagle, Colorado 81631
(303) 328-7311
September 1, 1988
Dr. Larry Brooks
P.O. Box 1050
Edwards, CO 81632
RE: Water supply and sewage disposal inspection for property located at
549 Big Dipper Road _
Dear Dr. Brooks,
All loan inspections are completed under the authority of the Eagle
County Building Resolution, .Section 3.09.03, A (7), adopted by the Eagle
County Commissioners on October 8, 1985.
On August 31, 1988, this department conducted a site inspection of the
above referenced property. The inspectionwas requested by you for the pur-
pose of evaluating the existing condition of the on -site wastewater disposal
and water supply systems.
A review of the County records indicates that the sewage disposal system
was permitted under Permit Number 374, inspected and approved in accordance
with County Individual Sewage Disposal Regulations. A visual inspection of
the ground surface indicated that the sewage disposal system was apparently
functioning satisfactorily at the time of inspection.
The water supply to this residence is from the Bellyache Ridge water
system. An inspection of this source revealed that it was properly con-
structed and located.
If you have any quesitons concerning this inspection, please call
or write.
Respectfully Submitted,
EuX
Erik Edeen
Envirommnetal Health Officer
Community Development
xc: Files
Board of County Commissioners Assessor Clerk and Recorder Sheriff Treasurer
P.O. Box 850 P.O. Box 449 P.O. Box 537 P.O. Box 359 P.O. Box 479
Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631 Eagle, Colorado 81631
COLORADO DEPARTMENT OF HEALTH
ACCOMMODATIONS INSPECTION REPORT
Name �G1/"jiP �"� ��ri C?� Co. ��i�/. Acct. No. Category No.
Location` Gl Zip
Owner c r �' �''� �� Address a� Zip
Operator Address / LS % Zip
Units Capacity Male Female Juv.
Water, Source -Type Sewage, Type -Method Food Source
Swimming Pool (A 0,�— 7 6o —6`60 /
An inspection of the above noted facility on this date reveals the violations and deficiencies
listed below which you are hereby ordered to correct:
)ete Received By Inspected By Score
:PS:57 (5-75-10)
JOB NAME —J
i
i
JOB LOCATION
BILL TO
DATE STARTED
U3 / . Lz r•lg z Bellyache r
Ridge, .0549 Big Dipper Rd, Tau :,�
BASQKS
Parcel # oo�
}
ATE COMPLETED
&
JOB N©.
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GROSS PROFIT
LESS OVERHEAD COSTS
% OF SELLING PRICE
NET PROFIT
.108 FOLDER Product 278 �p NEW ENGLAND BUSINESS SERVICE. INC., GROTON, MA 01471 JOB FOLDER
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INDIVIDUAL SEWAGE DISPOSAL SYSTEM PERMIT
EAGLE COUNTY ENVIRONMENTAL HEALTH DIVISION
P.O. Box 179 500 Broadway • Eagle, Colorado 81631
Telephone:328-8755 YELLOW COPY OF PERMIT MUST BE POSTED AT INSTALLATION SITE. PERMIT NO. 1511
Please call for final inspection before covering any portion of installed system.
OWNER: Richard Ranieri PHONE: (516) 928-4156
MAILINGADDRESS: 123 Mt. Sinai Ave. City: Mt. Sinai State: NY zip: 11766
APPLICANT: Richard Ranieri PHONE: Same
SYSTEMLOCATION: 549 Big Dipper Rd, Bellyache Ridr WARCELNUMBER: 1941-341-01-004
LICENSED INSTALLER: Long' S Excavation LICENSE NO: 42-95
DESIGN ENGINEER OF SYSTEM: Hank Danley/ White Water Systems
INSTALLATION HEREBY GRANTED FOR THE FOLLOWING:
980 _GALLON ✓ 6W40TANK* White Water Aerobic Treatment, plus 500 gallon dosing tank
ABSORPTION AREA REQUIREMENTS:
800 SQUARE FEET OFBEEPACI&M -sammE-FEET-amEI PrffmTm. absorption area via drip irrigation
SPECIAL REQUIREMENTS: 1• Field verify 4' separation to bedrock, 2.Representative of Summit Sewers,
Inc. must be present during installation, 3.Submit maintenance agreement to Eagle County
Environmental Health upon,,:e s 4.Install as per engineer's design.
ENVIRONMENTAL HEALTH APPROVAL: DATE: August 16, 1995
CONDITIONS:
1. ALL INSTALLATIONS MUST COMPLY WITH ALL REQUIREMEN OF THE AGLE COUNTY INDIVIDUAL SEWAGE DISPOSAL SYSTEM REGULATIONS, ADOPTED PURSUANT
TO AUTHORITY GRANTED IN 25- 10. 104. 1973, AS AMENDED.
2. THIS PERMIT IS VALID ONLY FOR CONNECTION TO STRUCTURES WHICH HAVE FULLY COMPLIED WITH COUNTY ZONING AND BUILDING REQUIREMENTS. CONNECTION
TO OR USE WITH ANY DWELLING OR STRUCTURE NOT APPROVED BY THE ZONING AND BUILDING DEPARTMENTS SHALL AUTOMATICALLY BE A VIOLATION OF A
REQUIREMENT OF THE PERMIT AND CAUSE FOR BOTH LEGAL ACTION AND REVOCATION OF THE PERMIT.
3. CHAPTER IV, SECTION 4.03.29 REQUIRES ANY PERSON WHO CONSTRUCTS, ALTERS OR INSTALLS AN INDIVIDUAL SEWAGE DISPOSAL SYSTEM TO BE LICENSED.
FINAL APPROVAL OF SYSTEM: (TO BE COMPLETED BY INSPECTOR):
NO SYSTEM SHALL BE DEEMED TO BE IN COMPLIANCE WITH THE EAGLE COUNTY INDIVIDUAL SEWAGE DISPOSAL SYSTEM REGULATIONS UNTIL THE SYSTEM IS APPROVED
PRIOR TO COVERING ANY PORTION OF THE SYSTEM.
INSTALLED ABSORPTION OR DISPERSAL AREA: SQUARE FEET.
INSTALLED SEPTIC TANK: GALLON DEGREES FEET FROM
SEPTIC TANK ACCESS TO WITHIN 8" OF FINAL GRADE AND
PROPER MATERIAL AND ASSEMBLY YES _NO
COMPLIANCE WITH COUNTY / STATE REQUIREMENTS: YES —NO
ANY ITEM CHECKED NO REQUIRES CORRECTION BEFORE FINAL APPROVAL OF SYSTEM IS MADE. ARRANGE A RE -INSPECTION WHEN WORK IS CORRECTED.
COMMENTS:
ENVIRONMENTAL HEALTH APPROVAL: DATE:
ENVIRONMENTAL HEALTH APPROVAL: DATE:
(RE -INSPECTION IF NECESSARY)
RETAIN WITH RECEIPT RECORDS
APPLICANT / AGENT:
PERMIT
PERCOLATION TEST FEE
OWNER:
RECEIPT #
CHECK#
InL:omplete Applications Will NOT Be Accep � �.
(Site Plan MUST be attached) ---
ISDS Permit ,
PENDHIBITANTS Building Permit X
EX
SlAq: APPLICATION FOR INDIVIDUAL SEWAGE DISPOSAL SYSTEM PERMIT
ENVIRONMENTAL HEALTH OFFICE.- EAGLE COUNTY
P. O. BOX 179
EAGLE, CO 81631
328-8755/927-3823 (Basalt)
**************************************************************************
* PERMIT APPLICATION FEE $150,00 PERCOLATION TEST FEE $200.00
* MAKE ALL REMITTANCE PAYABLE•.TO: "EAGLE COUNTY TREASURER"
PROPERTY OWNER:
Z,gNi2'
MAILING ADDRESS: / ;? 3 MT S//V /9/ A )/C PHONE:
APPLICANT/CONTACT PERSON: PHONE:
LICENSED SYSTEMS CONTRACTOR: b l0 �i' PHONE:
COMPANY / DBA : 1 T ADDRESS : rC7 ZzE?,
PERMIT APPLICATION IS FOR: ( ) NEW INSTALLATION ( ) ALTERATION V REPAIR
LOCATION OF PROPOSED INDIVIDUAL SEWAGE DISPOSAL SYSTEM:
Legal Description: R411
Tax Parcel Number:
-
Lot Size:
Physical Address:
L�
(001 . �i1i1�F�t_�72
BUILDING TYPE:. (Check applicable category)
. Residential/Single Family Number of Bedrooms
Residential/Multi-Family* Number of Bedr oms 3
( Commercial/Indugtrial* j Type � y=4 0
TYPE OF WATE SU%'PLY: (Chec applicable cat gory)
O Well ( ) Spring ( ) Surface
( ) Public Name of Supplier:
*These systems require design by a Registered Professional Engineer
SIGNATURE: his ADate:
**************************************************************************
AMOUNT PAID: RECEIPT #: DATE:
CHECK # : CASHIER:
:w
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A
`CONIMUN Y DE'vLOPlv1ENrl
DEPARFit vT
(303) 328-8 30
EAGLE COUNTY, COLORADO
June 23, 1994
Richard Ranieri
123 Mt Sianai Ave
Mt. Sianai, NY 11766
500 BROADWAY
P.O. BOX 179
EAGLE. COLORADO 81631
PAX: (303) 328-7195
RE: Failing septic system at 549 Big Dipper Rd. West Duplex Lot
27, Bellyache Ridge Rd. Tax parcel #1941-341-01-004.
Dear Mr. Ranieri,
On 5/10/94 this office conducted a.site visit on the above
referenced property. The purpose of the site visit was to
investigate an allegation that an individual sewage disposal
system (ISDS) was failing on the property. During this visit it
was discovered that this ISDS is not functioning properly.
Be aware that this constitutes a violation of Eagle County Land
Use Regulations 4.03, et sea. "The owners of any structure where
people live, work, or congregate shall insure that the structure
contains adequate, convenient, sanitary toilet and sewage
disposal systems in good working order. Under no condition shall
sewage effluent be permitted to be discharged upon the surface of
the ground , or into waters of the State, unless the sewage or
effluent meets the Water Quality Standards of the Colorado Water
Quality Control Commission, or the Colorado Department of Health
Guidelines Chapter 25, Article lo, C.R.S. 1973, as amended,
whichever are applicable.,,
As per Eagle County Land Use Regulations 4.03.06, "Application
for a repair permit shall be made by such owner or occupant to
the Environmental Health Department within two business days
after receiving notice from the Department that the system is not
functioning in compliance with section 25 article 10 C.R.S. 1973
as amended."
1 �
Mr. Richard Ranieri
June, 23, 1994
Page 2
It remains unclear as to the actual configuration of the waste
water facilities serving the duplex. The adjacent owner after
having received our notice has applied for a repair permit and
has proceeded to pump and uncover his systems components. In his
opinion there exist two tanks on one leach field. Our records do
not clarify the matter, but we do know that it is the leach field
that is failing. Therefore, you are required to conduct a,the
same investigative measures after your application has been made.
Eagle County Land Use Regulations 4.03.25 states "The order shall
require that the owner or occupant bring the system into
compliance or eliminate the nuisance or hazard within a
reasonable period of time, not to exceed 30 days, or thereafter
cease and desist from use of the system."
This situation must be rectified immediately. A repair permit
must be applied for within two business days after the receipt of
this letter to avoid court intervention. Georgi Turk has been
notified as well, and has indicated that she will aide with this
situation.
Please be advised, Eagle County will pursue all available legal
remedies to ensure that your septic system does not endanger the
health of your tenants or anyone else in the surrounding area.
Please find the enclosed ISDS repair application and other
pertinent information.
Sincerely,
CLL-- 51vv
Raym Merry, RE S
Envir ivision Manager
cc: James R. Fritze, Eagle County Attorney
Jim Chubrilo, CDH, Water Quality Control Div.
Keith Montag, Director of Community Development
Dr. Phil Friedman, Eagle County Health Officer
Georgi Turk, realtor
f � �
6�a�9y
�bl7`�iyr�c `✓2%� /l��
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 328.8730
May 23, 1995
Mr. Richard Ranieri
123 Mount Sinai Avenue
Mount Sinai, NY 11766
RE: NOTICE OF HEARING
Dear Mr. Ranieri,
P.O. BOX 179
EAGLE, COLORADO 81631
FAX (303) 328.7207
EAGLE COUNTY, COLORADO
CERTIFIED MAIL # P 794 721 497
In accordance with the procedure outlined in the Eagle County Land Use
Regulations (ECLUR), Section 4.03.25, a hearing will be held to determine
whether to issue an order to cease and desist from the use of your
individual sewage disposal system (ISDS) serving the dwelling located at
549 Big Dipper Road, Bellyache Ridge Subdivision, Eagle County, Colorado.
The order, if issued, will require the owner to bring the system into
compliance with ISDS Regulations or eliminate the nuisance or hazard within
a reasonable period of time, not to exceed thirty (30) days, or thereafter
cease and desist from the use of the system. You are entitled to be
present personally and/or with counsel if you wish to be heard.
Eagle County received correspondence from Long's Excavation, Inc., that we
felt justified refraining from requiring a repair of your system until
spring. I'm sending this notice now to allow time for the repairs to occur
prior to the hearing. In addition, the ISDS Permit previously issued to
Long's Excavation, Inc., (ISDS #1389) has since expired. It will be
necessary to re-evaluate the design of the repair for a new permit to be
issued. Eagle County will not be requiring an additional permit fee.
As you are aware, this system was determined not to be functioning in
compliance with the above referenced Regulations as it constitutes a
nuisance to public health and has not received timely repairs in accordance
with the provisions of paragraph 4.03.06, ECLUR.
The hearing will be held Thursday, July 6, 1995 at 3:00pm, in the Eagle
County Room at the Eagle County Building, located at 500 Broadway, Eagle,
Colorado.
Sincerely,
4Rad P.Merry, Vnag7er
nmental H lth
cc: Keith P. Montag, Director of Community Development
James R. Fritze, Eagle County Attorney
ISDS File #1389
om: KEITH AND JENNY GILBERT SUMMIT SEWER SYSTEMS, INC. Fax: 719396E637 Voice: 7193N4W To: HANK DANLEY Page 2 of 2 Friday, September 01,1995 9:41:19 AM
'Th
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
Fax 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY ENVIRONMENTAL HEALTH DEPT.
ATTN: RAY MERRY
P.O. BOX 179
EAGLE, CO 81631
REF: SEWER SYSTEMS FOR LOT #27, BELLYACHE RIDGE SUBDIVISION
EAGLE CO., CO.
EAST UNIT: STEVE ARMSTRONG
WEST UNIT: RICHARD RANIERI
THIS IS TO CERTIFY THAT THE WHITEWATER AEROBIC SEWER
TREATMENT SYSTEMS HAVE BEEN INSTALLED IN ACCORDANCE WITH
THE ENGINEER'S DESIGN AND THE MANUFACTURER'S INSTALLATION
GUIDLINES. IF ANY ADDITIONAL INFORMATION IS REQUIRED, PLEASE
FEEL FREE TO CONTACT ME.
SINCERELY,
Z"IZ14�1
KEITH GILBERT-
SUMMIT SEWER SYSTEMS, INC.
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
Fax 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179
500 BROADWAY
EAGLE, CO 81631
REF: SERVICE CONTRACT FOR LOT #27, BELLYACHE RIDGE
SUBDIVISION
EAGLE COUNTY, CO.
IR11119KOV, 1'
SUMMIT SEWER SYSTEMS, INC. WILL PROVIDE STANDARD MONTHLY
MAINTENANCE SERVICES FOR THE WHITEWATER AEROBIC SEWER
SYSTEMS INSTALLED AT THE ABOVE LOCATION AT NO CHARGE TO THE
HOMEOWNER.
THE STANDARD MAINTENANCE INCLUDES:
- CLEANING OF COMPRESSOR AIR FILTER
- CYCLING TIMER MECHANISM
- INSPECTING DRIPFIELD
- FLUSHING DRIPFIELD (BI-ANNUALLY)
- PERFORMING 4 BI-ANNUAL SAMPLINGS FOR SOLIDS CONTENT
ALL OPERATING EXPENSES OR REPLACEMENT ITEMS NOT COVERED
UNDER MANUFACTUERER'S WARRANTY WILL BE THE RESPONSABILITY
OF THE HOMEOWNER. (IE. ELECTRICAL EXPENSE, PUMP -OUT FEES,
ETC.)
IF THE OWNERSHIP OF THE UNIT CHANGES HANDS, THIS CONTRACT
SHALL BE NULL AND VOID, AND A NEW CONTRACT MUSE BE SIGNED
BY THE NEW OWNERS AS PART OF THE SALE OF THE PROPERTY. A FEE
SHALL BE CHARGED TO THE NEW OWNERS FOR SAID CONTRACT. THE
FEE WILL BAOF A STANDARD RATE EQUIVALENT TO THE COST OF
SIMILAR CONTRACTS AT THE TIME THE NEW CONTRACT IS WRITTEN.
KEITH GILBERT
SUMvUT SEWER SYSTEMS, INC.
i u I
FAX TRANS, 17TAL COVER SHEET
LONG'S R%CAVA.TI0N. INC.
P.O. BOX 894
AVON, CO.81620
(303)949-4682
FAX(303)949-4586
DATE: I�_'� G%� #PAGES_INCLUDES COVER
FRO
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SPECIAL INSTRUCTIONS: .
ORIGINAL TRANSMISSION DOCUMENT TO FOLLOW VIA:
REGULAR MAIL
SECOND DAY DELIVERY
OVERNIGHT LETTER
WII.LNOTFOLLOW�L
IF YOU DO NOT RECEIVE ALL OF THE ABOVE PAGES, PLEASE CONTACT
THE SENDER AT (303)949-4682 AS SOON AS POSSIBLE.
WORTANT NOTICE
THIS MESSAGE AND ATTACHU ENTS ARE INTENDED ONLY FOR THE USE OF
THE INDIVIDUAL TO WHICH IT IS ADDRESSED. PLEASE FORWARD THIS
TRANSMITTAL TO THE IIMNDP.D RECIPIENT AVAEDIA.TELY. IF YOU HAVE
RECEIVED THIS IN ERROR, PLEASE CONTACT OUR OFFICE AS SOON AS
POSSIBLE.
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EAGLE COUNTY, COLORADO
Date:. August 16, 1995
TO: Long's Excavation
FROM: Environmental Health Division
RE: Issuance of Individual Sewage Disposal System
Permit No. 1511-95 Tax Parcel #1941-341-01-004
Property Location: 549 Big Dipper Rd., Bellyache
Ridge, Ranieri residence.
Enclosed is your ISDS Permit No. 1511-95.It is valid for 120
days. The enclosed copy of the permit must be posted at the
installation site. Any changes in plans or specifications
invalidates the permit unless otherwise approved. Please call
,our office well in advance for the final inspection.
Systems designed by a Registered Professional Engineer must be
certified by the Engineer indicating that the system was
installed as specified. Eagle County does not.perform final
inspections on engineer designed systems. Engineer as-builts
must be submitted for permit to be finalized and T.C.O. issued.
Permit specifications are minimum requirements only, and should
be brought to the property owner's attention.
This permit does not indicate conformance with other Eagle County
requirements.
If you have any questions, please feel free to contact the
Environmental Health Division at 328-8755.
cc: files
Community Development Department
(970)328-8730
Fax: (970) 328-7185
TDD: (970) 328-8797
EAGLE COUNTY, COLORADO
September 27, 1995
Mr. Richard Ranieri
123 Mt. Sinai
Mt. Sinai, NY 11766
Dear Mr. Ranieri,
Eagle County Building
P.O. Box 179
500 Broadway
Eagle, Colorado 81631-0179
The Environmental Health Division is awaiting the signed
agreement stipulated in your Individual Sewage Disposal System
(ISDS) Permit #1389, between you and Summit Sewers, Inc., in
order to finally approve the repair to your ISDS.
In addition, the previously existing septic system needs to be
abandoned in accordance with Eagle County Land Use Regulation
4.15.07 which states "The contents of a septic tank, vault, or
seepage pit, the use of which has been terminated, shall be
properly disposed of as required in Section 4.15.05 whereupon the
emptied tank, vault, or pit shall be filled with rock or soil.
This means the old tank must be pumped by a licensed pumper, then
filled with dirt or rock, and the executed maintenance agreement
must be recieved by this office before the new system is finally
approved. The maintence agreemment will then be recorded with
the property deed by this office.
Should you have any questions, please call this office at (970)
328-8755.
Sincerely,
Raymond P. Mer'ry, REDS
Environmental Health Division Manager
cc: Robert W. Loeffler, Assistant County Attorney
Keith P. Montag, Director of Community Development
ISDS Permit File #1389
EI7H AND JENtJY GIL',,eRT SUMMIT SEWER SYSTEMS, INC. Fax: 7193964 W Voice: 7193954= To: HANK DANLEY Papa 2 of 2 Friday, Saptambar01,1996 9.41:19 AM
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY ENVIRONMENTAL HEALTH DEPT.
ATTN: RAY MERRY
P.O. BOX 179
EAGLE, CO 81631
Fax 719-395-6537
REF: SEWER SYSTEMS FOR LOT 927, BELLYACHE RIDGE SUBDIVISION
EAGLE CO., CO.
EAST UNIT: STEVE ARMSTRONG
WEST UNIT: RICHARD RANIERI
THIS IS TO CERTIFY THAT THE WHITEWATER AEROBIC SEWER
TREATMENT SYSTEMS HAVE BEEN INSTALLED IN ACCORDANCE WITH
THE ENGINEER'S DESIGN AND THE MANUFACTURER'S INSTALLATION
GUIDLINES. IF ANY ADDITIONAL INFORMATION IS REQUIRED, PLEASE
FEEL FREE TO CONTACT ME.
SINCERELY,
KEITH GILBERT-
SUMMIT SEWER SYSTEMS, INC.
w..ri,�
kid �x'"p"0 F f
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577794 B-681 P-786 11/27/95 03:13P PG 1 OF 1 REC
Sara J. Fisher Eagle County Clerk & Recorder 0.00
DOC
V)
s'
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
Fax 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179
500 BROADWAY
EAGLE, CO 81631
REF: SERVICE CONTRACT FOR LOT #27, BELLYACHE RIDGE
SUBDIVISION
EAGLE COUNTY, CO.
SUNMT SEWER SYSTEMS, INC. WILL PROVIDE STANDARD MONTHLY
MAINTENANCE SERVICES FOR THE WHITEWATER AEROBIC SEWER
SYSTEMS INSTALLED AT THE ABOVE LOCATION AT NO CHARGE TO THE
HOMEOWNER.
THE STANDARD MAINTENANCE INCLUDES:
- CLEANING OF COMPRESSOR AIR FILTER
- CYCLING TIMER MECHANISM
- INSPECTING DRIPFIELD
- FLUSHING DRIPFIELD (BI-ANNUALLY)
- PERFORMING 4 BI-ANNUAL SAMPLINGS FOR SOLIDS CONTENT
ALL OPERATING EXPENSES OR REPLACEMENT ITEMS NOT COVERED
UNDER MANUFACTUERER'S WARRANTY WILL BE THE RESPONSABILITY
OF THE HOMEOWNER. (IE. ELECTRICAL EXPENSE, PUMP -OUT FEES,
ETC.)
IF THE OWNERSHIP OF THE UNIT CHANGES HANDS, THIS CONTRACT
SHALL BE NULL AND VOID, AND A NEW CONTRACT MUST BE SIGNED
BY THE NEW OWNERS AS PART OF THE SALE OF THE PROPERTY. A FEE
SHALL BE CHARGED TO THE NEW OWNERS FOR SAID CONTRACT. THE
FEE WILL BWOF A STANDARD RATE EQUIVALENT TO THE COST OF
SIMILAR CONTRACTS AT THE TIME THE NEW CONTRACT IS WRITTEN.
KEITH GILBERT RICHARD RANIERI
SUNMT SEWER SYSTEMS, INC.
577795 B-681 P-787 11/27/95 03:15P PG 1 OF 1 REC
Sara J. Fisher Eagle County Clerk & Recorder 0.00
DOC
r��
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 328.8730
EAGLE COUNTY, COLORADO
August 4, 1995
Mr. Richard Ranieri
123 Mount Sinai Avenue
Mount Sinai, NY 11766
RE: Enforcement of the Cease and Desist Order
Dear Mr. Ranieri,
P.O. BOX 179
EAGLE, COLORADO 81631
FAX (303) 328.7207
Due to logistics involved with your desire to install a different
wastewater treatment technology than was originally specified, I have
chosen not to enforce the Cease and Desist Order until August 25, 1995. It
is important to understand that the Order is not being lifted or extended.
It is my understanding that Keith Gilbert, Summit Sewers, Inc., will be
installing his company's technology and that Hank Danley is the Registered
Professional Engineer designing the system. Mr. Gilbert informed me that
he was obligated to .go to Venezuela for the oil company he works for and
that Mr. Danley had a death in the family which would delay the submittal
of the design for a few days. I also understand that you have chosen
Long's Excavation, Inc. to install the system under the supervision of Mr.
Gilbert. If Long's Excavation is not your Licensed Systems Contractor,
please advise me, in writing, who you are selecting no later than August
11, 1995.
Please be advised that ISDS Permit #1511, will be conditioned by there
being a maintenance agreement to assure long-term performance of this
system. If there are any further questions regarding this correspondence,
please call my office at (970) 328-8755.
Sincere -�
Raymon Merry, R
Envir mental Heal Man
cc: Robert W. Loeffler, Attorney
Keith P. Montag, Director.of Community Development
ISDS File #1511
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 32 8.87 30
P.O. BOX 179
EAGLE, COLORADO 81681
FAX (303) 328.7207
EAGLE COUNTY, COLORADO
Stephen Armstrong -e f9 $6-ev, _ o2N,4
P.O. Box 3568
Vail, CO 81658
Richard Ranieri
123 Mt. Sinai Ave. PSG
Mt. Sinai, NY 11766
CEASE AND DESIST ORDER
RE: 549 Big Dipper Road, East Duplex Lot 27, Bellyache Ridge, Tax
parcel #1941-341-01-005
549 Big Dipper Road, West Duplex Lot 27, Bellyache Ridge, Tax
parcel #1941-341-01-004
This matter came on for hearing, pursuant to written notice, at
3:00 p.m. on July 6, 1995, before Raymond P. Merry, acting in his
capacity as the chief administrative officer of the Eagle County,
Colorado, Division of Environmental Health, and the Health Officer
for purposes of Eagle County Land Use Regulations ("ECLUR"),
Chapter 4. Stephen Armstrong did not appear. Richard Ranieri
appeared by his attorney, Kerry Wallace.
Based upon the statements and evidence offered at the hearing:
IT IS FOUND:
1. In response to a complaint, on May 10, 1994, the Eagle
County, Colorado, Division of Environmental Health investigated the
Individual Sewage Disposal System ("ISDS") serving the properties
located at 549 Big Dipper Road, East Duplex Lot 27, Bellyache
Ridge, Tax Parcel #1941-341-01-005 and at 549 Big Dipper Road, West
0
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 2
Duplex Lot 27, Bellyache Ridge, Tax Parcel #1941-3471-01-005,
owned, respectively, by Stephen Armstrong and Richard Ranieri. The
investigation showed that the system was failing, effluent was
saturating the ground and seeping onto the surface of the ground,
and the system was not functioning in compliance with Eagle County
Land Use Regulations, Chapter 4. It subsequently was determined
that a single tank was serving both properties.
2. Written notice of violation pursuant to ECLUR 4.03.24,
dated May 18, 1994, was given to Stephen Armstrong by mail, receipt
of which on May 20 was acknowledged by him. The notice stated that
he was required to apply for a repair permit within two.business
days, pursuant to ECLUR 4.03.06, and bring the ISDS into compliance
within 30 days.
3. Written notice of violation pursuant to ECLUR 4.03.24,
dated June 23, 1994, was given to Richard Ranieri by mail, receipt
of which on June 28 was acknowledged by him. The notice stated
that he was required to apply for a repair permit within two
business days, pursuant to ECLUR 4.03.06, and bring the ISDS into
compliance within 30 days.
4. Stephen Armstrong applied for a repair permit on May 23,
`vk"
5. Richard Ranieri applied for a repair permit on July 5,
1994.
6. A permit for the construction of new ISDS systems for the
respective properties, per engineering drawings, was issued to
Longs Excavation, Inc. on behalf of Stephen Armstrong and Richard
Ranieri on or about November 141 1994.
7. Longs Excavation, Inc. requested an extension of time to
complete the repair because of winter construction conditions, by
FAX on November 30, 1994.
8. Based on the advice of the County Health Officer that
during the winter the saturated surface and seeping effluent would
be ice or under snow and, therefore, would not constitute a
significant public health hazard while the winter conditions
existed, enforcement of the ECLUR was deferred pending repair in
Spring, 1995.
9. The Individual Sewage Disposal System(s) serving the two
duplexes on the properties is(are) not functioning in compliance
with the ECLUR and Title 25, Article 10 of the Colorado Revised
Statutes.
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 3
10. The Individual Sewage Disposal System(s) serving the two
duplexes on the properties has(have) not been repaired. The
system(s) has(have) not received timely repair as required by ECLUR
paragraph 4.03.06.
11. The failure(s) of the Individual Sewage Disposal
System(s) serving these properties constitutes a nuisance or hazard
to public health.
12. Written notice of this hearing was given to Stephen
Armstrong and Richard Ranieri, respectively, more than 48 hours in
advance of the hearing.
THEREFORE, IT IS ORDERED, pursuant to Eagle County Land Use
Regulations paragraph 4.03.25 and C.R.S. 25-10-106:
1. That Stephen Armstrong, and any person acting by, through
or in concert with him, shall cease and.desist from violation of
the Eagle County Land Use Regulations, Chapter 4, and Article 10 of
Title 25 of the Colorado Revised Statutes, with respect to the
property identified as 549 Big Dipper Road, East Duplex Lot 27,
Bellyache Ridge, Tax Parcel #1941-341-01-005, specifically by the
following acts:
a) refraining, after 11:59 p.m. on August 11, 1995,
from using or permitting the use in any way, including by
depositing water, liquid, or wastes of any nature in, the
Individual Sewage Disposal System serving that property;
b) bringing the Individual Sewage Disposal System
serving that property into compliance with the Eagle
County Land Use Regulations, and Article 10 of Title 25
of the Colorado Revised Statutes, and eliminating the
nuisance or hazard, not later than by 11:59 p.m. on
August 11, 1995.
2. That the issuance of any permit for the repair of the
system, including the installation of a replacement system,
pursuant to Eagle County Land Use Regulations paragraphs 4.03.06 or
4.03.04 shall not extend the time provided in paragraph 1 hereof.
3. That Richard.Ranieri, and any person acting by, through
or in concert with him, shall cease and desist from violation of
the Eagle County Land Use Regulations, Chapter 4, and Article 10 of
Title 25 of the Colorado Revised Statutes, with respect to the
property identified as 549 Big Dipper Road, West Duplex Lot 27,
4
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 4
Bellyache Ridge, Tax Parcel #1941-341-01-005, specifically by the
following acts:
a) refraining, after 11:59 p.m. on August 11, 1995,.
from using or permitting the use in any way, including by
depositing water, liquid, or wastes of any nature in, the
Individual Sewage Disposal System serving that property;
b) bringing the Individual Sewage Disposal System
serving that property into compliance with the Eagle
County Land Use Regulations and Article 10 of Title 25 of
the Colorado Revised Statutes, and eliminating the
nuisance or hazard, not later than by 11:59 p.m. on
August 11, 1995.
4. That the issuance of any permit for the repair of the
system, including the installation of a replacement system,
pursuant to Eagle County Land Use Regulations paragraphs 4.03.06 or
4.03.04 shall not extend the time provided in paragraph 3 hereof.
Dated: July 11, 1995
\ces&des
Ra d %Lry, REHSMa er,County
Environmen ivison
- _0 - -,- "-,- —'.- --'. . -- —.— I 1 .1- - - -" ". -- - -vill. mcFl IN rage i or I) PAonaay, AUOUR 14, 1 Wb 6:31:04 PM
FAX
Date: Monday, August 14,1995 Time: 6:36:01 PM 5 Pages
To: RAY MERRY
EAGLE CO. ENVIR. HEALTH
Fax: (970) 328-7207
VOICS: +1 (970) 328-8757
Comments:
From: KEITH AND JENNY GILBERT'
SUMMIT SEWER SYSTEMS, INC.
Fax: 719-395-6537
VolCe: 719-395-6537
AUG 15 1995
+, /14/95 Oe:31 TRUSWAL SYSTEMS 4 SUMMIT SEWER SYSTEM N0.249 P001
t
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GlUiERT
33305 COUNTY RD 36)
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179
500 BROADWAY
EAGLE, CO 81631
REF: SEWER SYSTEMS FOR LOT #27, BELLY
EAGLE COUNTY, CO.
DRIP FIELD LAYOUT
Tole one 719.395-6537
Fox 719-395-W7
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SUBDIVISION
UTILIZING ENGINEERING AND TEST DATA PERFORMED BY INTER-
k4OUNTAIN ENGINEERING (SEE ATTACHED BLUE PRINTS) , THE
FOLLOWING DESIGNED AEROBIC SYSTEMS SHOULD BE PLACED IN
AREAS DESIGNATED BY THE BLUE PRINTS.
3 BEDROOMS @ 150 GAL. EACH X" 150% = 675 GPD. (EACH UNIT)
SET DRIP FIELDS TO DOSE 101vIINUTES EVERY 2 HOURS (60 GAL/DOSE),
120 ]MINUTES OF DOSING PER DAY, (ASSUMING FLOAT SWITCH IS AT
DOSING LEVEL).
EACH EMITTER WILL HANDLE 1.5 GPH @ 25 PSI,
675 GPDI(1.5 GPH (2 HOUR DOSING/DAY)) = 225 EMITTERS. WITH 2 FT,
OF SPACING BETWEEN EMITTERS, 450 FT. OF DRIPLINE WILL SUPPLY
225 EMITTERS;
AS PER INTER -MOUNTAIN ENGINEERING, THE NATIVE SOIL CONSISTS
OF COARSE TO FINE SILTY SAND. WITH A HYDRAULIC LOADING RATE
OF 1-3 TO 1.6 GAL/SQ.FT./DAY, 80 SQ-FT./100 GAL/DAY IS REQUIRED FOR
TOTAL H2O ABSORPTION.
6.75 X 80 = 540 SQ/FT.
WITH 9 RUNS OF DRIPLINE /RUN, SPACED 2 FT. APART
TOTAL SURFACE AREA = 0�SQ)Ff'
HYD. LOADING FOR SANDY LOAM = 1.3 GAL / SQ/FT / DAY. W/ 8Qi Q/FT
AND 675 GPD, HYD. LOADING = l .19 GAL / SQ/FT /DAY. / �
--- -----.._....--------. ._.__.. UM .-----_. ._.._.............„. goy,""'N"O"' ,Huyuaw, iaao o.aa:�a rrn
©8i14ig5 08:3i TRUSWpL S`fSTEMS -� SMIT SEbJER SYSTEM �J0.249 P002
WEST UN IIARD CE
PREPARE SITE 24' X 58' BY PLOWING UNDER EXISTING GRADE, BEGIN
I3UILDMG MOUND UP TO I.5' ABOVE EXISTING GRADE USING NATIVE
SOIL, BED DRIP GRID (9 RUNS, 50' EACH, PLACED 2' APART) IN 2" OF
SAND (ANY SIZE). COVER WITH F OF NATIVE FILL. PLACE 2" BED OF
STRAW AND COVER WITH 2' OF NATIVE FILL.
FAST IINiT• S�.TE_V�,xIA17�1���TR6JNiG RESMNU
PREPARE SITE 22' X 56' BY EXCAVATLOG I' TO T OF EXISTING GRADE,
BEGINNING AT TEST PIT 4 AND ENDING BEFORE 'PEST PIT 5. PLOW NEW
BOTTOM. CENTER DRIP GRID (9 RUNS, 50' EACH, PLACED 2' APART) IN
EXCAVATION AND BED WITH 2" OF SAND (ANY SIZE). COVER WITH I' OF
NATIVE FILL. PLACE 2" BED OF STRAW AND COVER WITH 2° OF NATIVE
FILL.
DRIP GRID TO BE USED ONLY WITH THE WHITEWATER AEROBIC
TREATMENT PLANT INSTALLED AS PER x4ANUFACTUItEF'co
INSTALLATION INSTRUCTIONS.
09/14/95 08:31 TRUSWAL SYSTEMS 3 SUMM-IT SEWER SYSTEM NO.249 P003
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9
NOTICE OF INJURY CAUSED BY A PUBLIC ENTITY AND PUBLIC EMPLOYEE IN
THE COURSE OF EMPLOYMENT
TO:
EAGLE COUNTY BOARD OF COUNTY COMMISSIONERS
P.O. Box 850
Eagle, Colorado 81631
EAGLE COUNTY ATTORNEYS OFFICE _
JI_M FRITZ, COUNTY ATTORNEY
P.O. Box 850
APR 101995
Eagle, Colorado 81631
CLAIMANT.~
%,UVUV l NITY DEVELOPMENT
RICHARD RANIERI
'123 Mount Sinai Avenue
Mount Sinai, NY 11766®
CLAIMANT ATTORNEYS::
STOVALL GOODMAN WALLACE, P.C.
KERRY H. WALLACE, #21033
P.O. Drawer 58601
Avon, Colorado 81620
�
(303) 949-4200
RESPONSIBLE ENTITIES:
EAGLE COUNTY GOVERNMENT
P.O. Box 850
Eagle, Colorado 81631
(303) 328-8685
EAGLE COUNTY DEPARTMENT OF ENVIRONMENTAL HEALTH
P.O. Box 179
Eagle, Colorado 81631
(303) 328-8755
RESPONSIBLE EMPLOYEES KNOWN AT THIS TIME:
ERIK W . EDEEN
0541 Singletree Road
Edwards, Colorado 81632
(303) 926-2130
Any and all other employees of the Eagle County Department of Community
Development and Eagle County Department of Environmental Health or personnel which were
involved in the permitting, inspection, approval and reparation requirements of the septic system
located at Lot 27, Bellyache Subdivision, Filing Number 2, according to the recorded Plat
thereof, County of Eagle, State of Colorado also known as 0549 Big Dipper Road, Bellyache
Ridge Subdivision, Colorado whose names are not available at this time.
NOTICE: YOU ARE HEREBY PROVIDED with Notice of Claim pursuant to C.R.S.
24-10-109 that the CLAIMANT, RICHARD RANIERI, asserts a claim against the responsible
entities, parties, employers and agents based upon the following statement of facts known at this
time.
The CLAIMANT is the owner of real property known as Lot 27, Bellyache Ridge
Subdivision, Filing Number 2, according the recorded Plat thereof, also known as 0549 Big
Dipper Road, Wolcott, Colorado ("the property"). The Plaintiff purchased the property on April
15, 1994 from John L. and Ellen Warnack. Approximately two weeks after the CLAIMANT
purchased the property the previous owners reported to the Eagle County Department of
Environmental Health that the septic system upon the property appeared to be malfunctioning.
That upon the Eagle County Department of Environmental Health's inspection of the system it
was determined that the septic system had failed and would require replacement at a significant
cost and impact to the property.
That upon investigation by the Eagle County Department of Environmental Health, it was
determined that there was only one 1,000 gallon septic tank and one 800 square foot leach field
for the duplex building upon the property, which is inadequate for a duplex the size of the one
located upon the property. Upon investigation by CLAIMANT of the Eagle County Records
in regard to the property, it came to the CLAIMANT'S attention in mid -October, 1994, that
Eagle County had issued a permit, Number 374, on or about October 17, 1979 for installation
of a septic system when the duplex upon the property was constructed. The permit required that
there be the following type of septic system installed upon the property:
A. 1,000 gallon septic tank for each unit of the duplex and two 800 square foot installed
leach fields, with the recommendation of the installation of two dry wells, each 10 foot by 10
foot (1 dry well for each unit, leading from each one of the tanks).
B. An alternative absorption area is a terraced leach field of 1200 square foot combined
for both units.
The permit required that there be a final visual inspection of the septic system twenty-
four (24) hours prior to back fill (See Exhibit "A"). That Erik W. Edeen of the Eagle County
Department of Environmental Health issued a letter November 20, 1979 stating that upon
inspection of the individual sewage disposal systems upon the duplex, it was determined that the
disposal systems were installed according to specifications of the Eagle County Department of
Environmental Health, in particular that two 1,000 gallon septic tanks were installed (one for
each unit of the duplex) and two 800 square foot leach fields were installed (one for each unit
of the duplex) (Exhibit "B"). Yet, as stated previously, in 1994 it was determined by the Eagle
County Department of Environmental Health that only one septic tank and one leach field were
in place for the entire duplex.
In 1987 the septic system upon the property failed and the Eagle County Department of
Environmental Health only required minor repairs which, at best, would only temporarily
alleviate any problems with the septic system. At the time of this failure, the Eagle County
Department of Environmental Health failed to determine that there was only one system for the
entire duplex in place. (Exhibit "C"). That once the minor and inadequate reparations upon the
septic system were performed, the Eagle County Department of Environmental Health issued
at least two letters indicating that the system was functioning properly.
That the initial installation of an inadequate septic/sewage system upon the property
which did not comply with existing regulations in effect at the time and which in fact did not
even comply with the Eagle County Department of Environmental Health's permit requirements,
even though said system had been visually inspected and improved by the Eagle County
Department of Environmental Health, and the failure of the Eagle County Department of
Environmental Health to inspect and require the proper reparations in 1987 when the system on
the property failed has caused the CLAIMANT to incur damages including, but not limited to,
the cost of a new septic system, and loss of value of the property due to removal of trees to
make space for the new septic system.
CLAIMANT claims that due to the negligent actions of the Eagle County Department of
Environmental Health the CLAIMANT has suffered the above referenced damages. The exact
amount and nature of CLAIMANT'S damages are unknown at this time, but estimates for
installation of a new septic system are approximately $35,000.00 for each side of the duplex
upon the property. A new septic system will require the removal of a majority of the mature
trees upon the lot and will negatively impact existing landscaping.
Dated this —� day of 1995.
STOVALL GOODMAN WALLACE, P.C.
P.O. Drawer 5860
Avon, Colorado 81620
(303) 949-4200
ATTORNEYS FOR CLAIMANT
Richard Ranieri
Approved:
a
(date)
SUBSURFACE TRICKLE IRRIGATION SYSTEM
FOR ON -SITE
WASTEWATER DISPOSAL AND REUSE
Dr. B.L. Carlile P.E. Dr. A. Sanjines, Mech. E.
Cert. Prof. Soil Scientistt Geoflow, Inc. §
Summary of Process Description
The subsurface trickle irrigation system described in this report utilizes an
aerobic treatment system in conjunction with a proven subsurface water
application system developed by GEOFLOW, Inc. to offer a total system concept
for safe and effective sewage disposal for site conditions considered marginal
or unsuitable for conventional septic tank systems.
The integrated system described here is an improved dosing and
distribution concept compared to the low pressure pipe system, approved and
utilized in many states to overcome soil/site limitations. The proposed system is
also an effective irrigation system allowing reuse of treated wastewater in home
and lawn settings without the concerns of direct exposure of the effluent to
human and animal populations.
The system proposed is an integrated package consisting of several
components, each designed for a specific purpose in the treatment and
disposal of wastewater by trickle irrigation. including:
1. Primary treatment - the wastewater is first passed through a primary tank to
achieve physical settling of macro -solids and to assist in degradation of some
pollutants including oil and grease. This will be achieved in a septic tank for
home systems and a properly designed primary tank for larger flow systems
2. Secondary treatment - the primary effluent will be further treated in a
secondary treatment process by extended aeration in a Clearstream Aerobic
Treatment System that has been fully field and lab tested to show
achievement of effluent quality of better than 20 mg/I Biological Oxygen
Demand (BOD) and 20 mg/I Total Suspended Solids (TSS) at maximum
design flow.
3. Disinfection - the secondary effluent will be treated by chlorination ozonation
or ultra -violet radiation at adequate dosage to achieve disinfection of
pathogens to drinking water quality standards.
4. Filtration - the treated effluent in passed through a 150 mesh disc filter, with
manual or automatic backwash, prior to irrigation.
5. Subsurface irrigation - the relatively clean effluent is injected 6 to 10 inches
below the soil surface through trickle emitters located on 24 inch centers
throughout the disposal area. The effluent will be applied in several "pulses"
per day at rates not to exceed the water absorption capacity of the soil. A
typical system would be dosed 5 to 8 times per day at 50 gallons per dose. A
Carlile and Associates, Inc. PO Box 2677 College Station, TX 77841
Geoflow, Inc. Subsurface Irrigation. 236 W. Portal Ave, #327 San Francisco, CA 94127
Aerobic Chlorinator
unit
Wastewater
-----
Septic e o o
tank
I
Air compressor Dosing
chamber
Figure 1. Pretreatment System
Flush line -,*,
Compresion adapter
Driplines —►
Emitters �- ►
Moisture
sensor
`
(optional)
C
a Header
line
--_-------
Control valve-----
--T
i
i
��
i
► i
o000
0000
o000
Treated
Screen
000a
i effluent
Filt
Filter Water meter
I Timer
Pressure i
i
(optional)
regulator i '*-_ Valve
-- - - - - - -
- - - - - - - - - - - -
- - - - - - -- Box
Figure 2. Subsurface irrigation system
Sampling Treated
box Effluent
To subsurface
level switches drip system
PUMP
Flush =
valve
Valve box —
i
GEOFLOW INC.
Subsurface Irrigation
Installation Detail
design. It is proposed that the subsurface trickle irrigation system proposed
here is an improved and suitable replacement for both of the systems.
Soil Absorption System
The major factor in design of a satisfactory on -site waste disposal system for
poor soil conditions can be summarized as follows: 1) distribution, 2) dosing, 3)
sewage placement, and 4) improved pre-treatment and disinfection.
Distribution cannot be over -emphasized in the design of any on -site system
for "low perc" soils due to the need to spread sewage over large land areas.
The effluent must be distributed evenly over this large area so as not to exceed
the capacity of the soil to absorb the hydraulic load. Adequate distribution is
extremely hard, if not impossible, to achieve in any currently designed gravity
flow system. Some portion of the system is inherently overloaded which results
in initiation of the clogging phenomena and hence the "progressive failure"
observed in many such systems. Low pressure systems improve on the
distribution concept but have limitations in "low perc" soils in that trenches can
only be installed on 4 or 5 foot centers and the relatively high flow from drilled
orifices often result in effluent surfacing.
Dosina of effluent is equally important in maintaining the aerobic status of
the soil system in and around the distribution trench, thus preventing the
clogging or "slimming up" of soil interfaces and subsequent failure. Dosing
concepts can be described as either 1) short term dosing or 2) alternate dosing.
Short term dosing usually refers to multiply daily dosings of effluent into a
single system with several hours or sometimes days of resting and re -aeration
between each dose. Two to eight doses per day has been shown to be
satisfactory in systems designed for pressure dosing in either subsurface or
surface application.
Alternate dosing refers to dual or multiple fields where one part of field
receives all of the effluent for a specified period. at which time the effluent is
switched to the alternate plot. This can be done each pump cycle, once per day
or switched only when one field has a problem. Both short term and alternate
dosing is often utilized in trickle irrigation systems.
Both dosing concepts as well as combinations and modifications of the
above have been successfully utilized in several states to treat and dispose of
sewage from individual homes as well as cluster developments, school
systems, and mobile home parks with flows of up to 50,000 gpd.
The design factor of sewage placement refers to the concept of placing the
sewage in the soil zone or horizon most conducive to absorption, treatment, and
re -aeration. In soils with high water tables this usually means at least a one or
two foot separation between the seasonal water table and the point of sewage
injection. For soils with restrictive clay horizons or hardpans, the sewage should
be injected as high above the restrictive zone as possible. This minimum
separation allows for lateral or horizontal flow of effluent away from the
distribution trench or pipe before interception by the restrictive zone and allows
for more uniform absorption through the restricting layer. This, coupled with
enhanced treatment of the sewage in the better soils above the restrictive
horizon, greatly enhances the quality of effluent impacting the restrictive
3
Small individual home aerobic decomposition and treatment can be
accomplished at comparatively low cost through small mechanically aerated
treatment systems. The better small aerobic units are capable of producing
an effluent exceeding that of the most sophisticated municipal treatment
plants. Table 1 shows the summary of effluent quality from a two year
operational study of the Clearstream Aerobic Treatment System, field tested
at several homes in Florida and Texas and by extensive testing of the unit by
the National Sanitation Foundation, a national independent testing agency.
The aerobic treatment unit described here treats the primary effluent by
extended aeration in a mechanically aerated contact chamber. The aerated
wastewater in the contact chamber is well mixed to provide optimum
exposure of the microorganism to the waste material. There is also a
significant reduction of pathogenic bacteria during this process. After
approximately 24 hours of aerobic contact, the activated wastewater is
clarified in a settling chamber and the settled solids returned to the aeration
chamber. The settled and clarified effluent is discharged from the settling
chamber through an improved design discharge assembly to minimize
solids carryover.
Aerobic treatment of domestic wastewater can be accomplished in other
ways. Sand filtration is a process sometimes used whereby the domestic
wastewater is first given primary treatment in a septic tank to reduce solids
and then applied intermittently to the surface of a sand bed of 2.5 to 3 foot
depth. An efficient sand filtration method is the recirculating sand filter (RSF).
The RSF offers a high degree of treatment with a minimum of maintenance
or nuisance problems. The RSF when loaded at a raw waste hydraulic
loading of 2.5-3.0 gal/ft2 per day produces a high quality effluent of similar
characteristics to that of the better aerobic treatment units. The slow rate,
intermittent sand filter, when designed at an hydraulic loading of 1.5 to 2
gal/ ft2 per day of septic tank effluent can also produce a high quality
effluent.
The choice between an aerobic system or a sand filter system depends
both upon the particular technical circumstances as well as local
regulations. We suggest that a Professional Engineer be consulted.
All treatment systems require routine systematic maintenance and the
successful long term operation of the system is dependent upon this
maintenance being correctly carried out.
B. Disinfection
The treatment by chlorination, ozonation, or UV radiation of the effluent
discharged from the aerobic cell represents the final step of a "safe" pre-
treatment system designed to allow maximum reuse of the wastewater in a
landscape mode. The potential of ozonation for deactivating viruses and
bacteria, detoxifying organic compounds and oxidizing any odorous
components make it the logical choice for systems installed in lake shore
settings or in extremely high groundwater conditions.
Ozone concentration in very low amounts and at very short contact time
is capable of disinfecting and deodorizing the effluent. This process has
only recently been utilized for home waste treatment due to the high
installation and operation costs of ozonation systems.
5
treatment unit with disinfection designed in conjunction with the system should
keep the bacterial slimes under control in the system and the 150 mesh disc
filter installed in -line of the header should remove any extraneous solids which
might be of size to plug the emitter orifice.
All these components integrated into a reliable sub -irrigation system makes
this a unique process for domestic waste disposal. Other systems of a similar
nature are being promoted and used in some southeastern states. One such
system utilizes a rubber diaphragm pressure compensating emitter. The rubber
diaphragm reduces the outlet orifice during operation, making it highly
susceptible to clogging. Even though the orifice opens when pressure is off, the
chances of intermittent plugging with bacterial slimes are quite high.
A rubber diaphragm is susceptible to attack by oil, gasoline products and
oxidizing agents, resulting in a likely change in the physical characteristics of
the rubber overtime and thus affecting the uniformity of flow in the emitters.
Deposits also tend to build up at the seat of the diaphragm over time, changing
the flow characteristics of the emitter.
These pressure compensating emitters are not protected against root
intrusion and is susceptible to plugging by roots (2). Only the GEOFLOW
emitter protected by ROOTGUARD® can offer positive protection against a very
serious threat of root plugging.
Soil Application Design
The instantaneous water application rate of the system must not exceed the
water absorption capacity of the soil. A determination of the instantaneous
water absorption capacity of the soil is difficult, however, since the value varies
with the water content of the soil. As the soil approaches saturation with water,
the absorption rate reduces to an equilibrium rate called the "saturated
hydraulic conductivity." Wastewater application rates should be less that 10
percent of this saturated equilibrium
Even though the trickle irrigation system maximizes the soil absorption rate
through the low rate of application, thus keeping the soil below saturation, there
will be times when the soil is at or near saturation from rainfall events. The
design must account for these periods and assume the worst case condition of
soil saturation. By designing for a safety factor of 10 or 12, based on the .
saturated hydraulic conductivity, the system will be under -loaded most of the
time but should function without surface failure during extreme wet periods.
Using a safety factor of 12, a suitable design criteria would be to load the
system at the estimated hydraulic conductivity but apply water for only a total of
2 hours per day out of the available 24 hours. By applying wastewater for a
total of 2 hour per day, particularly if applied in "pulses" or short doses several
times per day near the soil surface were the soil dries the quickest, this would
keep the soil absorption rate at the highest value and minimize the potential of
water surfacing on poor soil conditions.
As stated previously, this design criteria will under -load the system at all
times except when the soil is at or near saturation from rainfall. If designing for
an efficient irrigation system, the water supply may not be sufficient to meet the
demands of a lawn or landscaped area during peak water demand months.
This problem can be overcome by either of two solutions: add additional fresh-
7
Pump Tank and Controls
Dosing and irrigation supply will be by a submersible effluent pump located
in a 150-300 gallon storage tank. The operation of the pump will be by a simple
float on -off level switch in the tank. The "on" level switch will activate the pump
when the tank reaches a high water mark and the low level switch will turn the
pump off when the tank reaches a predetermined minimum water level. For a
typical system this volume would be 50-100 gallons. For a 250 to 500 GPD
system, this results in 3 to 10 irrigation pulses per day. For systems on sloping
ground where water drains from the pipes to the lower points of the system after
each pulse or dose, larger doses and fewer pulses per day would be more
suitable. Irrigation uniformity is best maintained with irrigation pulses of 10
minutes or more.
Filter Requirements
The recommended disc filter uses a 150 mesh screen that filters out particles
larger than about 100 microns. The type of emitter used in GEOFLOW trickle
systems will not have problems with this particular size since the diameter of the
flow path is 14 to 17 times larger, or 0.056 inches (1400 microns) for the 1 GPH
emitter to 0.08 inches (2,000 microns) for the 2 GPH emitter. To maintain the
proper water quality for the drip system, the filters are easily backwashed
manually or equipped with automatic back flush triggered by a timer or a
pressure differential switch. The installation schematic of the in -line filter is
shown in the typical system lay -out. `
Flow Regulator
Under normal conditions, the pressure in the trickle lines should be
maintained between 20 and 25 psi during operations. This is controlled by a
pressure regulator located in -line following the filter. The emitter lines are
connected at each end by a PVC header line and flush line to allow optimum
pressure equilibrium in the system. Flush /vacuum release valves are located
at each end of these lines to allow a small amount of water to be automatically
flushed from the system every time it is started and avoid dirt suck back when
the system is switched off. This is important to prevent solids from accumulating
at the ends of these lines and to prevent dirt from entering the lines.
The schematic of a typical field layout of the trickle irrigation system shows
only a single field. For systems over 2000 ft in size or having over 500 emitters,
the system would be split into 2 or more fields of equal size. Flow for a dual
field system would be alternated through the use of a mechanical valve which
automatically switches fields each time the pump is activated.
For systems with more than 2 fields, the operation of each field is controlled
with an irrigation controller utilizing electric solenoid valves for each field
station. By separating the system into several fields, smaller pumps and more
uniform distribution can be achieved. Where soil conditions vary, some fields
may be programmed to receive less water than other fields of the system .
Trickle Emitter Lines
A normal home system would have emitter lines placed on 2 foot centers
with a 2 foot emitter spacing such that each emitter supplies a 4 ft area (Fig. 3).
These lines are best placed at depths of 6-10 inches below the surface. This is
0
Bibliography
1. Pettygrove, G.S. Asano, T. editors, Irrigation with reclaimed municipal wastewater - A
guidance manual, Lewis Publishers, Inc.
2. Bui, W. Performance of turbo model drip irrigation tubes. Proceedings of the third national
irrigation symposium. ASAE, November 1990 pp. 198-203.
3. Fowler, Lloyd C. Water reuse for the landscape. Goleta Water District. Goleta, CA.
4. Irwin, John. On -site wastewater reclamation and recycling. Proceedings of CONSERV90
Conference AWWA, AWRA, ASCE August 1990 pp 107-111
5. Jackson, J. D. Aquatic macrophite treatment systems for water reuse. Proceeding of
CONSERV90 Conference AWWA, AWRA, ASCE August 1990 pp 101-105
6. Gross, Mark A. et al. On -site treatment for reuse of domestic septic tank effluent in an
artificially drained soil. Proceedings of CONSERV90 Conference AWWA, AWRA, ASCE August
1990 pp 95-97.
7. Farwell, Larry. Grey Water reuse. Goleta, Water District, Goleta, CA. Proceedings of
CONSERV90 Conference AWWA, AWRA, ASCE August 1990 pp 1065-66.
8. English, Stephen. Filtration and water treatment for micro irrigation. Proceedings of the 3rd
International drip irrigation congress, Fresno, CA, 1985.
9. Phene, Claude C. Drip irrigation saves water. Proceedings of CONSERV90 Conference
AWWA, AWRA, ASCE August 1990 pp 645- 650
10. Stevens, Leonard. Clean Water Nature's way to stop pollution. Sunrise, New York 1974.
11. Reed, Sherwood. Land treatment of wastewater, Noyes Publications, Park Ridge, 1984.
12. Holden, Tim et al. How to select hazardous waste treatment technologies for soils and
sludges. Noyes Publications, Park Ridge, 1989.
13. Nakayama, F.S. Water analysis and treatment techniques to control emitter plugging.
Proceedings of the Irrigation Association Conference, Portland, 1982.
14. EPA "Land Treatment of Municipal Wastewater." EPA 625/1-81- 013. 1981.
15. Stewart, L.W. and R.B. Reneau, Jr. Spatial and Temporal Variation of Fecal Coliform
Movement Surrounding Septic Tank Soil Absorption systems in Coastal Plain Soils. J. Env. Qual.
10:528-531, 1981.
16. Carlile, B.L., C.G. Cogger, M.D. Sobsey and S.S. Steinbeck. Movement and Fate of Septic
Tank Effluent in Soils of the North Carolina Coastal Plain. Dept. of Human Resources, State of
North Carolina, Raleigh, North Carolina, 1981.
17. Carlile, B. L. "Use of Shallow, Low Pressure Injection Systems for Large and Small
Installations" in Individual Onsite Wastewater Systems, N. McClelland Ed. (Ann Arbor, MI: Ann
Arbor Science Publishers, Inc. 1979).
18. Carlile, B. L., A. R. Rubin and D. J. Osborne. "Status of Innovative and Alternative
Wastewater Treatment Systems in North Carolina." Paper No. 79-2586 presented at American
Soc. Ag. Eng. Conf. (Dec., 1979).
12
COLORADD DP''AD-VZ^r
Or '�����.'
DATE:
03/22/95
iyORGAWC CHEMISTRY
LABORATORY
REPORTED BY;
0k
4210 E 11TH AVE, DENVER.
CC 30220
(303)691-4726
SAMPLE NUMBER:
�510G2
SAMPLE DESCRIPTION:
SUMMIT �EWER SYSTEMS
ADDRESS 33305
CP 25`
COUNTY:
CHF
BUENA
VISTA. CO 81211
PHONE :
COLLECTED BY: KEIrH GILOER-
YVHERE: EFFULENT
DATE SAMPLED: 03/10/95
DATE RECEIVED: 03/10/95
BOTTLES: 2L @EUT
TYPE: 7
COMMENTS: FEE PAID $67.7'.
ANALYSIS RESULTS
80D, SEWAGE mg/L
PH
SOLIDS, SUS. < 10 mq/L
COLORADO DEPARTMENT OF HEALTH DATE: 03/16/95
INORGANIC CHEMISTRY LABORATORY REPORTED BY: HN
4210 E 11TH AVE. DENVER, CO 80220
(303)691-4726
SAMPLE NUMBER: 951062 PWSID #:
SAMPLE DESCRIPTION: SUMMIT SEWER SYSTEMS INC
ADDRESS 33305 CR 361 COUNTY:
BUENA VISTA, CO 81211 PHONE : 7193956537
COLLECTED BY: KEITH GILBERT
WHERE:
DATE SAMPLED: 03/09/95
DATE RECEIVED: 03/09/95
BOTTLES: L NUT
TYPE: 8
COMMENTS: FEE PAID 28.50
ANALYSIS RESULTS
EPA LIMITS
N-NITRATE/NITRITE NONE DETECTED MCL=10.0 mg/L
PHOSPHATE - TOT 6.7 mg/L
MCL = MAXIMUM CONTAMINANT LEVEL
MSL = MAXIMUM SUGGESTED LEVEL
NLE = NO LIMITS ESTABLISHED
EAL = EPA ACTION LEVEL
�J
SPECIMEN
I.D.
SPECIMEN
I.D.
Delta Environmental Products, Inc.
WIDTH
(in.)
0.748
0.751
0.758
0.752
0.760
WIDTH
b
0.511
0.501
0.487
0.508
0.520
FIBERGLASS TEST REPORT
DEPTH
d
0.253
0.275
0.238
0.265
0.243
TENSILE PROPERTIES
ASTM D 638
DEPTH
ARE
(in.)
sq. i
0.242
0.1
0.230
0.17
0.273
0.20
0.245
0.18
0.265
0.20
EA MAX. LOAD TENSILE STRENGTH
n. (pounds) (PSI)
81 3,580 19,800
3 3,560 20,600
7 4,040 19,500
4 3,980 21,600
1 4,150 20,600
AVERAGE 20,420
STD. DEV. 8?0
FLEXURAL PROPERTIES
ASTM D790
MAX LOAD FLEXURAL STRENGTH
P (PSI)
177.7 32,600
209.9 33,240
139.2 30,280
185.0 31,110
188.1 36,760
AVERAGE 32,800
STD, DEV. 2506
SLOPE FLEXURAL MODULUS
m (PSI)
648 1.25 E+06
768 1.18 E+06
468 1.14 E+06
724 1.23 E+06
568 1.22 E+06
AVERAGE 1.20 E+06
STD. DEV. 4.39 E+04
VOID CONTENT of REINFORCED RESIN
ASTM D 2734
SPECIMEN ASTM D 792 ASTM D 2584 THEORETICAL DENSITY CALCULATED VOIDS I.D. DENSITY RESIN / GLASS
(70)
1 1.516 56.3 43.7 1.634
2 1.519 56.0 44.0 7.2
1.630 S.g
3 1.523 56.0 44.0 1.630
AVERAGE 1.519 56.1 44.9 6.6
1.631 6.9
STD. DEV. 0.004 0.17 0.002
0.31
FLEXURAL PROPERTIES
ASTM D790
MAX LOAD FLEXURAL STRENGTH
P (PSI)
177.7 32,600
209.9 33,240
139.2 30,280
185.0 31,110
188.1 36,760
AVERAGE 32,800
STD, DEV. 2506
SLOPE FLEXURAL MODULUS
m (PSI)
648 1.25 E+06
768 1.18 E+06
468 1.14 E+06
724 1.23 E+06
568 1.22 E+06
AVERAGE 1.20 E+06
STD. DEV. 4.39 E+04
VOID CONTENT of REINFORCED RESIN
ASTM D 2734
SPECIMEN ASTM D 792 ASTM D 2584 THEORETICAL DENSITY CALCULATED VOIDS I.D. DENSITY RESIN / GLASS
(70)
1 1.516 56.3 43.7 1.634
2 1.519 56.0 44.0 7.2
1.630 S.g
3 1.523 56.0 44.0 1.630
AVERAGE 1.519 56.1 44.9 6.6
1.631 6.9
STD. DEV. 0.004 0.17 0.002
0.31
SLOPE FLEXURAL MODULUS
m (PSI)
648 1.25 E+06
768 1.18 E+06
468 1.14 E+06
724 1.23 E+06
568 1.22 E+06
AVERAGE 1.20 E+06
STD. DEV. 4.39 E+04
VOID CONTENT of REINFORCED RESIN
ASTM D 2734
SPECIMEN ASTM D 792 ASTM D 2584 THEORETICAL DENSITY CALCULATED VOIDS I.D. DENSITY RESIN / GLASS
(70)
1 1.516 56.3 43.7 1.634
2 1.519 56.0 44.0 7.2
1.630 S.g
3 1.523 56.0 44.0 1.630
AVERAGE 1.519 56.1 44.9 6.6
1.631 6.9
STD. DEV. 0.004 0.17 0.002
0.31
VOID CONTENT of REINFORCED RESIN
ASTM D 2734
SPECIMEN ASTM D 792 ASTM D 2584 THEORETICAL DENSITY CALCULATED VOIDS I.D. DENSITY RESIN / GLASS
(70)
1 1.516 56.3 43.7 1.634
2 1.519 56.0 44.0 7.2
1.630 S.g
3 1.523 56.0 44.0 1.630
AVERAGE 1.519 56.1 44.9 6.6
1.631 6.9
STD. DEV. 0.004 0.17 0.002
0.31
0
NSF International
November 2, 1994
Ms. Brenda Guy
Delta Fiberglass & Environmental Products Inc
P.O. Box 969
Denham Springs, LA 70727
Dear Ms. Guy:
By this letter, NSF certifies that the results reported below are true and accurate results of
ammonia nitrogen analyses completed at the request of Delta Fiberglass & Environmental Products,
e
Inc. following completion of the Standard 40 Certification evaluation for the Delta Model DF
Plant at the NSF Wastewater Technology Site in Chelsea, Michigan. The Standard 40 tes ' 40the
Plant was completed during the week of January 24, 1993, however dosing ung of the
capacity of 400 gallons per day was continued at the request of Delta Fiberglass. plant the rated
Delta Fiberglass requested analysis of the Chelsea influent wastewater dosed to the last
efrTueat samples from the DF40-M for ammonia nitrogen. Samples were collected once and the
beg�g March 26, 1993 (37 weeks after the Stan of the Standard 40 evaluation) and en reek
samples collected on May 26, 1993 (46 weeks after the start of the Standard 4 ded Kith
samples were collected as described in the Wastewater Technology report (dated June 19 3)
Model DF40-_14 and were analyzed in. accordance with EPA Method 350.1. 93) for the
The results of the analyses (reported as mg/L as N) were:
Samo_le� Influent NH, Effluertt NIA,
3/26/93
13
2.8
3/31/93
14
1.4
4/8/93
12
0.98
4/14/93
11
1.9
4/21/93
13
1.6
S"1112 OatC emu— en—t L Efriue�-H,
4/28/93 14
1.5
5/5/93 11
2.3
5/12/93 20
4.6
5/21/93 26
2.2
5/26/93 25
Delta Fiberglass is hereby authorized to distribute this letter 2.1
results of ammonia nitrogen analyses completed b ' m its entirety, y NSF, as described Y' � a summary of the
any questions you have, above. Please contact me wilh
Sincerely,
i
ThomasWi.ursema
Manager, Wastewater Treatment Unit
Certification & Related Programs
(313) 769-5575
3475 Plymou(h Road, PO lion 130140 Ann rbor
Telephone: 313 780-801(1 FAX: 313-7G9-01A(i9 Aficltignn 48113-0140 USA
T'd=: 753215 NSF INTL
Rt. 2, Box 359A
Guntown, MS 38849
7, :L994
Phone
Pager
348-5521
678-4858
348-5339
678-4859
?1� GUY
F'IPiD , ,Ur OF ANALY , •, PERFORMED
�DEN TEN DELTA TREATMENT PLANTS.
Ph.E:3F.RVED. AND t1NP,LY�;F,ji t, AL' .ryAMPLE:3 WERE COLLECTED,
E�_iV1 R(-UMENTAL PROTECTION ,-.AGrUF;I.�ANt, WITH UNI't'EU STA'CE:;
Fl- - T AGENCY C- TIDELINE; AUD ARE SUITABLE
_E rA REr(:)kL�N{.,_ IF [d,I�';, INS_. CAN ts.F' c:�F FURThEFt A?,._ISTf.NCF:
FLEA CALL.
SINCERELY,
Water & Waste Water Operation, Maintenance and Consulting
MSDEQ Class 4 — MSDOH Class A
October 13, 1994
Lab ID #
Sample
Description
Date
Received
Sample
Parameter
Result
4901
N401000CC
09/29/94
Nitrate
0.08 mg/I
4902
N401002CC
09/29/94
Nitrate
2.02 mg/1
4903
1003
09/29/94
Nitrate
1.95 mg/1
4904
N401006CC
09/29/94
Nitrate
0.12 mg/1
4905
1008
09/29/94
Nitrate
2.07 mg/1
4906
N401014CC
09/29/94
Nitrate
0.08 mg/1
4907
01033
09/29/94
Nitrate
1.37 mg/1
4908
01067
09/29/94
Nitrate
2.16 mg/1
4909
01069
09/29/94
Nitrate
2.01 mg/1
4910
01122
09/29/94
Nitrate
1.60 mg/1
THE TESTS PERFORMED ARE IN ACCORDANCE WITH STANDARD
METHODS 17TH EDMON.
LABORATORY STATEMENT OF QUALIFICATIONS AVAILABLE
ON REQUEST
SUBSURFACE TRICKLE- IRRIGATION SYSTEM
FOR ON -SITE
WASTEWATER DISPOSAL AND REUSE
Dr. B.L. Carlile P.E. Dr. A. Sanjines, Mech. E.
Cert. Prof. Soil Scientistt Geoflow, Inc. §
Summary of Process Description
The subsurface trickle irrigation system described in this report utilizes an
aerobic treatment system in conjunction with a proven subsurface water
application system developed by GEOFLOW, Inc. to offer a total system concept
for safe and effective sewage disposal for site conditions considered marginal
or unsuitable for conventional septic tank systems.
The integrated system described here is an improved dosing and
distribution concept compared to the low pressure pipe system, approved and
utilized in many states to overcome soil/site limitations. The proposed system is
also an effective irrigation system allowing reuse of treated wastewater in home
and lawn settings without the concerns of direct exposure of the effluent to
human and animal populations.
The system proposed is an integrated package consisting of several
components, each designed for a specific purpose in the treatment and
disposal of wastewater by trickle irrigation. including:
1. Primary treatment - the wastewater is first passed through a primary tank to
achieve physical settling of macro -solids and to assist in degradation of some
pollutants including oil and grease. This will be achieved in a septic tank for
home systems and a properly designed primary tank for larger flow systems
2. Secondary treatment - the primary effluent will be further treated in a
secondary treatment process by extended aeration in a Clearstream Aerobic
Treatment System that has been fully field and lab tested to show
achievement of effluent quality of better than 20 mg/I Biological Oxygen
Demand (BOD) and 20 mg/I Total Suspended Solids (TSS) at maximum
design flow.
3. Disinfection - the secondary effluent will be treated by chlorination ozonation
or ultra -violet radiation at adequate dosage to achieve disinfection of
pathogens to drinking water quality standards.
4. Filtration - the treated effluent in passed through a 150 mesh disc filter, with
manual or automatic backwash, prior to irrigation.
5. Subsurface irrigation - the relatively clean effluent is injected 6 to 10 inches
below the soil surface through trickle emitters located on 24 inch centers
throughout the disposal area. The effluent will be applied in several "pulses"
per day at rates not to exceed the water absorption capacity of the soil. A
typical system would be dosed 5 to 8 times per day at 50 gallons per dose. A
Carlile and Associates, Inc. PO Box 2677 College Station, TX 77841
Geoflow, Inc. Subsurface Irrigation. 236 W. Portal Ave, #327 San Francisco, CA 94127
submersible effluent pump with water level controls in a pump tank will be
used to control dosing volumes in most systems.
6. Economics - the estimated system cost will be slightly higher than a typical
low pressure pipe or surface irrigation disposal system. The subsurface
trickle system does offer a suitable irrigation system for lawns and landscape
beds whereas the low pressure pipe system cannot be considered an
efficient replacement for an irrigation system. While surface irrigation of
wastewater is limited to off -hours application to remote or low use areas of a
lot, the subsurface trickle irrigation system can be utilized for the entire high -
use lawn area even through some fresh make-up water may be required to
be added during peak water use months.
A schematic diagram of the treatment process is shown in Figure 1 and a
typical field layout of the trickle irrigation system is shown in Figure 2.
Introduction
Many homes, communities, businesses, and schools in rural United States
do not have access to public sewage treatment facilities and must treat and
dispose of the daily sewage flow through on -site disposal systems or by
wastewater treatment systems whose effluent flows to a receiving stream for
discharge.
In the past, the system most often chosen beeause it was the simplest and
cheapest to build was the conventional septic tank followed by soil trenches
filled with stone which served as underground storage reservoirs and
absorption surfaces for disposal of the sewage in the surrounding soil.
Because of site specific factors such as poor soils, high water tables and
excessive slopes, as well as the limitations of gravity distribution for large flows,
the conventional septic tank -soil absorption systems often malfunctioned after a
limited period of use.
Several alternatives have been developed and used for repair and
replacement of the conventional septic tank system for these poor site locations.
The major consideration in assessing the suitability of these alternatives for
such installation were:
1) simple and reliable - ability to operate over a long period without continuous
presence of a skilled operator
2) efficient - simple to install and efficient in operation with minimum
operational costs
3) environmental impact - health, aesthetic and water quality problems should
be minimized
4) costs - both installation and O & M costs should be within the range of current
alternatives available
5) potential for reuse - effluents from the system should have potential for reuse
for irrigation of lawns and shrubs with minimum impact on underlying
groundwater
The soil absorption systems developed and most utilized currently for these
fragile site installations include the low pressure pipe (LPP) system, and the
surface irrigation system. Each of these systems have specific site and soil
criteria where best utilized and require detailed site investigations for proper
2
Aerobic Chlorinator
unit
Wastewater
7
Septic oa
tank 8 °�` I
Air compressor Dosing
chamber
Figure 1. Pretreatment System
Flush line -,*,
Compresion adapter
Driplines
Emitters
Moisture" sensor
4,
(optional)
0 Header
line-.,
------------------------
Control valve
--
T
MOO-
000a
C3-
Treated
Screen
effluent
Filter Water meter
Pressure
Timer
I
(optional)
regulator
i '"-- Valve
- - - - - - - -
- - - - - - - - - - - -
- - - - -
- - - Box
Figure 2. Subsurface irrigation system
Sampling Treated
box Effluent
level To subsurface
switches drip system
. pump
L
Flush
valve
Valve box
GEOFLOW INC.
Subsurface Irrigation
Installation Detail
O
Cl)
L
'Ilkw
0
16-
r
cc
75
aCc
4)
4)
4)
Co
cc
0
CL
ca
cli
cc
4)
> >
ad
LL
in Co
design. It is proposed that the subsurface trickle irrigation system proposed
here is an improved and suitable replacement for both of the systems.
Soil Absorption System
The major factor in design of a satisfactory on -site waste disposal system for
poor soil conditions can be summarized as follows: 1) distribution, 2) dosing, 3)
sewage placement, and 4) improved pre-treatment and disinfection.
Distribution cannot be over -emphasized in the design of any on -site system
for "low perc" soils due to the need to spread sewage over large land areas.
The effluent must be distributed evenly over this large area so as not to exceed
the capacity of the soil to absorb the hydraulic load. Adequate distribution is
extremely hard, if not impossible, to achieve in any currently designed gravity
flow system. Some portion of the system is inherently overloaded which results
in initiation of the clogging phenomena and hence the "progressive failure"
observed in many such systems. Low pressure systems improve on the
distribution concept but have limitations in "low perc" soils in that trenches can
only be installed on 4 or 5 foot centers and the relatively high flow from drilled
orifices often result in effluent surfacing.
Dosing of effluent is equally important in maintaining the aerobic status of
the soil system in and around the distribution trench, thus preventing the
clogging or "slimming up" of soil interfaces and subsequent failure. Dosing
concepts can be described as either 1) short term dosing or 2) alternate dosing.
Short term dosing usually refers to multiply daily dosings of effluent into a
single system with several hours or sometimes days of resting and re -aeration
between each dose. Two to eight doses per day has been shown to be
satisfactory in systems designed for pressure dosing in either subsurface or
surface application.
Alternate dosing refers to dual or multiple fields where one part of field
receives all of the effluent for a specified period. at which time the effluent is
switched to the alternate plot. This can be done each pump cycle, once per day
or switched only when one field has a problem. Both short term and alternate
dosing is often utilized in trickle irrigation systems.
Both dosing concepts as well as combinations and modifications of the
above have been successfully utilized in several states to treat and dispose of
sewage from individual homes as well as cluster developments, school
systems, and mobile home parks with flows of up to 50,000 gpd.
The design factor of sewage placement refers to the concept of placing the
sewage in the soil zone or horizon most conducive to absorption, treatment, and
re -aeration. In soils with high water tables this usually means at least a one or
two foot separation between the seasonal water table and the point of sewage
injection. For soils with restrictive clay horizons or hardpans, the sewage should
be injected as high above the restrictive zone as possible. This minimum
separation allows for lateral or horizontal flow of effluent away from the
distribution trench or pipe before interception by the restrictive zone and allows
for more uniform absorption through the restricting layer. This, coupled with
enhanced treatment of the sewage in the better soils above the restrictive
horizon, greatly enhances the quality of effluent impacting the restrictive
3
horizon. Generally, water tables and restricting layers must be deeper than 36"
for conventional gravity systems to function adequately on such sites.
The final design factor is that of pre-treatment and disinfection. This factor
becomes most important on sites located on fragile conditions such as high
water tables and/or on soils having restrictive horizons near the surface. These
conditions result in the potential for effluent impacting groundwater or surface
water quality near the site location. If the soil treatment zone is not sufficient to
adequately treat the injected sewage flow, some pre-treatment and disinfection
must be utilized prior to soil disposal to offer needed protection of surface and
ground water resources.
System Design Parameters.
A. Primary and Secondary Pre-treatment -
Both primary and secondary pre-treatment will be afforded to the sewage
to achieve greater than 90 percent removal of suspended solids and organic
contaminants from the wastewater prior to disinfection and disposal.
Primary treatment will be by anaerobic treatment in an initial settling tank
with at least 1 day detention time. Primary treatment is both a physical and
biological process that achieves about 40% degradation of soluble BOD and
50 to 60% removal of solids by physical settling.
Secondary treatment may be by the aerobic process which applies the
principles of an aerobic environment to provide more rapid and complete
decomposition of organic waste material, greater reduction of pathogens,
and oxidation of nitrogen products as compared to an anaerobic
environment. A NSF Standard 40 Class I aerobic system that is properly
sized and maintained should provide an additional 85 to 90 percent removal
of BOD and TSS from the wastewater. As of November 26, 1991 specific
models from Aquarobic, Canada; Clearstream, TX; Klargester, FL; Multi -Flo,
OH; Nayadic Sciences, PA; and Norweco, OH are on the Official NSF List.
Table 1. Typical field data of effluent quality from
Clearstream* Home Aerobic Treatment Units.
No of
Location
Sam
BOD
TSS
pH
Fecal
Units
pies
(mg/1)
(mg/1)
colif.
/100ml
6
Orlando, FL
8
5.5
5.1
6.7
-
1
Rockwall, TX (Note 1)
3
3
10
7.5
21
1
Rockwall, TX (Note 2)
3
<3.0
<1
7.5
<3
1
NSF testing
120
5 -10
5- 10
7.2
-
Note 1) Before Ozonation
Note 2) After Ozonation
* Clearstream Wastewater Systems,. P.O. Box 705, Silsbee, TX 77656
El
Small individual home aerobic decomposition and treatment can be
accomplished at comparatively low cost through small mechanically aerated
treatment systems. The better small aerobic units are capable of producing
an effluent exceeding that of the most sophisticated municipal treatment
plants. Table 1 shows the summary of effluent quality from a two year
operational study of the Clearstream Aerobic Treatment System, field tested
at several homes in Florida and Texas and by extensive testing of the unit by
the National Sanitation Foundation, a national independent .testing agency.
The aerobic treatment unit described here treats the primary effluent by
extended aeration in a mechanically aerated contact chamber. The aerated
wastewater in the contact chamber is well mixed to provide optimum
exposure of the microorganism to the waste material. There is also a
significant reduction of pathogenic bacteria during this process. After
approximately 24 hours of aerobic contact, the activated wastewater is
clarified in a settling chamber and the settled solids returned to the aeration
chamber. The settled and clarified effluent is discharged from the settling
chamber through an improved design discharge assembly to minimize
solids carryover.
Aerobic treatment of domestic wastewater can be accomplished in other
ways. Sand filtration is a process sometimes used whereby the domestic
wastewater is first given primary treatment in a septic tank to reduce solids
and then applied intermittently to the surface of a sand bed of 2.5 to 3 foot
depth. An efficient sand filtration method is the recirculating sand filter (RSF).
The RSF offers a high degree of treatment with a minimum of maintenance
or nuisance problems. The RSF when loaded at a raw waste hydraulic
loading of 2.5-3.0 gal/ft2 per day produces a high quality effluent of similar
characteristics to that of the better aerobic treatment units. The slow rate,
intermittent sand filter, when designed at an hydraulic loading of 1.5 to 2
gal/ ft2 per day of septic tank effluent can also produce a high quality
effluent.
The choice between an aerobic system or a sand filter system depends
both upon the particular technical circumstances as well as local
regulations. We suggest that a Professional Engineer be consulted.
All treatment systems require routine systematic maintenance and the
successful long term operation of the system is dependent upon this
maintenance being correctly carried out.
B. Disinfection
The treatment by chlorination, ozonation, or UV radiation of the effluent
discharged from the aerobic cell represents the final step of a "safe" pre-
treatment system designed to allow maximum reuse of the wastewater in a
landscape mode. The potential of ozonation for deactivating viruses and
bacteria, detoxifying organic compounds and oxidizing any odorous
components make it the logical choice for systems installed in lake shore
settings or in extremely high groundwater conditions.
Ozone concentration in very low amounts and at very short contact time
is capable of disinfecting and deodorizing the effluent. This process has
only recently been utilized for home waste treatment due to the high
installation and operation costs of ozonation systems.
5
C. Final Treatment and Reuse by Subsurface Irrigation
Decentralizing the treatment process and producing a safe effluent at the
point of generation makes reuse an attractive activity. Reusing aerobic,
disinfected wastewater instead of potable water for non -potable uses like
lawns, flower -bed and shrubbery sub -irrigation reduces the effective cost of
the system and can lead to significant reduction in per capita demands for
potable water supplies. Applying wastewater to the soil is in itself a very
effective treatment process. There are many chemical, biological and
physical processes that occur in the soil that substantially improve the
quality of wastewater (1, 11, 12).
Trickle Emitter Design
A reliable subsurface trickle irrigation system for wastewater combines the
advantages of high irrigation efficiency and water economy with that of safe
underground application.
The major concern and problem with drip or trickle irrigation has always
been the risk of clogging of emitters, even when using clean well -water. This
has resulted in the design and use of relatively larger diameter outlets in the
emitters. However, by using larger outlet emitters in subsurface drip systems,
root intrusion became the main constraint. Roots seeking moisture and
nutrients have been shown to enter drip irrigation lines and block them in the
same manner they enter sewer pipes (2). `
Because of the amount of impurities associated with wastewater and the
potential for bacterial growth in the lines, the constraints of emitter blockage is
quite real and must be addressed. To minimize this problem, the emitters
should have relatively large diameter outlets. GEOFLOWTM has developed an
emitter with "turbulent flow long path" design that has the largest flow area for a
given flow rate of any emitters in use today. These emitters operate at a flow
rate of 1 to 2 GPH with 0.06 to 0.07 inch orifices.
To inhibit the growth of bacterial slimes on the walls of the trickle irrigation
lines GEOFLOWTM incorporates a bactericide into the tube material. The tube
with bactericide is purple in color to indicate non -potable water.
To solve the problem of root intrusion, the ROOTGUARDO 1 process was
developed. This is an exclusive GEOFLOWTM process by which an
environmentally safe herbicide (TREFLAN02 )is compounded into the emitters
to protect them from root intrusion for many years. The quantities of herbicide
used are very small since only a small area around the emitter orifice has to be
protected. Because of the very limited movement of ROOTGUARD in the soil
and its virtual insolubility in water, only the roots that try to enter the emitter
orifice will be inhibited.
The turbulent flow emitters used by GEOFLOW in the proposed wastewater
systems are made out of polypropylene and polyethylene and are resistant to
most acids and substances likely to be found in domestic wastewater. The
pre-
ROOTGUARD® is a registered Agrifim Irrigation trade mark. The ROOTGUARD
technology is used under license from the Battelle Memorial Institute.
TREFLAN®is a trademark of Dow- Elanco
on
treatment unit with disinfection designed in conjunction with the system should
keep the bacterial slimes under control in the system and the 150 mesh disc
filter installed in -line of the header should remove any extraneous solids which
might be of size to plug the emitter orifice.
All these components integrated into a reliable sub -irrigation system makes
this a unique process for domestic waste disposal. Other systems of a similar
nature are being promoted and used in some southeastern states. One such
system utilizes a rubber diaphragm pressure compensating emitter. The rubber
diaphragm reduces the outlet orifice during operation, making it highly
susceptible to clogging. Even though the orifice opens when pressure is off, the
chances of intermittent plugging with bacterial slimes are quite high.
A rubber diaphragm is susceptible to attack by oil, gasoline products and
oxidizing agents, resulting in a likely change in the physical characteristics of
the rubber overtime and thus affecting the uniformity of flow in the emitters.
Deposits also tend to build up at the seat of the diaphragm over time, changing
the flow characteristics of the emitter.
These pressure compensating emitters are not protected against root
intrusion and is susceptible to plugging by roots (2). Only the GEOFLOW
emitter protected by ROOTGUARDO can offer positive protection against a very
serious threat of root plugging.
Soil Application Design
The instantaneous water application rate of the system must not exceed the
water absorption capacity of the soil. A determination of the instantaneous
water absorption capacity of the soil is difficult, however, since the value varies
with the water content of the soil. As the soil approaches saturation with water,
the absorption rate reduces to an equilibrium rate called the "saturated
hydraulic conductivity." Wastewater application rates should be less that 10
percent of this saturated equilibrium
Even though the trickle irrigation system maximizes the soil absorption rate
through the low rate of application, thus keeping the soil below saturation, there
will be times when the soil is at or near saturation from rainfall events. The
design must account for these periods and assume the worst case condition of
soil saturation. By designing for a safety factor of 10 or 12, based on the
saturated hydraulic conductivity, the system will be under -loaded most of the
time but should function without surface failure during extreme wet periods.
Using a safety factor of 12, a suitable design criteria would be to load the
system at the estimated hydraulic conductivity but apply water for only a total of
2 hours per day out of the available 24 hours. By applying wastewater for a
total of 2 hour per day, particularly if applied in "pulses" or short doses several
times per day near the soil surface were the soil dries the quickest, this would
keep the soil absorption rate at the highest value and minimize the potential of
water surfacing on poor soil conditions.
As stated previously, this design criteria will under -load the system at all
times except when the soil is at or near saturation from rainfall. If designing for
an efficient irrigation system, the water supply may not be sufficient to meet the
demands of a lawn or landscaped area during peak water demand months.
This problem can be overcome by either of two solutions: add additional fresh-
7
water make-up to the system during the growing season to supply the needed
water for plants in question; or split the system into two or more fields with
necessary valves and only use one of the fields during the peak water demand
months and alternate the fields during winter months or extremely wet periods
Table 2 shows the recommended hydraulic loading rates for various soil
conditions, using a safety factor of 12 with regard to the equilibrium saturated
hydraulic conductivity rate of the soil.These loading rates assumes a treated,
disinfected effluent with BOD and TSS values of less than 20 mg/I is produced
in the pre treatment system.
Table 2. Minimum surface area required to dispose of 100 gpd
Soil absorption rates
Design
Total
Soil
Est.Soil
Hydraulic.
Hydraulic
Area
type
Perc.
Conduc-
Loading
required
rate
tivity.
rate
ft2 / 100gal
min/in
in/hr
gal / ft2-day
per day
Coarse- sand
<5
>2
2.0
52
Fine sand
5-10
1.5-2
1.6
6
Sandy loam
10-20
1.0-1.5
1.3
—iaat�
20-30
0.75-1.0
0.9
115
Clay loam
30-45
0.5-0.75
6.6
175
Silt -clay loam
45-60
0.3-0.5
0.4
260
Clay non -swell
60-90
0.2-0.3
0.2
520
Clay - swell
90-120
0.1-0.2
0.1
1040
Poor clay
>120
<0.1
0.075
1380
System Installation
Pre-treatment System
For individual home systems, a 500 gallon septic tank and an aerobic
treatment system of 500 gallons per day capacity is generally used for homes of
4 bedrooms or less. For larger homes, a 600 - 750 gallon per day aerobic unit
should be used.
After primary and secondary treatment, disinfection is the next step to reduce
pathogen levels in the effluent and minimize bacterial growth in the field lines
and emitters. The usual treatment to control bacterial slime growth is
chlorination on a continuous basis to achieve a residual concentration of 1-2
mg/I. If ozone or UV disinfection is used, which have no residual effect in the
lines, then chlorine should be applied on an intermittent basis at a rate of 10-20
mg/I just before the system is finished dosing the last dose of the day.
Chlorine may be introduced into the system either as liquid, solid or gas
forms. For home systems, the liquid or solid form is more appropriate. Since
calcium hypochlorite tablets may flake when dissolving and chlorine may cause
some iron and manganese precipitation, it is better to chlorinate ahead of the
final filter so that any particulates are removed.
Pump Tank and Controls
Dosing and irrigation supply will be by a submersible effluent pump located
in a 150-300 gallon storage tank. The operation of the pump will be by a simple
float on -off level switch in the tank. The "on" level switch will activate the pump
when the tank reaches a high water mark and the low level switch will turn the
pump off when the tank reaches a predetermined minimum water level. For a
typical system this volume would be 50-100 gallons. For a 250 to 500 GPD
system, this results in 3 to 10 irrigation pulses per day. For systems on sloping
ground where water drains from the pipes to the lower points of the system after
each pulse or dose, larger doses and fewer pulses per day would be more
suitable. Irrigation uniformity is best maintained with irrigation pulses of 10
minutes or more.
Filter Requirements
The recommended disc filter uses a 150 mesh screen that filters out particles
larger than about 100 microns. The type of emitter used in GEOFLOW trickle
systems will not have problems with this particular size since the diameter of the
flow path is 14 to 17 times larger, or 0.056 inches (1400 microns) for the 1 GPH
emitter to 0.08 inches (2,000 microns) for the 2 GPH emitter. To maintain the
proper water quality for the drip system, the filters are easily backwashed
manually or equipped with automatic back flush triggered by a timer or a
pressure differential switch. The installation schematic of the in -line filter is
shown in the typical system lay -out. `
Flow Regulator
Under normal conditions, the pressure in the trickle lines should be
maintained between 20 and 25 psi during operations. This is controlled by a
pressure regulator located in -line following the filter. The emitter lines are
connected at each end by a PVC header line and flush line to allow optimum
pressure equilibrium in the system. Flush /vacuum release valves are located
at each end of these lines to allow a small amount of water to be automatically
flushed from the system every time it is started and avoid dirt suck back when
the system is switched off. This is important to prevent solids from accumulating
at the ends of these lines and to prevent dirt from entering the lines.
The schematic of a typical field layout of the trickle irrigation system shows
only a single field. For systems over 2000 ft in size or having over 500 emitters,
the system would be split into 2 or more fields of equal size. Flow for a dual
field system would be alternated through the use of a mechanical valve which
automatically switches fields each time the pump is activated.
For systems with more than 2 fields, the operation of each field is controlled
with an irrigation controller utilizing electric solenoid valves for each field
station. By separating the system into several fields, smaller pumps and more
uniform distribution can be achieved. Where soil conditions vary, some fields
may be programmed to receive less water than other fields of the system .
Trickle Emitter Lines
A normal home system would have emitter lines placed on 2 foot centers
with a 2 foot emitter spacing such that each emitter supplies a 4 ft area (Fig. 3).
These lines are best placed at depths of 6-10 inches below the surface. This is
0
a typical design for systems on sandy and loamy soils which will have a cover
crop of lawn grass. Other line spacing may be used for special use situations
such as for landscape beds where shrubs and trees are to be watered and are
planted on an irregular spacing. Closer line spacings of 15 to 18 inches can be
used on clay soils where lateral movement of water is restricted.
The shallow depth of installation is an advantage of the trickle irrigation,
system since the topsoil or surface soil is generally the most permeable soil for
accepting water. The topsoil also dries the fastest after a rainfall event and will
maintain the highest water absorption rate. Where restrictive horizons such as
hardpans or claypans are present or sites with seasonal high water tables near
the surface, shallow placement allows the dispersement of water above these
zones. Where fill material is used to increase the soil depth on such problem
sites, the trickle emitter lines can be laid on the original soil surface and the fill
material carefully placed over the lines.
Table 3. Water application table for a 1 Gallon/hour emitter
Water application (inches of water per hour)
Emitter
spacing (in)
12
15
Drip line spacing (inches)
18 24 36 48
60
12
1.60
1.28
1.07 ;
0.80
0.53
0.40
0.32
15
1.28
1.03
0.86
0.64
0.43
0.32
0.26
1 8
1.07
0.86
0.71
0.53
0.36
0.27
0.21
24
0.80
0.64
0.53
0.40
0.27
0.20
0.16
36
0.53
0.43
0.36
0.27
0.18
0.13
0.11
48
0.40
0.32
0.27
0.20
0.13
0.10
0.08
60
0.32
0.26
0.21
0.16
0.11
0.08
0.06
All trickle irrigation systems are dependent on a good vegetative cover to
prevent erosion from the field and utilize the water applied to the rooting zone.
Sites should be quickly sodded or seeded and mulched with appropriate lawn
grasses immediately after installation. Most lawn grasses will use 0.25 to 0.35
inches of water per day during the peak growing season. This calculates to be
about 0.16 to 0.22 gal/ft2 /day, a significant part of the daily effluent loading. By
overseeding lawns with winter ryegrass, this use efficiency can be continued
through much of the year.
For vegetation using 0.16 to 0.22 gal/ft2 /day by evapo-transpiration, the
typical home sewage flow of 250 gallons per day would supply the water needs
of a landscaped area of 1150 to 1600 sq. ft. without having to add fresh make-
up water. For systems larger than this, the plants will suffer water stress during
the hot dry months unless additional fresh water is applied.
To determine the rate of water application from various trickle irrigation
designs, Table 3 gives the rate for a 1 gph emitter at various line and emitter
spacings. These values assume the water is equally distributed between the
emitters.
10
1511-95 Tax#1941-341-01-004
NAME 549 Big Dipper .Rd. RANIERI aOB N©.
Bellyache Ridge
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A (2o-lo-��,�-l��l �
1-//S/� S'0SI
INDIVIDUAL SEWAGE DISPOSAL SYSTEM PERMIT
EAGLE COUNTY ENVIRONMENTAL HEALTH DIVISION
P.O. Box 179 - 500 Broadway • Eagle, Colorado 81631
Telephone: 328-8755
YELLOW COPY OF PERMIT MUST BE POSTED AT INSTALLATION SITE. PERMIT NO. 1 5 1 O
Please call for final inspection before covering any portion of installed system.
owNER: Stephen Armstrong
PHONE: (970) 926-2025
MAILING ADDRESS: P.O. BOX 3568 City: Vail dada: CO ZIP: 81658
APPLICANT: Stephen Armstrong PHONE: (970) 926-2025
SYSTEM LOCATION: 549 Big Dipper Rd Bellyache TAX PARCEL NUMBER: 1941-341-01-005
LICENSED INSTALLER: Long's Excavation LICENSE NO: 42-95
DESIGN ENGINEER OF SYSTEM: Hank Danle /White Water Systems, SU�,,,,,,4S�vs�ynC
INSTALLATION HEREBY GRANTED FOR THE FOLLOWING:
980 GALLONTANK* White Water Aerobic Treatment, plus 500 gallon dosing tank
ABSORPTION AREA REQUIREMENTS:
800 SQUARE FEET ePOES-A=E-eE6----------seFihREFE-Etef'TfteN&twwtom-absorption area via drip irrigation
SPECIAL REQUIREMENTS: 1. Field verify 4' separation to bedrock, 2 Representative of Summit Sewers,
Inc. must be present during installation, 3. Submit maintenance agreement to Eagle County
Environmental Health up om e n of em, Install as per engineer's design.
ENVIRONMENTAL HEALTH APPROVAL; DATE: August 16.1995
CONDITIONS:
1. ALL INSTALLATIONS MUST COMPLY WITH ALL REQUI EN' E EAGLE COUNTY INDIVIDUAL SEWAGE DISPOSAL SYSTEM REGULATIONS, ADOPTED PURSUANT
TO AUTHORITY GRANTED IN 25- 10- 104. 1973. AS AMENDED.
2. THIS PERMIT IS VALID ONLY FOR CONNECTION TO STRUCTURES WHICH HAVE FULLY COMPLIED WITH COUNTY ZONING AND BUILDING REQUIREMENTS. CONNECTION
TO OR USE WITH ANY DWELLING OR STRUCTURE NOT APPROVED BY THE ZONING AND BUILDING DEPARTMENTS SHALL AUTOMATICALLY BE A VIOLATION OF A
REQUIREMENT OF THE PERMIT AND CAUSE FOR BOTH LEGAL ACTION AND REVOCATION OF THE PERMIT.
3. CHAPTER IV, SECTION 4.03.29 REQUIRES ANY PERSON WHO CONSTRUCTS, ALTERS OR INSTALLS AN INDIVIDUAL SEWAGE DISPOSAL SYSTEM TO BE LICENSED.
FINAL APPROVAL OF SYSTEM: (TO BE COMPLETED BY INSPECTOR):
NO SYSTEM SHALL BE DEEMED TO BE IN COMPLIANCE WITH THE EAGLE COUNTY INDIVIDUAL SEWAGE DISPOSAL SYSTEM REGULATIONS UNTIL THE SYSTEM IS APPROVED
PRIOR TO COVERING ANY PORTION OF THE SYSTEM.
INSTALLED ABSORPTION OR DISPERSAL AREA: SQUARE FEET.
INSTALLED SEPTIC TANK: GALLON DEGREES FEET FROM
SEPTIC TANK ACCESS TO WITHIN 8" OF FINAL GRADE AND
PROPER MATERIAL AND ASSEMBLY YES _ NO
COMPLIANCE WITH COUNTY / STATE REQUIREMENTS: YES _ NO
ANY ITEM CHECKED NO REQUIRES CORRECTION BEFORE FINAL APPROVAL OF SYSTEM IS MADE. ARRANGE A RE -INSPECTION WHEN WORK IS CORRECTED.
COMMENTS:
ENVIRONMENTAL HEALTH APPROVAL: DATE:
ENVIRONMENTAL HEALTH APPROVAL: DATE:
(RE -INSPECTION IF NECESSARY)
APPLICANT / AGENT:
RETAIN WITH RECEIPT RECORDS
OWNER:
PERMIT FEE PERCOLATION TEST FEE RECEIPT # CHECK #
Incomplete Applications Will NOT Be Accepted �519 _# /15 /0 -N61Wj A"Lf-
(Site Plan MUST be attached)
ISDS Permit. #77,
Building Permit # ,w//�- )17.
APPLICATION FOR INDIVIDUAL SEWAGE DISPOSAL SYSTEM PERMIT
ENVIRONMENTAL HEALTH OFFICE.- EAGLE COUNTY
P. O. BOX 179
EAGLE, CO 81631
328-8755/927-3823 (Basalt)
**************************************************************************
* PERMIT APPLICATION FEE $150.00 PERCOLATION TEST FEE $200.00
* MAKE ALL REMITTANCE PAYABLE"JTO: "EAGLE COUNTY TREASURER"
PROPERTY OWNER: .� e � l� � A v- � vo� a
MAILING ADDRESS:
APPLICANT/CONTACT PERSON:
J 6 V cl� j co 2(6SI PHONE:
PHONE:
LICENSED SYSTEMS CONTRACTOR: %/� ter, r.,. e� PHONE:
COMPANY/DBA: ADDRESS:
PERMIT APPLICATION IS FOR: ( ) NEW INSTALLATION ( ) ALTERATION (REPAIR
LOCATION OF PROPOSED INDIVIDUAL SEWAGE DISPOSAL SYSTEM: (� p
Legal Description: ,0/0 QF� Lkyc A Fus DC40tey lol d,? RP � ��ta C � ,A;
Tax Parcel Number: lq of % " 3 4I" ^ O 1 Lot Size:
Physical Address:
I B 1
BUILDING TYPE:. (Check applicable category)
(r� Residential/Single Family
( ) Residential/Multi-Family*
( ) Commercial/Industrial*
Number of Bedrooms
Number of Bedrooms
Type
3
TYPE OF WATER SUPPLY: (Check applicable category)
( ) Well ( ) Spring ( ) Surface �+
(�) Public Name of Supplier: s t O-Q (A "Me S4
*These system require design by a Registered Professional Engineer
SIGNATURE: Date:�G��_
************ ** **********************************************************
AMOUNT PAID: ��� ` RECEIPT #: DATE.
CHECK #: '% If CASHIER:
Community Development Department
(970)328-8730
Fax: (970) 328-7185
TDD: (970) 328-8797
EAGLE COUNTY, COLORADO
September 11, 1995
Stephen Armstrong
P.O. Box 3568
Vail, CO 881658
Eagle County Building
P.O. Box 179
500 Broadway
Eagle, Colorado 81631-0179
RE: Final of ISDS Permit No. 1510-95 Parcel #1941-341-01-005.
Property located at: 549 Big Dipper Rd., Bellyache Ridge.
Dear Mr. Armstrong,
This letter is to inform you that the above referenced ISDS
Permit has been inspected and finalized. Enclosed is a copy to
retain for your records. This permit does not indicate
compliance with any other Eagle County requirements. Also
enclosed is a brochure regarding the care of your septic system.
Be aware that later changes to your building may require
appropriate alterations of your septic system.
If you have any questions regarding this permit, please contact
the Eagle County Environmental Health Division at 328-8755.
Sincerely,
Janet Kohl
Environmental Health Department
ENCL: Information Brochure
Final ISDS Permit
enclosures
EAGLE COUNTY, COLORADO
Date: August 16, 1995
TO: Long's Excavation
FROM: Environmental Health Division
RE: Issuance of Individual Sewage Disposal System
Permit.No. 1510-95 Tax Parcel #1941-341-01-005
Property Location: 549 Big Dipper Rd., Bellyache
Ridge, Armstrong residence.
Enclosed is your ISDS Permit No. 1510-95.It is valid for 120
days. The enclosed copy of the permit must be posted at the
installation site. Any changes in plans or specifications
invalidates the permit unless otherwise approved. Please call
our office well in advance for the final inspection.
Systems designed by a Registered Professional Engineer must be
certified by the Engineer indicating that the system was
installed as specified. Eagle County does not perform final
inspections on engineer designed systems. Engineer as-builts must
be submitted for permit to be finalized and T.C.O. issued.
Permit specifications are minimum requirements only, and should
be brought to the property owner's attention.
This permit does not indicate conformance with other Eagle County
requirements.
If you have any questions, please feel free to contact the
Environmental Health Division at 328-8755.
cc: files
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 328.8730
EAGLE COUNTY, COLORADO
August 4, 1995
Mr. Stephen Armstrong
P.O. Box 3568
Vail, CO 81658
RE: Enforcement of the Cease and Desist Order
Dear Mr. Armstrong,
P.O. BOX 179
EAGLE, COLORADO 81631
FAX (303) 328-7207
Due to logistics involved with your desire to install a different
wastewater treatment technology than was originally specified, I have
chosen not to enforce the Cease and Desist Order until August 25, 1995. It
is important to understand that the Order is not being lifted or extended.
It is my understanding that Keith Gilbert, Summit Sewers, Inc., will be
installing his company's technology and that Hank Danley is the Registered
Professional Engineer designing the system. Mr. Gilbert informed me that
he was obligated to go to Venezuela for the oil company he works for and
that Mr. Danley had a death in the family which would delay the submittal
of the design for a few days. I also understand that you have chosen
Long's Excavation, Inc. to install the system under the supervision of Mr.
Gilbert. If Long's Excavation is not your Licensed Systems Contractor,
please advise me, in writing, who you are selecting no later than August
11,.1995.
Please be advised that ISDS Permit #1510, will be conditioned by there
being a maintenance agreement to assure long-term performance of this
system. If there are any further questions regarding this correspondence,
please call my office at (970) 328-8755.
Sincerel
Raymo P. Mer , REHS
Envir nmental Hea Ma ger
cc: Robert W. Loeffler, Attorney
Keith P. Montag, Director of Community Development
ISDS File #1510
08/14/95 08:31 TRUSWAL SYSTEMS 4 SUMMIT SEWER SYSTEM
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT
3M COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179 y,
500 BROADWAY
.EAGLE, CO 81631
RIFF: SEWER SYSTEMS FOR LOT #27, BELLY
EAGLE COUNTY, CO,
DRIP FIELD LAYOUT:
N0.249 P001
Telef3hone 719-395-6S37
®� FOX 719-395-6537
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SUBDIVISION,
UTILIZING ENGINEERING AND TEST DATA PERFORMED BY INTER-
MOUNTAIN ENGINEERING (SEE ATTACHED BLUE PRINTS) , THE
FOLLOWING DESIGNED AEROBIC SYSTEMS SHOULD BE PLACED IN
AREAS DESIGNATED BY THE BLUE PRINTS.
3 BEDROOMS @ 150 GAL. EACH X 150% = 675 GPD. (EACH UNIT)
SET DRIP FIELDS TO DOSE 10 MINUTES EVERY 2 HOURS (60 GAL/DOSE),
120 MINUTES OF DOSING PER DAY, (ASSUMING FLOAT SWITCH IS AT
DOSING LEVEL).
EACH EMITTER WELL HANDLE 1.5 GPH @ 25 PSI.
675 GPD/(1.5 GPH (2 HOUR. DOSING/DAY)) — 225 EMITTERS. WITH 2 FT.
OF SPACING BETWEEN EMITTERS, 450 FT. OF DRIPLINE WILL SUPPLY
225 EMITTERS.
AS PER INTER -MOUNTAIN ENGINEERING, THE NATIVE SOIL CONSISTS
OF COARSE TO FINE SILTY SAND. WITH A HYDRAULIC LOADING RATE
OF 1.3 TO 1.6 GAL/SQ.FT./DAY, 80 SQ.FT./100 GAL/DAY IS REQUIRED FOR
TOTAL H2O ABSORPTION.
6.75 X 80 = 540 SQ/FT.
WITH 9 RUNS OF DRIPLINE @ 50 FT/RUN, SPACED 2 FT. APART
TOTAL SURFACE AREA = 800 SQ/FT.
HYD, LOADING FOR SANDY LOAM = 1.3 GAL / SQ/FT / DAY. W/ $00 SQ/FT
AND 675 GPD, HYD. LOADING = 1.19 GAL / SQ/FT /DAY.
rlVnl. nCllnlUVU JCnivI-1-1 ...-w .. YGCMQTO I CWIO,IIW.. rax. 11,7�gj vuiuu; riwWp W1 10.R lHICRRT a[: CAbLC 6U. CIVYIn. MAL IN Page 4%Or0 I Uesaay, AUQU8T lb," NM U:JU:02 AM
08/14/95 09:31 TRUSWAL SYSTEMS 4 SUMMIT SEWER SYSTEM N0.249 P002
NTMIMT
MrA ��T?'� T58 BY PLOWING UNDER EXISTING GRADE. BEGIN
BUILDING MOLND UP TO LT ABOVE EXISTING GRADE USING NATIVE
SOIL. BED DRIP GRID (9 RUNS, 50' EACH, PLACED 2' APART) IN 2" OF
SAND (ANY SIZE). COVER WITH I OF NATIVE FILL. PLACE 2" BED OF
STRAW AND COVER WITH 2' OF NATIVE FILL.
FAST ITNrrt STEVEN A IR G-RESMMr
PREPARE STTE.22' X 56' BY EXCAVATING 1' TO 2' OF EXISTING GRADE,
BEGDTA% TC AT TEST PIT 4 AND E2.TDIn-go i5nrropLb 1IGJ"! Yl'1 J. NL() W NEW
BOTTOM. CENTER DRIP GRID (9 RUNS, 50' EACH, PLACED 2' APART) IN
EXCAVATION AND BED WITH 2" OF SAND (ANY SIZE). COVER WITH 1' OF
NATIVE FILL. PLACE 2" BED OF STRAW AND COVER WITH 21 OF NATIVE
FILL.
DRIP GRID TO BE USED ONLY WITH THE WHITEWATER AEROBIC
TREATMENT PLANT INSTALLED AS PER MANl'UFACTUREP'e
INSTALLATION INSTRUCTIONS.
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Community Development Department
(970)328-8730
Fax: (970) 328-7185
TDD: (970) 328-8797
EAGLE COUNTY, COLORADO
September 27, 1995
Mr. Stephen Armstrong
P.O. Box 3568
Vail, CO 81658
Dear Mr. Armstrong,
Eagle County Building
P.O. Box 179
500 Broadway
Eagle, Colorado 81631-0179
The Environmental Health Division is awaiting information on the
proper closure of the old septic system in order to finally
approve the repair to your Individual Sewage Disposal System
Permit #1399.
Eagle County Land Use Regulation 4.15.07 states "The contents of
a septic tank, vault, or seepage pit, the use of which has been
terminated, shall be properly disposed of as required in Section
4.15.05 whereupon the emptied tank, vault, or pit shall be filled
with rock or soil.
This means the old tank must be pumped by a licensed pumper, then
filled with dirt or rock. By the way, the executed maintenance
agreement between you'and Summit Sewers, Inc., has been recieved
by this office and has been recorded with the property deed.
Should you have any questions, please call this office at (970)
328-8755.
Sincerely,
Raymond P. Merry, REDS
Environmental Health Division Manager
cc: Robert W. Loeffler, Assistant County Attorney
Keith P. Montag, Director of Community Development
ISDS Permit File #1399
From: KEITH AND JENNY GILBERT SUMMIT SEWER SYSTEMS, INC. Fax: 719396b637 Voice: 719396-6537 To: HANK DANLEY Page 2 of2 Friday, September 01, 19% 9:41:19 AM
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
33305 COUNTY RD 361 Fax 719-395-6537
BUENA VISTA, CO 81211
EAGLE COUNTY ENVIRONMENTAL HEALTH DEPT.
ATTN: RAY MERRY
P.O. BOX 179
EAGLE, CO 81631
REF: SEWER SYSTEMS FOR LOT #27, BELLYACHE RIDGE SUBDIVISION
EAGLE CO., CO.
EAST UNIT: STEVE ARMSTRONG
WEST UNIT: RICHARD RANIERI
THIS IS TO CERTIFY THAT THE WHITEWATER AEROBIC SEWER
TREATMENT SYSTEMS HAVE BEEN INSTALLED IN ACCORDANCE WITH
THE ENGINEER'S DESIGN AND THE MANUFACTURER'S INSTALLATION
GUIDLINES. IF ANY ADDITIONAL INFORMATION IS REQUIRED, PLEASE
FEEL FREE TO CONTACT ME.
SINCERELY,
KEITH GILBERT-
SUMMIT SEWER SYSTEMS, INC.
s
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
Fax 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179
500 BROADWAY
EAGLE, CO 81631
REF: SERVICE CONTRACT FOR LOT #27, BELLYACHE RIDGE
SUBDIVISION
EAGLE COUNTY, CO.
[VA-1111RiLl_I M-1
SUMIVIIT SEWER SYSTEMS, INC. WILL PROVIDE STANDARD MONTHLY
MAINTENANCE SERVICES FOR THE WHITEWATER AEROBIC SEWER
SYSTEMS INSTALLED AT THE ABOVE LOCATION AT NO CHARGE TO THE
HOMEOWNER.
THE STANDARD MAINTENANCE INCLUDES:
- CLEANING OF COMPRESSOR AIR FILTER
- CYCLING TIMER MECHANISM
- INSPECTING DRIPFIELD
- FLUSHING DRIPFIELD (BI-ANNUALLY)
- PERFORMING 4 BI-ANNUAL SAMPLINGS FOR SOLIDS CONTENT
ALL OPERATING EXPENSES OR REPLACEMENT ITEMS NOT COVERED
UNDER MANUFACTUERERS WARRANTY WILL BE THE RESPONSABILITY
OF THE HOMEOWNER. (IE. ELECTRICAL EXPENSE, PUMP -OUT FEES,
ETC.)
IF THE OWNERSHIP OF THE UNIT CHANGES HANDS, THIS CONTRACT
SHALL BE NULL AND VOID, AND A NEW CONTRACT MUST BE SIGNED
BY THE NEW OWNERS AS PART OF THE SALE OF THE PROPERTY. A FEE
SHALL BE CHARGED TO THE NEW OWNERS FOR SAID CONTRACT. THE
FEE WILL BE OF A STANDARD RATE EQUIVALENT TO THE COST OF
SIMILAR CONTRACTS AT THE TIME THE NEW CONTRACT IS WRITTEN.
ITH GI .BERT fT-ETN ARMSTRONG
SUMHT SEWER SYSTEMS, INC.
YOUR LOCAL DISTRIBUTOR
SUMMIT SEWER SYSTEMS, INC.
KEITH & JENNY GILBERT
(719) 395-6537
SUBSURFACE TRICKLE IRRIGATION SYSTEM
FOR ON -SITE
WASTEWATER DISPOSAL AND REUSE
Dr. B.L. Carlile P.E. Dr. A. Sanjines, Mech. E.
Cert. Prof. Soil Scientistt Geoflow, Inc. §
Summary of Process Description
The subsurface trickle irrigation system described in this report utilizes an
aerobic treatment system in conjunction with a proven subsurface water
application system developed by GEOFLOW, Inc. to offer a total system concept
for safe and effective sewage disposal for site conditions considered marginal
or unsuitable for conventional septic tank systems.
The integrated system described here is an improved dosing and
distribution concept compared to the low pressure pipe system, approved and
utilized in many states to overcome soil/site limitations. The proposed system is
also an effective irrigation system allowing reuse of treated wastewater in home
and lawn settings without the concerns of direct exposure of the effluent to
human and animal populations.
The system proposed is an integrated package consisting of several
components, each designed for a specific purpose in the treatment and
disposal of wastewater by trickle irrigation. including:
1. Primary treatment- the wastewater is first passed through a primary tank to
achieve physical settling of macro -solids and to assist in degradation of some
pollutants including oil and grease. This will be achieved in a septic tank for
home systems and a properly designed primary tank for larger flow systems
2. Secondary treatment - the primary effluent will be further treated in a
secondary treatment process by extended aeration in a Clearstream Aerobic
Treatment System that has been fully field and lab tested to show
achievement of effluent quality of better than 20 mg/I Biological Oxygen
Demand (BOD) and 20 mg/I Total Suspended Solids (TSS) at maximum
design flow.
3. Disinfection - the secondary effluent will be treated by chlorination ozonation
or ultra -violet radiation at adequate dosage to achieve disinfection of
pathogens to drinking water quality standards.
4. Filtration - the treated effluent in passed through a 150 mesh disc filter, with
manual or automatic backwash, prior to irrigation.
5. Subsurface irrigation - the relatively clean effluent is injected 6 to 10 inches
below the soil surface through trickle emitters located on 24 inch centers
throughout the disposal area. The effluent will be applied in several "pulses"
per day at rates not to exceed the water absorption capacity of the soil. A
typical system would be dosed 5 to 8 times per day at 50 gallons per dose. A
Carlile and Associates, Inc. PO Box 2677 College Station, TX 77841
§ Geoflow, Inc. Subsurface Irrigation. 236 W. Portal Ave, #327 San Francisco, CA 94127
Aerobic Chlorinator
unit
Wastewater /
Septic
tank
Air compressor
Figure 1. Pretreatment System
Flush line -*,
Compresion adapter
Sampling
box
level
switches
pump
Dosing
chamber
Driplines
Emitters
Moisture
sensor
\41 74,
(optional)
0
0
.1
Header
line_,
------------------
Control valve ------
-- T
e0000 co
M C3=
Treated
screen
000a
effluent
Filter Water meter
Timer
Pressure
(optional)
regulator Valve
— — — — — — —
— — — — — — —
— — — — — — — — Box
Figure 2. Subsurface irrigation system
Treated
Effluent
—0-
To subsurface
drip system
L
Flush
valve
Valve box
�7
GEOFLOW INC.
Subsurface Irrigation
Installation Detail
design. It is proposed that the subsurface trickle irrigation system proposed
here is an improved and suitable replacement for both of the systems.
Soil Absorption System
The major factor in design of a satisfactory on -site waste disposal system for
poor soil conditions can be summarized as follows: 1) distribution, 2) dosing, 3)
sewage placement, and 4) improved pre-treatment and disinfection.
Distribution cannot be over -emphasized in the design of any on -site system
for "low perc" soils due to the need to spread sewage over large land areas.
The effluent must be distributed evenly over this large area so as not to exceed
the capacity of the soil to absorb the hydraulic load. Adequate distribution is
extremely hard, if not impossible, to achieve in any currently designed gravity
flow system. Some portion of the system is inherently overloaded which results
in initiation of the clogging phenomena and hence the "progressive failure"
observed in many such systems. Low pressure systems improve on the
distribution concept but have limitations in "low perc" soils in that trenches can
only be installed on 4 or 5 foot centers and the relatively high flow from drilled
orifices often result in effluent surfacing.
Dosing of effluent is equally important in maintaining the aerobic status of
the soil system in and around the distribution trench, thus preventing the
clogging or "slimming up" of soil interfaces and subsequent failure. Dosing
concepts can be described as either 1) short term dosing or 2) alternate dosing.
Short term dosing usually refers to multiply daily dosings of effluent into a
single system with several hours or sometimes days of resting and re -aeration
between each dose. Two to eight doses per day has been shown to be
satisfactory in systems designed for pressure dosing in either subsurface or
surface application.
Alternate dosing refers to dual or multiple fields where one part of field
receives all of the effluent for a specified period. at which time the effluent is
switched to the alternate plot. This can be done each pump cycle, once per day
or switched only when one field has a problem. Both short term and alternate
dosing is often utilized in trickle irrigation systems.
Both dosing concepts as well as combinations and modifications of the
above have been successfully utilized in several states to treat and dispose of
sewage from individual homes as well as cluster developments, school
systems, and mobile home parks with flows of up to 50,000 gpd.
The design factor of sewage placement refers to the concept of placing the
sewage in the soil zone or horizon most conducive to absorption, treatment, and
re -aeration. In soils with high water tables this usually means at least a one or
two foot separation between the seasonal water table and the point of sewage
injection. For soils with restrictive clay horizons or hardpans, the sewage should
be injected as high above the restrictive zone as possible. This minimum
separation allows for lateral or horizontal flow of effluent away from the
distribution trench or pipe before interception by the restrictive zone and allows
for more uniform absorption through the restricting layer. This, coupled with
enhanced treatment of the sewage in the better soils above the restrictive
horizon, greatly enhances the quality of effluent impacting the restrictive
3
Small individual home aerobic decomposition and treatment can be
accomplished at comparatively low cost through small mechanically aerated
treatment systems. The better small aerobic units are capable of producing
an effluent exceeding that of the most sophisticated municipal treatment
plants. Table 1 shows the summary of effluent quality from a two year
operational study of the Clearstream Aerobic Treatment System, field tested
at several homes in Florida and Texas and by extensive testing of the unit by
the National Sanitation Foundation, a national independent testing agency.
The aerobic treatment unit described here treats the primary effluent by
extended aeration in a mechanically aerated contact chamber. The aerated
wastewater in the contact chamber is well mixed to provide optimum
exposure of the microorganism to the waste material. There is also a
significant reduction of pathogenic bacteria during this process. After
approximately 24 hours of aerobic contact, the activated wastewater is
clarified in a settling chamber and the settled solids returned to the aeration
chamber. The settled and clarified effluent is discharged from the settling
chamber through an improved design discharge assembly to minimize
solids carryover.
Aerobic treatment of domestic wastewater can be accomplished in other
ways. Sand filtration is a process sometimes used whereby the domestic
wastewater is first given primary treatment in a septic tank to reduce solids
and then applied intermittently to the surface of a sand bed of 2.5 to 3 foot
depth. An efficient sand filtration method is the recirculating sand filter (RSF).
The RSF offers a high degree of treatment with a minimum of maintenance
or nuisance problems. The RSF when loaded at a raw waste hydraulic
loading of 2.5-3.0 gal/ft2 per day produces a high quality effluent of similar
characteristics to that of the better aerobic treatment units. The slow rate,
intermittent sand filter, when designed at an hydraulic loading of 1.5 to 2
gal/ ft2 per day of septic tank effluent can also produce a high quality
effluent.
The choice between an aerobic system or a sand filter system depends
both upon the particular technical circumstances as well as local
regulations. We suggest that a Professional Engineer be consulted.
All treatment systems require routine systematic maintenance and the
successful long term operation of the system is dependent upon this
maintenance being correctly carried out.
B. Disinfection
The treatment by chlorination, ozonation, or UV radiation of the effluent
discharged from the aerobic cell represents the final step of a "safe" pre-
treatment system designed to allow maximum reuse of the wastewater in a
landscape mode. The potential of ozonation for deactivating viruses and
bacteria, detoxifying organic compounds and oxidizing any odorous
components make it the logical choice for systems installed in lake shore
settings or in extremely high groundwater conditions.
Ozone concentration in very low amounts and at very short contact time
is capable of disinfecting and deodorizing the effluent. This process has
only recently been utilized for home waste treatment due to the high
installation and operation costs of ozonation systems.
5
treatment unit with disinfection designed in conjunction with the system should
keep the bacterial slimes under control in the system and the 150 mesh disc
filter installed in -line of the header should remove any extraneous solids which
might be of size to plug the emitter orifice.
All these components integrated into a reliable sub -irrigation system makes
this a unique process for domestic waste disposal. Other systems of a similar
nature are being promoted and used in some southeastern states. One such
system utilizes a rubber diaphragm pressure compensating emitter. The rubber
diaphragm reduces the outlet orifice during operation, making it highly
susceptible to clogging. Even though the orifice opens when pressure is off, the
chances of intermittent plugging with bacterial slimes are quite high.
A rubber diaphragm is susceptible to attack by oil, gasoline products and
oxidizing agents, resulting in a likely change in the physical characteristics of
the rubber over time and thus affecting the uniformity of flow in the emitters.
Deposits also tend to build up at the seat of the diaphragm over time, changing
the flow characteristics of the emitter.
These pressure compensating emitters are not protected against root
intrusion and is susceptible to plugging by roots (2). Only the GEOFLOW
emitter protected by ROOTGUARDO can offer positive protection against a very
serious threat of root plugging.
Soil Application Design
The instantaneous water application rate of the system must not exceed the
water absorption capacity of the soil. A determination of the instantaneous
water absorption capacity of the soil is difficult, however, since the value varies
with the water content of the soil. As the soil approaches saturation with water,
the absorption rate reduces to an equilibrium rate called the "saturated
hydraulic conductivity." Wastewater application rates should be less that 10
percent of this saturated equilibrium
Even though the trickle irrigation system maximizes the soil absorption rate
through the low rate of application, thus keeping the soil below saturation, there
will be times when the soil is at or near saturation from rainfall events. The
design must account for these periods and assume the worst case condition of
soil saturation. By designing for a safety factor of 10 or 12, based on the
saturated hydraulic conductivity, the system will be under -loaded most of the
time but should function without surface failure during extreme wet periods.
Using a safety factor of 12, a suitable design criteria would be to load the
system at the estimated hydraulic conductivity but apply water for only a total of
2 hours per day out of the available 24 hours. By applying wastewater for a
total of 2 hour per day, particularly if applied in "pulses" or short doses several
times per day near the soil surface were the soil dries the quickest, this would
keep the soil absorption rate at the highest value and minimize the potential of
water surfacing on poor soil conditions.
As stated previously, this design criteria will under -load the system at all
times except when the soil is at or near saturation from rainfall. If designing for
an efficient irrigation system, the water supply may not be sufficient to meet the
demands of a lawn or landscaped area during peak water demand months.
This problem can be overcome by either of two solutions: add additional fresh-
7
Pump Tank and Controls
Dosing and irrigation supply will be by a submersible effluent pump located
in a 150-300 gallon storage tank. The operation of the pump will be by a simple
float on -off level switch in the tank. The "on" level switch will activate the pump
when the tank reaches a high water mark and the low level switch will turn the
pump off when the tank reaches a predetermined minimum water level. For a
typical system this volume would be 50-100 gallons. For a 250 to 500 GPD
system, this results in 3 to 10 irrigation pulses per day. For systems on sloping
ground where water drains from the pipes to the lower points of the system after
each pulse or dose, larger doses and fewer pulses per day would be more
suitable. Irrigation uniformity is best maintained with irrigation pulses of 10
minutes or more.
Filter Requirements
The recommended disc filter uses a 150 mesh screen that filters out particles
larger than about 100 microns. The type of emitter used in GEOFLOW trickle
systems will not have problems with this particular size since the diameter of the
flow path is 14 to 17 times larger, or 0.056 inches (1400 microns) for the 1 GPH
emitter to 0.08 inches (2,000 microns) for the 2 GPH emitter. To maintain the
proper water quality for the drip system, the filters are easily backwashed
manually or equipped with automatic back flush triggered by a timer or a
pressure differential switch. The installation schematic of the in -line filter is
shown in the typical system lay -out.
Flow Regulator
Under normal conditions, the pressure in the trickle lines should be
maintained between 20 and 25 psi during operations. This is controlled by a
pressure regulator located in -line following the filter. The emitter lines are
connected at each end by a PVC header line and flush line to allow optimum
pressure equilibrium in the system. Flush /vacuum release valves are located
at each end of these lines to allow a small amount of water to be automatically
flushed from the system every time it is started and avoid dirt suck back when
the system is switched off. This is important to prevent solids from accumulating
at the ends of these lines and to prevent dirt from entering the lines.
The schematic of a typical field layout of the trickle irrigation system shows
only a single field. For systems over 2000 ft in size or having over 500 emitters,
the system would be split into 2 or more fields of equal size. Flow for a dual
field system would be alternated through the use of a mechanical valve which
automatically switches fields each time the pump is activated.
For systems with more than 2 fields, the operation of each field is controlled
with an irrigation controller utilizing electric solenoid valves for each field
station. By separating the system into several fields, smaller pumps and more
uniform distribution can be achieved. Where soil conditions vary, some fields
may be programmed to receive less water than other fields of the system .
Trickle Emitter Lines
A normal home system would have emitter lines placed on 2 foot centers
with a 2 foot emitter spacing such that each emitter supplies a 4 ft area (Fig. 3).
These lines are best placed at depths of 6-10 inches below the surface. This is
0
Bibliography
1. Pettygrove, G.S. Asano, T. editors, Irrigation with reclaimed municipal wastewater - A
guidance manual, Lewis Publishers, Inc.
2. Bui, W. Performance of turbo model drip irrigation tubes. Proceedings of the third national
irrigation symposium. ASAE, November 1990 pp. 198-203.
3. Fowler, Lloyd C. Water reuse for the landscape. Goleta Water District. Goleta, CA.
4. Irwin, John. On -site wastewater reclamation and recycling. Proceedings of CONSERV90
Conference AWWA, AWRA, ASCE August 1990 pp 107-111
5. Jackson, J. D. Aquatic macrophite treatment systems for water reuse. Proceeding of
CONSERV90 Conference AWWA, AWRA, ASCE August 1990 pp 101-105
6. Gross, Mark A. et al. On -site treatment for reuse of domestic septic tank effluent in an
artificially drained soil. Proceedings of CONSERV90 Conference AWWA, AWRA, ASCE August
1990 pp 95-97.
7. Farwell, Larry. Grey Water reuse. Goleta, Water District, Goleta, CA. Proceedings of
CONSERV90 Conference AWWA, AWRA, ASCE August 1990 pp 1065-66.
8. English, Stephen. Filtration and water treatment for micro irrigation. Proceedings of the 3rd
International drip irrigation congress, Fresno, CA, 1985.
9. Phene, Claude C. Drip irrigation saves water. Proceedings of CONSERV90 Conference
AWWA, AWRA, ASCE August 1990 pp 645- 650
10. Stevens, Leonard. Clean Water Nature's way to stop pollution. Sunrise, New York 1974.
11. Reed, Sherwood. Land treatment of wastewater, Noyes Publications, Park Ridge, 1984.
12. Holden, Tim et al. How to select hazardous waste treatment technologies for soils and
sludges. Noyes Publications, Park Ridge, 1989.
13. Nakayama, F.S. Water analysis and treatment techniques to control emitter plugging.
Proceedings of the Irrigation Association Conference, Portland, 1982.
14. EPA "Land Treatment of Municipal Wastewater." EPA 625/1-81- 013. 1981.
15. Stewart, L.W. and R.B. Reneau, Jr. Spatial and Temporal Variation of Fecal Coliform
Movement Surrounding Septic Tank Soil Absorption systems in Coastal Plain Soils. J. Env. Qua].
10:528-531, 1981.
16. Carlile, B.L., C.G. Cogger, M.D. Sobsey and S.S. Steinbeck. Movement and Fate of Septic
Tank Effluent in Soils of the North Carolina Coastal Plain. Dept. of Human Resources, State of
North Carolina, Raleigh, North Carolina, 1981.
17. Carlile, B. L. "Use of Shallow, Low Pressure Injection Systems for Large and Small
Installations" in Individual Onsite Wastewater Systems, N. McClelland Ed. (Ann Arbor, MI: Ann
Arbor Science Publishers, Inc. 1979).
18. Carlile, B. L., A. R. Rubin and D. J. Osborne. "Status of Innovative and Alternative
Wastewater Treatment Systems in North Carolina." Paper No. 79-2586 presented at American
Soc. Ag. Eng. Conf. (Dec., 1979).
12
1510-95 Tax#1941-341-01-005 \i
JOB NAME 549 Big Dipper Rd. ARMSTRONG
JOB NO.
Bellyache Ridge
Wolcott, CO 81655
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JO.B FOLDER
4
EI7H AND JENNY GILBERT SUMWr SEWER SYSTEMS, INC. Fax: 719396.66J7 Vole@: 719J9646N To: HANK DANLEY Paps Y 0f2 Friday, Saptember01.1996 9:41:19 AM
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6S37
33305 COUNTY RD 361
Fax 719-395-6537
BUENA VISTA. CO 81211
EAGLE COUNTY ENVIRONMENTAL, HEALTH DEPT.
ATTN: RAY MERRY
P.O. BOX 179
EAGLE, CO 81631
�.0
REF: SEWER SYSTEMS FOR LOT 927, BELLYACHE RIDGE SUBDIVISION
EAGLE CO., CO.
EAST UNIT: STEVE ARMSTRONG
WEST UNIT: R CHARD RANIERI
THIS IS TO CERTIFY THAT THE WHITEWATER AEROBIC SEWER
EREATMENT SYSTEMS HAVE BEEN INSTALLED IN ACCORDANCE: WITH
THE ENGINEER'S DESIGN AND THE MANUFACTURER'S INSTALj"ATION
GUIDLINES. IF ANY ADDITIONAL INFORMATION IS REQUIRED, PLEASE
FEEL FREE TO CONTACT ME.
SINCERELY,
KEITH GILBERT-
SUMMIT SEWER SYSTEMS, INC.
if �9i�1 z
0
4
� OF C 0 \-O
i
577796 B-681 P-788 11/27/95 03:16P PG 1 OF 1 REC DOC
Sara J. Fisher Eagle County Clerk & Recorder 0.00
4
SUMMIT SEWER SYSTEMS, INC.
KEITH AND JENNY GILBERT Telephone 719-395-6537
Fax 719-395-6537
33305 COUNTY RD 361
BUENA VISTA, CO 81211
EAGLE COUNTY HEALTH DEPARTMENT
P.O. BOX 179
500 BROADWAY
EAGLE, CO 81631
REF: SERVICE CONTRACT FOR LOT #27, BELLYACHE RIDGE
SUBDIVISION
EAGLE COUNTY, CO.
SLTN4A.4IT SEWER SYSTEMS, INC.. WILL PROVIDE STANDARD MONTHLY
MAINTENANCE SERVICES FOR THE NVHITEWATER AEROBIC SEWER
SYSTEMS INSTALLED AT THE ABOVE LOCATION AT NO CHARGE TO THE
HOMEOWNER.
THE STANDARD MAINTENANCE INCLUDES:
- CLEANING OF COMPRESSOR AIR FILTER
- CYCLING TIMER MECHANISM
- INSPECTING DRIPFIELD
- FLUSHING DRIPFIELD (BI-ANNUALLY)
- PERFORMING 4 BI-ANNUAL SAMPLINGS FOR SOLIDS CONTENT
ALL OPERATING EXPENSES OR REPLACEMENT ITEMS NOT COVERED
UNDER MANUFACTUERER'S WARRANTY WILL BE THE RESPONSABILITY
OF THE HOMEOWNER. (IE. ELECTRICAL EXPENSE, PUMP -OUT FEES,
ETC.)
IF THE OWNERSHIP OF THE UNIT CHANGES HANDS, THIS CONTRACT
SHALL BE NULL AND VOID, AND A NEW CONTRACT MUST BE SIGNED
BY THE NEW OWNERS AS PART OF THE SALE OF THE PROPERTY. A FEE
SHALL BE CHARGED TO THE NEW OWNERS FOR SAID CONTRACT. THE
FEE WILL BE OF A STANDARD RATE EQUIVALENT TO THE COST OF
SIMILAR CONTRACTS AT THE TIME THE NEW CONTRACT IS WRITTEN.
ITH GILBERT 4TENUMSTRONG
SUMMIT SEWER SYSTEMS, INC.
577797 B-681 P-789 11/27/95 03:18P PG 1 OF 1 REC DOC
Sara J. Fisher Eagle County Clerk & Recorder 0.00
NSF
Certified to'ANSI/NSF Standard 40
'Class I
Whitewater" Systems
The Clear Cho ice
The Clear Choice for residential sewage treatment is the Whitewater Mechanical Sewage
Treatment System.
The Whitewater treatment system is tested under the stringent conditions of NSF
International* and meets or exceeds all certification requirements, with an average effluent
quality of 6 mg/L BODS and 7 mg/L TSS.
How Whitewater Why Use Whitewater
Treatment Systemst Treatment Systems?
Work
In using the Whitewater Treatment System you
can be proud that you are directly contributing to a
cleaner, safer environment.
Whitewater works by using the bacteria nature
provides. As a result of air being pumped into the
system, the bacteria thrive and grow in much
greater numbers than would occur naturally. This
"overpopulation" of bacteria speeds the process of
breaking down the sewage, making it safe for
release into the environment.
The process occurs entirely within the
self-contained Whitewater system which is
comprised of an outer mixing tank and a
cone -shaped settling chamber. Raw, unsettled
domestic wastewater enters directly into the
mixing tank where mixing occurs by air blown
through pipes. Solids remain in suspension with a
general flow up the outer plant wall and down the
outside of the settling chamber.
The mixed liquid then enters the settling
chamber from the bottom. The settling chamber
maintains a quiet condition which allows solids to
settle down and re-enter the mixing chamber for
more processing. The liquid, however, flows up and
is discharged as clear, odorless treated water which
meets or exceeds state water quality standards.
Whitewater Systems have been
independently tested and evaluated
by NSF International, the
premier U.S. based third party
certifier of health and environmental
products.
• Whitewater Treatment Systems
dispose of wastewater quietly,
efficiently, and with no odor in just
24 hours.
• Whitewater Systems operate on less
power than a 60 watt lightbulb!
• Whitewater Systems are FHA and
VA acceptable.
• Whitewater Systems have low initial
cost.
• Whitewater Systems are easily
installed.
• Whitewater Systems have low
maintenance costs.
• Whitewater Systems carry a full,
2-year warranty.
* Formerly the National Sanitation Foundation t Patent Pending
Model DF40
A L
4' INLET
4-SAMFLcrv—
Whitewater® Models
AIR DISCHARGE
RGEAION BI-Y or Specific Uses
DISCHARGE ASSEMBLY I
j A Whitewater Treatment Systems are
OUTLET manufactured to specifications according
'
to wastewater flow requirements.
Residential systems are available in two
sizes:
(COVER f OTAN0 NEW VIEW)
CONTROL PANEL
COMPRESSOR
MAIN
POWER CORD
COMPRESSOR
POWER AIR 6' DIAMETER ACCESS COVER
CORD OUTLET
' TO TANK
AIR AS
TUBE GRADE ELEVATION
M'-
4' OUTLETINVERTCLARIFIERAERATION TANK 4'-4'
4'-6"AIR DROP LINE
DEFLECTOR
5'-6'
SECTION A -A
(4' SAMPLE PORT NOT SHOWN FOR CLARITY)
Patent Pending
Design Components
Material
Specifications
Model DF40
Treatment Capacity...............................400 GPD
Volumetric Capacity.................................770 Gal
Electrical Requirement ............56 Watts; 115/ 1/6o
Aerator-Whitewater Compressor................DF40
Choice of steel, fiberglass or concrete Aeration
Tank, Cover, and Clarifier.
• Model DF40 for homes requiring
treatment of 400 gals. per day
• Model DF50 for homes requiring
treatment of 500 gals. per day
Where larger wastewater flow
requirements are required, the following
systems are available:
• Model DF60 treating 600 gals per day
• Model DF75 treating 750 gals per day
• Model DF100 treating 1000 gals per day
• Model DF150 treating 1500 gals per day
Fabricated According
to Need
Four choices of fabrication are offered,
consistent with your preference or
regulatory requirements:
• Coal tar coated steel tank with
fiberglass cover
• Solid fiberglass tank with fiberglass
cover
• Concrete tank with fiberglass cover*
• Concrete tank with concrete cover*
*Based on regional availability
Whitewater Treatment Systems are
manufactured regionally under license
from Delta Environmental Products, Inc.,
a respected leader in wastewater
treatment with over 25 years of
technical, design, and manufacturing
experience.
Service Policy and Optional Equipment
The Whitewater treatment system reflects Delta Environmental Products' state-of-the-art technology
backed by twenty-five years of wastewater treatment experience and service. The following service
policy is standard on all models of Whitewater Mechanical Sewage Treatment products for two years
following onset of use:
Regular six month inspections and maintenance of mechanical and electrical components as well
as an effluent quality inspection consisting of a visual check for color, turbidity, scum overflow and
examination for odors. If improper operation cannot be corrected at inspection, the dealer will
notify the owner of the conditions and provide estimated costs, if any, and date for correction. An
annually renewable service policy affording the same coverage is available after two years.
Delta Environmental Products, Inc. manufactures optional treatment system equipment including
chlorination systems, effluent pump with sump and automatic control, and offers sub -surface irrigation
systems which utilize Whitewater Treatment System effluent.
For further information contact Delta Environmental Products, Inc.
P.O. Box 969, Denham Springs, LA 70727. Phone (504) 665-1666 or (800) 219-9183.
Limited Warranty
Delta Environmental Products, Inc. warrants the parts in each treatment system with five (5) years on the com-
pressor regardless of tank material of construction, and ten (10) years on each fiberglass tank. Delta
Environmental Products, Inc. warrants other tanks as follows: two (2) years on metal tanks and two (2) years on
concrete tanks. All warranty questions are resolved through Delta Environmental Products, Inc. The warranty
on the treatment device is free from defects in material and workmanship from the date of installation treating
household wastewater. Some states do not allow limitations on how long an implied warranty lasts, so the above
limitation may not apply. Sole obligation under this warranty is as follows: Delta Environmental Products, Inc.
shall fulfill this warranty by repairing or exchanging any component part, F.O.B. factory that in Delta
Environmental Products, Inc.'s judgment shows evidence of defects, provided said component part has been paid
for and is returned through an authorized dealer, transportation prepaid. The warrantee must also specify the
nature of the defect to the manufacturer.
The warranty does not cover treatment processes/devices that have been flooded, by external means, or that have
been disassembled by unauthorized persons, improperly installed, subjected to external damage or damage due to
altered or improper wiring or overload protection.
This warranty applies only to the treatment process/device and does not include any of the house wiring, plumb-
ing, drainage, or disposal system. Delta Environmental Products, Inc. is not responsible for any delay or damages
caused by defective components or material, or for loss incurred because of interruption of service, or for any
other special or consequential damages or incidental expenses arising from the manufacture, sale, or use of this
process/device.
Delta Environmental Products, Inc. reserves the right to revise, change, or modify the construction and design of
the treatment process/device for household wastewater or any component part or parts thereof without incurring
any obligation to make such changes for modifications in previously sold equipment. Delta Environmental
Products, Inc. also reserves the right, in making replacements of component parts under this warranty, to furnish
a component part which, in its judgment, is equivalent to the company part replaced.
Under no circumstances will Delta Environmental Products, Inc. be responsible to the warrantee for any other
direct or consequential damages, including but not limited to lost profits, lost income, labor charges, delays in pro-
duction, and/or idle production, which damages are caused by a defect in material and/or workmanship in its
parts. Some states do not allow the exclusion or limitation of incidental or consequential damages, so the above
limitation or exclusion may not apply to you.
This warranty is expressly in lieu of any other express or implied warranty, excluding any warranty of mer-
chantability or fitness, and of any other obligation on the part of Delta Environmental Productions, Inc.
This warranty gives you specific legal rights, and you may also have other rights which vary from state to state.
DW42095
P.O. Box 969
Denham Springs, LA 70727
(504) 665-1666
FAX (504) 665-1855
Whitewater Systems
Model HC-1
Liquid Chlorination System
The Whitewater Model HC-1 Liquid Chlorination System chlorinates waste-
water to remove bacteria and viruses. The liquid type chlorination system is
easier to maintain than solid type systems and the duration between charging is
also extended to 6 months or more, making it much more cost effective to
recharge.
The chlorination system consists of a 15 gallon polyethylene tank and a pres-
sure operated pump that injects an adjustable amount of liquid disinfectant
into the wastewater each time the pump receives a pressure signal. The pump
is made of all non -corrosive materials and is constructed for long life.
The chlorine pump has no motor or other similar moving parts. It operates
when pressure inside the annulus of the pump between the pump wall and a
length of collapsible tubing squeezes the tubing and forces its contents out of
the pump through an external check valve at the outlet of the tubing. When the
pressure signal is removed, the tubing expands to its original shape during
which it draws in more disinfectant from the opposite end through another
check valve. This process is repeated each time the pressure signal is applied
and released.
The dosage is adjusted with a 3-way valve that returns an adjustable portion
of the pumped liquid back into the storage tank.
The tank is typically buried below ground. The fill tube and pump housing is
located inside a surface mounted valve box. 15 gallons of 5% to 12% Sodium
Hypochlorite solution is poured into the tank through the fill tube. The pump is
then placed and secured in the fill tube. A full tank will last approximately 6
months on a 500 gallon per day treatment plant.
For the gravity system, a contact tank is placed in the wastewater discharge
line. Wastewater enters the tank where it is periodically mixed with chlorine
disinfectant. Each time the main pump turns on, a pressure signal is applied to
the chlorine pump which then injects a predetermined amount of chlorine into
the contact tank. In the contact tank system supplied by Delta, the main pump
pumps about 15 gallons of disinfected water during each pump cycle. The prop-
er amount of chlorine required to treat 15 gallons of wastewater is injected into
the contact tank each cycle, thereby keeping the correct amount of residual
chlorine in the contact tank for the required amount of time to disinfect the
wastewater.
For drip and spray irrigation systems, the chlorine can be injected directly
into the lines to control bacteria build-up or into the main dose tank for com-
plete disinfection.
The HC-1 system can also be used for dechlorination by injecting a dechlori-
nation chemical into the waste stream after the wastewater has been disinfected.
YOUR LOCAL DISTRIBUTOR
SUMMIT SEWER SYSTEMS, INC.
KEITH & JENNY GILBERT
11%itewater is a registered trademark of Delta Environmen (719) 395-6537
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FIBERGLASS TEST REPORT
TENSILE PROPERTIES
ASTM D 638
SPECIMEN
I.D.
WIDTH
(in.)
DEPTH
(in.)
AREA MAX. LOAD
in.
TENSILE STRENGTH
1
sq. (pounds)
(PSI)
2
0.748
0.242
0.181 3,580
19,800
3
0.751
0.230
0.173 3,560
20,600
4
0.758
0.273
0.207 4,040
19,5 00
5
0.752
0.760
0.245
0.184 3,980
21,600
0.265
0.201 4,150
20,600
AVERAGE
20,420
STD. DEV.
820
FLEXURAL
PROPERTIES
ASTM
D790
SPECIMEN
I.D.
WIDTH DEPTH
b d
MAX LOAD
FLEXURAL STRENGTH SLOPE
FLEXURAL MODULUS
1
P
(PSI) m
(PSI)
2
0.511 0.253
0.501
177.7
32,600 648
1.25 E+06
3
0.275
0.487 0.238
209.9
139.2
33,240 768
1.18 E+06
4
0.508 0.265
185.0
30,280 468
31,110
1.14 E+06
5
0.520 0.243
188 1
724
36,760
1.23 E+06
AVERAGE
568 1.22 E+06
32,800 AVERAGE 1.20 E+06
STD. DEV.
2506 STD. DEV. 4.39 E+04
VOID
CONTENT of
REINFORCED RESIN
ASTM D
2734
SPECIMEN
I.D.
ASTM D 792
DENSITY RESIN
ASTM D 2584 THEORETICAL DENSITY
/ GLASS
CALCULATED VOIDS
1
(%�
1.516
56.3 43.7
1.634
2
1.519
56.0 44.0
1.630
7.2
3
1.523
56.0 44.0
1.630
6.8
AVERAGE
1.519 56.1 44.9
1.631
6.6
STD. DEV.
0.004
0 17
6.9
0.002
0.31
13
NSF International
November 2, 1994
his. Brenda Guy
Delta Fiberglass & Environmental Products Inc
P.O. Box 969
Denham Springs, LA 70727
Dear Ms. Guy:
By this letter, NSF certifies that the results reported below are true and accurate results of the
ammonia nitrogen analyses completed at the request of Delta Fiberglass &Environmental Products,
Inc. following completion of the Standard 40 Certification evaluation for the Delta MadeI DF40-;yi
Plant at the NSF Wastewater Technology Site in Chelsea, Michigan. The Standard 40 testis
Plant was completed during the week of January 24, 1993, however dosing got the
capacity Of 400 gallons per day was continued at the request of Delta Fiberglasse plant the rated
Delta Fiberglass requested analysis of the Chelsea influent wastewater dosed to the Plant and the
effluent samples from the DF40-M for ammonia nitrogen.
beginning March 26, 1993 (37 weeks Samples were collected once per week
after the start of the Standard 40 evaluation) and ended Pvith
samples collected on May 26, 1993 (46 weeks after the start of the Standard 40 evaluation). The
samples were collected as described in the Wastewater Technology report (dated June 1993) for the
Model DF40--M and were analyzed in- accordance with EPA Method 350.1.
The results of the analyses (reported as mg/L as N) were:
Sawn_ 1_ a Date Influent NH, Effluent NIA,
3/26/93
13
2.8
3/31/93
14
1.4
4/8/93
12
0.98
4/14/93
11
1.9
4/21/93
13
1.6
Samn�� u—NTL Effluent NH
4/28/93
14
—
I.5
5/5193
11
2.3
5/12/93
20
4.6
5/21/93
26
2.2
5/26193
25
21
Delta Fiberglass is hereby authorized to distribute this letter, in its entirety, as a summary
resulLQ of ammonia nitrogen analyses completed by NSF, le described ' of the
any questions you have. above. Please contact me with
Sincerely,
i
v
Thomas J. ruursema
Manager, Wastewater Treatment Unit
Certification & Related Programs
(313) 769-5375
3175 etymon(: Io
Telephony: 313-780P-O pox 1301.10 :11 nil 010 FAX: 313-7fg-01(T 8113-0190 USA)9"IM: 753215 NSF INTL
Rt. 2, Box 359A
Guntown, MS 38849
OCTOBER. 7, 1904
Phone
Pager
348-5521
678-4858
348-5339
678-4859
Ma . r TJY
ATTACHED Yojj WILL FIND RESULTS, OF AtIALY:;IS r'ERFC�R"iEi�
ON TEN DELTA TREATMr:�1'I' FI.,ANTS
ALL SAMPLES WERE COLLECTED
PRESERVED, AND ANALYZED I N ilc.%COF;DANt� , , '
1 T , r WITH UHTTED STA.IES
EN 1 Ri- MENTAL F PROTECT AGENc.y GUIDELINES AND ARE SUITABLE
FOR EPA RErC)h'r I NG . I r AIrIL': ,
PLEASE CALL. INC. i'A^I iF c il; FURTHEf� :SS.= I;TE.NCE:
SINCERELY,
R-A';' I:_ U . KITCHENS, ..�— _ -
Water & Waste Water Operation, Maintenance and Consulting
MSDEQ Class 4 — MSDOH Class A
October 13, 1994
Lab ID #
Sample
Description
Date
Received
Parameter
Sample
Result
4901
N401000CC
09/29/94
Nitrate
0.08 mg/1
4902
N401002CC
09/29/94
Nitrate
2.02 mg/1
4903
1003
09/29/94
Nitrate
1.95 mg/1
4904
N401006CC
09/29/94
Nitrate
0.12 mg/1
4905
1008
09/29/94
Nitrate
2.07 mg/1
4906
N401014CC
09/29/94
Nitrate
0.08 mg/1
4907
01033
09/29/94
Nitrate
1.37 mg/1
4908
01067
09/29/94
Nitrate
2.16 mg/1
4909
01069
09/29/94
Nitrate
2.01 mg/1
4910
01122
09/29/94
Nitrate
1.60 mg/1
THE TESTS PERFORMED ARE IN ACCORDANCE WITH STANDARD METHODS 17TH EDITION.
LABORATORY STATEMENT OF QUALIFICATIONS AVAILABLE
ON REQUEST
COMMUNITY DEVI-ORMENT
DEPARTMENT
(303) 328-8730
EAGLE COUNTY, COLORADO
May 18, 1994
Stephen Armstrong
P.O. Box 3568
Vail, CO 81658
Certified #P 794 728 314
500 BROADWAY
P.O. BOX 179
EAGLE, COLORADO 81631
FAX: (303) 328-7185
RE: Failing septic system at 549 Big Dipper Rd. East Duplex Lot
27, Bellyache Ridge Rd. Tax parcel #1941-341-01-005.
Dear Mr. Armstrong,
On 5/10/94 this office conducted a site visit on the above
referenced property. The purpose of the site visit was to
investigate a complaint alleging that your individual sewage
disposal system (ISDS) was failing. During this visit it was
discovered that your ISDS is not functioning properly.
Be aware that this constitutes a violation of Eagle County Land
Use Regulations 4.03, et sect. "The owners of any structure where
people live, work, or congregate shall insure that the structure
contains adequate, convenient, sanitary toilet and sewage
disposal systems in good working order. Under no condition shall
sewage effluent be permitted to be discharged upon the surface of
the ground, or into waters of the State, unless the sewage or
effluent meets the Water Quality Standards of the Colorado Water
Quality Control Commission, or the Colorado Department of Health
Guidelines Chapter 25, Article 10, C.R.S. 1973, as amended,
whichever are applicable."
As per Eagle County Land Use Regulations 4.03.06,., "Application
for a repair permit shall be made by such owner or occupant to
the Environmental Health Department within two business days
after receiving notice from the Department that the system is not
functioning in compliance with section 25 article 10 C.R.S. 1973
as amended."
This situation must be rectified immediately. A repair permit
must be applied for within two business days after the receipt of
this letter to avoid court intervention.
Please be advised, Eagle County will pursue all available legal
remedies to ensure that your septic system does not endanger the
health of your tenants or anyone else in the surrounding area.
Please find the enclosed ISDS repair application and other
pertinent information.
Sincerely,
Raymon Merry, REHS, --f
Environmental Health Division Manager
cc: James R. Fritze, Eagle County Attorney
Jim Chubrilo, CDH, Water Quality Control Div.
Keith Montag, Director of Community Development
Dr. Phil Friedman, Eagle County Health Officer
11-30-94 06:54FM FROM LONGS EXCAVATION
{
,,-
F92
0
LON'S EXCAVATION, INC:.
Paui Long
President
November JU, 1994
Eagle County
Environmental Heath Division
This is a letter in response to a sewage system permit issued for
Stephen Armstrong and Richard Ranieri for 549 Big dipper Road. The
Site has been visited by Longs and a bid sent to owners �,:z of
December 1., 1994. The sits: is such that to insure a qua.lti.ty
system the job will need to be done in the spring or summer months
cf the year. The site access is such that material imported for
the mound system wjould bc- very difficult or impossible.. This and
the fact that most material would have than potential to be frozen
would make the job impossible at this time of year. There is also
the potential dur- to the existing system, that the area will need
to be dried out by installing west system first. Then allow the
area to rest for .;a week L.'r Sc and install ether system. These are
All reasons why the job should wait till spring. We estimate it
will take two wee;;s to complete both systems. rf the system has to
be put - in now. I would suggest an alternative such as a storage
system or some other means to get by until spring.
7 ank-you r
1
f1'U�
L©ng's Excavation Inc.
P.O. Box B94 • Avon, Colorado 81620 a (303) 949-4W2
INDIVIDUAL SEWAGE DISPOSAL SYSTEM PERMIT
EAGLE COUNTY ENVIRONMENTAL HEALTH DIVISION
P.O. Box 179 - 500 Broadway • Eagle, Colorado 81631
Telephone: 328-8755
YELLOW COPY OF PERMIT MUST BE POSTED AT INSTALLATION SITE.
Please call for final inspection before covering any portion of installed system.
PERMIT NO.
OWNER: Stephen Armstrong PHONE: 926-2025
MAILING ADDRESS: P.O. Box 3568 City:, Vail slate: CO ZIP: 81658
APPLICANT: Same PHONE:
SYSTEM LOCATION: 549 Big Dipper Road TAX PARCEL NUMB 1941-341-01-005
LICENSED INSTALLER: Longs Excavation Inc LICENSE NO: 61-94
DESIGN ENGINEER OF SYSTEM: Inter -Mountain En i eerie
INSTALLATION HEREBY GRANTED FOR THE FOLLOWING: `y i
1000 GALLON SEPTIC TANK X �� e
ABSORPTION AREA REQUIREMENTS:
SQUARE FEET OF SEEPAGE BED 562.5 SQUARE FEET OF TR/11M. 1 „T C
SPECIAL REQUIREMENTS: Install as per Engineer's des V
ENVIRONMENTAL HEALTH APPROVAL: , DATE:
CONDITIONS:
1. ALL INSTALLATIONS MUST COMPLY WITH ALL REQUIREME S OF THE EAGLE COUNTY DIVIDUAL SEWAGE DISPOSAL SYSTEM REGULATIONS, ADOPTED PURSUANT
TO AUTHORITY GRANTED IN 25- 10- 104. 1973, AS AMEND .
2. THIS PERMIT IS VALID ONLY FOR CONNECTION TO STR TURFS WHICH HAVE FULLY CO LIED WITH COUNTY ZONING AND BUILDING REQUIREMENTS. CONNECTION
TO OR USE WITH ANY DWELLING OR STRUCTURE NOT PPROVED BY THE ZONING AND BUI DING DEPARTMENTS SHALL AUTOMATICALLY BE A VIOLATION OF A
REQUIREMENT OF THE PERMIT AND CAUSE FOR SOT LEGAL ACTION AND REVOCATION OF HE PERMIT.
3. CHAPTER IV, SECTION 4.03.29 REQUIRES ANY PER N WHO CONSTRUCTS, ALTERS OR INSTA LS AN INDIVIDUAL SEWAGE DISPOSAL SYSTEM TO BE LICENSED.
FINAL APPROVAL OF SYSTEM: (TO BE COMPLETED BY INSPE OR):
NO SYSTEM SHALL BE DEEMED TO BE IN COMPLIANCE W H THE EAGLE COUNTY INDIVIDUAL SEWAGE DIS SAL SYSTEM REGULATIONS UNTIL THE SYSTEM IS APPROVED
PRIOR TO COVERING ANY PORTION OF THE SYSTEM.
INSTALLED ABSORPTION OR DISPERSAL AREA: SQUARE FEET.
INSTALLED SEPTIC TANK: GALLON DEGREES FEET FROM
SEPTIC TANK ACCESS TO WITHIN S" OF FINAL GRAD AND
PROPER MATERIAL AND ASSEMBLY YES —NO
COMPLIANCE WITH COUNTY / ST TE REQUIREMENTS: YES NO
ANY ITEM CHECKED NO REQUIRES CORRECTION BEFORE FINAL APPROVAL OF SYSTEM IS MADE. ARRAN\RE-1ECTION WHEN WORK IS CORRECTED.
COMMENTS:
ENVIRONMENTAL HEALTH APPROVAL: \ DATE:
ENVIRONMENTAL HEALTH APPROVAL: DATE:
(RE -INSPECTION IF NECESSARY)
RETAIN WITH RECEIPT RECORDS
APPLICANT / AGENT:
PERMIT
PERCOLATION TEST FEE
OWNER:
RECEIPT #
CHECK#
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 328-8730
May 23, 1995
Mr. Stephen Armstrong
P.O. Box 3568
Vail, CO 81658
EAGLE COUNTY, COLORADO
RE: NOTICE OF HEARING
Dear Mr. Armstrong,
P.O. BOX 179
EAGLE. COLORADO 81631
FAX (303) 328.7207
CERTIFIED MAIL #P 794 721 498
In accordance with the procedure outlined in the Eagle County Land Use
Regulations (ECLUR), Section 4.03.25, a hearing will be held to determine
whether to issue an order to cease and desist from the use of your
individual sewage disposal system (ISDS) serving the dwelling located at
549 Big Dipper Road, Bellyache Ridge Subdivision, Eagle County, Colorado.
The order, if issued, will require the owner to bring the system into
compliance with ISDS Regulations or eliminate the nuisance or hazard within
a reasonable period of time, not to exceed thirty (30) days, or thereafter
cease and desist from the use of the system. You are entitled to be
present personally and/or with counsel if you wish to be heard.
Eagle County received correspondence from Long's Excavation, Inc., that we
felt justified refraining from requiring a repair of your system until
spring. I'm sending this notice now to allow time for the repairs to occur
prior to the hearing. In addition, the ISDS Permit previously issued to
Long's Excavation, Inc., (ISDS #1399) has since expired. It will be
necessary to re-evaluate the design of the repair for a new permit to be
issued. Eagle County will not be requiring an additional permit fee.
As you are aware, this system was determined not to be functioning in
compliance with the above referenced Regulations as it constitutes a
nuisance to public health and has not received timely repairs in accordance
with the provisions of paragraph 4.03.06, ECLUR.
The hearing will be held Thursday, July 6, 1995 at 3:00pm, in the Eagle
County Room at the Eagle County Building, located at 500 Broadway, Eagle,
Colorado.
Sincerely,
Raym P. Merry, R�HS
Env' onmental Hea th M a
cc: Keith P. Montag, Director of Community Development
James R. Fritze, Eagle County Attorney
ISDS File #1399
COMMUNITY DEVELOPMENT
DEPARTMENT
(303) 328.8730
P.O. BOX 179
EAGLE, COLORADO 81631
FAX (303) 328.7207
EAGLE COUNTY, COLORADO
Stephen Armstrong— A4411?�
P.O. Box 3568
Vail, CO 81658
Richard Ranieri — P g5 ;2q y le"
123 Mt. Sinai Ave.
Mt. Sinai, NY 11766
CEASE AND DESIST ORDER
RE: 549-Big Dipper Road, East Duplex Lot 27, Bellyache Ridge, Tax
parcel #1941-341-01-005
549 Big Dipper Road, West Duplex Lot 27, Bellyache Ridge, Tax
parcel #1941-341-01-004
This matter came on for hearing, pursuant to written notice, at
3:00 p.m. on July 6, 1995, before Raymond P. Merry, acting in his
capacity as the chief administrative officer of the Eagle. County,
Colorado, Division of Environmental Health, and the Health Officer
for purposes of Eagle County Land Use Regulations ("ECLUR"),
Chapter 4. Stephen Armstrong did not appear. Richard Ranieri
appeared by his attorney, Kerry Wallace.
Based upon the statements and evidence offered at the hearing:
IT IS FOUND:
1. In response to a complaint, on May 10, 1994, the Eagle
County, Colorado, Division of Environmental Health investigated the
Individual Sewage Disposal System ("ISDS") serving the properties
located at 549 Big Dipper Road, East Duplex Lot 27, Bellyache
Ridge, Tax Parcel #1941-341-01-005 and at 549 Big Dipper Road, West
r-
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 2
Duplex Lot 27, Bellyache Ridge, Tax Parcel #1941-3471-01-005,
owned, respectively, by Stephen Armstrong and Richard Ranieri. The
investigation showed that the system was failing, effluent was
saturating the ground and seeping onto the surface of the ground,
and the system was not functioning in compliance with Eagle County
Land Use Regulations, Chapter 4. It subsequently was determined
that a single tank was serving both properties.
2. Written notice of violation pursuant to ECLUR 4.03.24,
dated May 18, 1994, was given to Stephen Armstrong by mail, receipt
of which on May 20 was acknowledged by him. The notice stated that
he was required to apply for a repair permit within two business
days, pursuant to ECLUR 4.03.06, and bring the ISDS into compliance
within 30 days.
3. Written notice of violation pursuant to ECLUR 4.03.24,
dated June 23, 1994, was given to Richard Ranieri by mail, receipt
of which on June 28 was acknowledged by him. The notice stated
that he was required to apply for a repair permit within two
business days, pursuant to ECLUR 4.03.06, and bring the ISDS into
compliance within 30 days.
4. Stephen Armstrong applied for a repair permit on. May 23,
1994.
5. Richard Ranieri applied for a repair permit on July 5,
1994.
6. A permit for the construction of new ISDS systems for the
respective properties, per engineering drawings, was issued to
Longs Excavation, Inc. on behalf of Stephen Armstrong and Richard
Ranieri on or about November 14, 1994.
7. Longs Excavation, Inc. requested an extension of time to
complete the repair because of winter construction conditions, by
FAX on November 30, 1994. -
8. Based on the advice of the County Health Officer that
during the winter the saturated surface and seeping effluent would
be ice or under snow and, therefore, would not constitute a
significant public health hazard while the winter conditions
existed, enforcement of the ECLUR was deferred pending repair in
Spring, 1995.
9. The Individual Sewage Disposal Systems) serving the two
duplexes on the properties is(are) not functioning in compliance
with the ECLUR and Title 25, Article 10 of the Colorado Revised
Statutes.
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 3
10. The Individual Sewage Disposal System(s) serving the two
duplexes on the properties has(have) not been repaired. The
system(s) has(have) not received timely repair as required by ECLUR
paragraph 4.03.06.
11. The failure(s) of the Individual Sewage Disposal
System(s) serving these properties constitutes a nuisance or hazard
to public health.
12. Written notice of this hearing was given to Stephen
Armstrong and Richard Ranieri, respectively, more than 48 hours in
advance of the hearing.
THEREFORE, IT IS ORDERED, pursuant to, Eagle County Land Use
Regulations paragraph 4.03.25 and C.R.S. 25-10-106:
1. That Stephen Armstrong, and any person acting by, through
or in concert with him,, shall cease and desist from violation of
the Eagle County Land Use Regulations, Chapter 4, and Article 10 of
Title 25 of the Colorado Revised Statutes, with respect to the
property identified as 549 Big Dipper Road, East Duplex Lot 27,
Bellyache Ridge, Tax Parcel 11941-341-01-005, specifically by the
following acts:
a) refraining, after 11:59 p.m. on August 11, 1995,
from using or permitting the use in any way, including by
depositing water, liquid, or wastes of any nature in, the
Individual Sewage Disposal System serving that property;
b) bringing the Individual Sewage Disposal System
serving that property into compliance with the Eagle
County Land Use Regulations, and Article 10 of Title 25
of the Colorado Revised Statutes, and eliminating the
nuisance or hazard, not later than by 11:59 p.m. on
August 11, 1995.
2. That the issuance of any permit for the repair of the
system, including the installation of a replacement system,
pursuant to Eagle County Land Use Regulations paragraphs 4.03.06 or
4.03.04 shall not extend the time provided in paragraph 1 hereof.
3. That Richard Ranieri, and any person acting by, through
or in concert with him, shall cease and desist from violation of
the Eagle County Land Use Regulations, Chapter 4, and Article 10 of
Title 25 of the Colorado Revised Statutes, with respect to the
property identified as 549 Big Dipper Road, West Duplex Lot 27,
Stephen Armstrong
Richard Ranieri
July 11, 1995
Page 4
Bellyache Ridge, Tax Parcel #1941-341-01-005, specifically by the
following acts:
a) refraining, after 11:59 p.m. on August 11, 1995,
from using or permitting the use in any way, including by
depositing water, liquid, or wastes of any nature in, the
Individual Sewage Disposal System serving that property;
b) bringing the Individual Sewage Disposal System
serving that property into compliance with the Eagle
County Land Use Regulations and Article 10 of Title 25 of
the Colorado Revised Statutes, and eliminating the
nuisance or hazard, not later than by 11:59 p.m. on
August 11, 1995.
4. That the issuance of any permit for the repair of the
system, including the installation of a, replacement system,
pursuant to Eagle County Land Use Regulations paragraphs 4.03.06 or
4.03.04 shall not extend the time provided in paragraph 3 hereof.
Dated: July 11, 1995
A15W
RaYmo,od P. reCount
REH
Man er, Ea
Environment ivison
\ces&des
YOUR LOCAL DISTRIBUTOR
SUMMIT SEWER SYSTEMS, INC.
KEITH & JENNY GILBERT
(719) 395-6537
COLORADO DEPARTMENT OF HEALTH DATE:
INORGANIC CHEMISTRY LABORATORY REPORTED BY:
4210'E`11TH AVE. DENVER, CO 80220
(,303)691-4726
SAMPLE NUMBER: 951062 PWSID #:
SAMPLE DESCRIPTION: SUMMIT SEWER SYSTEMS INC
ADDRESS 33305 CR 361
BUENA VISTA, CO 81211
COLLECTED BY: KEITH GILBERT
WHERE:
DATE SAMPLED: 03/09/95
DATE RECEIVED: 03/09/95
BOTTLES: L NUT
TYPE: 8
COMMENTS: FEE PAID 28.50
ANALYSIS RESULTS
N-NITRATE/NITRITE NONE DETECTED
PHOSPHATE - TOT 6.7 mg/L
MCL = MAXIMUM CONTAMINANT LEVEL
MSL = MAXIMUM SUGGESTED LEVEL
NLE = NO LIMITS ESTABLISHED
EAL = EPA ACTION LEVEL
03/16/95
HN
COUNTY:
PHONE : 7193956537
EPA LIMITS
MCL=10.0 mg/L
e
COLORADO DEPARTMENT OF !HEALTH
INORGANIC CHEMISTRY LABORATORY
4210 E 11TH AVE. DENVER, CO 80220
(303)691-4726
SAMPLE NUMBER: 951063
SAMPLE DESCRIPTION: SUMMIT SEWER SYSTEMS
ADDRESS 33305 CR 361
BUENA VISTA. CO 81211
COLLECTED BY: KEITH GILBERT
WHERE: EFFULENT
DATE SAMPLED: 03/10/95
DATE RECEIVED: 03/10/95
BOTTLES: 2L NEUT
TYPE: 7
COMMENTS: FEE PAID $67.75
ANALYSIS RESULTS
BOD, SEWAGE 11 mg/L
PH 7.5
SOLIDS, SUS. < 10 mg/L
DATE: 03/22/95
REPORTED BY: mk
COUNTY: CHF
PHONE : 0
m
44(1114z-�Ice
ANI
-4