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BOARD OF HEALTH
CITY OF NORTHAMPTON i •" 1Jti
DONNA C.SALLOOM,CHAIR
SUZANNE SMITH.M.D
MASSACHUSETTS 01060 NO•�'
JOANNE LEV{N,M D. i41 11
OFFICE OF THE
Benjamin Wood,MPH,Director
Jeverta Mir, MPH,rearm inspector BOARD OF HEALTH
Petri=Abbott,RN,Public Health Nurse 212 MAIN STREET
eu har McBride, Olen(
(413)587-1214 NOR—HAMPTON.MA 01060
FAX(413)587-1221
1/77/0,5/7/1-)y e /
Onsite Septic System Construction Permit: Conservation Commission Review
NOTE: As of 1/1/11, Septic System Permits will not be issued by the Northampton Board of Health
until we receive this form signed by the Northampton Conservation Commission Staff Member.
The Conservation Commission can be reached by contacting:
0 Sarah LaValley, Conservation, Preservation and Land Use Planner
SLaValleyPnorthamptonma.gov
Office of Planning& Development
210 Main Street, Rm. 11, City Hall
Northampton, MA 01060
C
Property Owner: / r- / Address: /23 76,Jowu
Engineer. j' ,1 p 6, 5 Ze•Le
Conservation Commission Conservation, Preservation and Land Use Planner
Date:
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1664 Cape St.
HOMESTEAD Williamsburg, MA 01096
413 628-4533
Vegheat@gmail.com
May 2,2016
Narrative Summary
This is an application for a disposal works permit for 123 Meadow Street in Florence,owned by
Lance Kirley who resides at that location. The application is to approve a new toilet facility in
an existing outbuilding for use of employees and tenants. The toilet facility will be an alternative
type facility that is comprised of a Phoenix brand composting toilet with a urine divesion system
built in.A second chamber will be used for urine composting on-site and any possible leachate
from the solids composting system.
The new toilet facility will be constructed in the"Hay Barn"as shown on the attached site plan.
This is an unheated facility without any nearby water supply or removal systems. It has an
existing cement lined manure pit built during the times this was an animal shelter. Currently
unused, the manure pit will be thoroughly cleaned, the concrete inspected and repaired as
required to be a sealed chamber on the sides and base. The masonry wall height may be extended
to avoid any possible flood intrusion from the nearby Mill River. A backup sump pump system
will automatically remove any leakage during spring floods.The composting chambers will be
tied down in case of any flood in the manure pit so they are not dislodged.
Additional improvements will include the use of a waterless handwashing station with an alcohol
based hand cleaner and the installation of LED lighting system. A toilet enclosure will be
constructed over a fraction of the square footage of the manure pit to provide conventional
privacy surrounding the toilet seat. This enclosure will be handicapped accessible.The enclosure
will also be ventilated. A small silicone type heating pad will be installed below the composters
and operated thermostatically to avoid complete freezing of the compost systems in cold
weather.
The Phoenix composting toilet, model 199, will have an automatic leachate pump system that
will collect any excess liquid at the base and pump it to the adjacent urine/leachate composting
system.This system will be constructed from one or more 96-gallon, rolling, blow-molded
plastic totes, modified with a double snorkel system to aerate the wood-shaving based compost
so to promote biological activity and evaporation.These systems are currently in operation at the
Community Garden located directly across the street from the proposed facility at 140 Meadow
St. These have been operational for approximately one year at that location and have been found
to be satisfactory in performance. A copy of a chemical analysis of the compost resulting from
this system is attached.
The toilet facility will be used by a maximum number of eight employees or tenants.Typical
usage will be fewer than four per day.310 CMR 15.203 (3)defines the facility as a Factory,
Industrial Plant or Dry Storage Space without cafeteria with a sewage production rate of 15
gallons per day.The use of a compost toilet reduces this flow rate by 50%, or 7.5 gallons per
person per day.The lack of any water source to the toilet facility further reduces the total
expected flow by an additional 80%. For the maximum number of users this will result in a
calculated flow rate to the Phoenix composter of 12 gallons per day. To this we calculate that
only 10% of this volume may become leachate needing further disposal, or at most 1.2 gallons
per day that will be sent to the leachate/urine composter.
The literature states that humans produce up to 150 gallons of urine per year. No adult is likely to
spend more than 20% of his/her time at this facility,producing a maximum of 30 gallons per
year. For the total user population, this would result in a maximum of 0.66 gallons of urine per
day.Thus the total liquid input to the urine composting system is 1.86 gallons per day or less.
This urine/leachate composting system is designed to handle this liquid volume.
Composted solids from both the Phoenix composter and the urine composter will be disposed of
at a schedule to be determined, and on-site at the garden site shown on the plans.The solids will
be manually removed when necessary and buried below six inches of garden soil as per the Title
5 code.
---litsrut,zesr
Thomas S. Leue R.S.
President
Homestead Inc.
Soil and Plant Tissue Testing Laboratory
(V) Ii M a s s 203 Paige laboratory
161 Holdsworth Way
University of Massachusetts
Extension Amherst,MA 01003
Phone: (413)545-2311
e-mail:soiltest@umass.edu
website:soifest.umass.edu
Compost - Comprehensive Sample Information:
Sample ID: FOG 3/16
Prepared For:
Adele Franks Order Number: 21114
123 Black Birch Trail Lab Number: C160415-103
Florence, MA 01062
Received: 4/15/2016
Reported: 4/22/2016
adele.franks@ gmail.com
413-582-0191
irri°"114111111"1"11.411.11.11111111.11.1.11111111111.1111111.1111111111111.1111111.11111I lii %4'e ,Basis W ilk Bit oIu' r
pH 531
Bulk Density 360 Ibsrcub yd
Moisture Content 723% 261 lbs/cub yd
Total Nitrogen 1.64% 0.45% 1.63 lbs/cub yd
Nitrate Ni 1 n 2148 mg/kg 594 mg/kg
Total Carbon 40.7% 11.3% 40.5 lbs/cub yd
Phosphorus 0.19% 0.05% 0.191bsrcub yd
Calcium 1.12% 031 % 1.10 lbs/cub yd
Material: Finished Feedstock: Leaves,sawdust,urine,finished compost
Age In weeks: 25 Intended Use: Landscape Mulch,
Compost Method: Passive
Interpreting your Compost Test Results
1 t 1:'.l .. 11 it - 1•. 1 11 l 1'- . -It
•
1 of 1 Sample ID:FOG 3116 Lab Number C160415-103
City of Northampton Mail - 123 Meadow Street Composting Toilet https:!!mail.google.comimail!u/0/?ui=2&ik=6523cdbe9e&view=
•
? CitJ of Daniel Wasiuk<dwasiuk@northamptonma.gov>
Northampton
123 Meadow Street Composting Toilet
4 messages
Sarah LaValley <slavalley@northamptonma.gov> Tue, Jun 21, 2016 at 2:25 PM
To: Daniel Wasiuk<dwasiuk@northamptonma.gov>
Hi Daniel-
I spoke with the engineer for this project,for which I had listed a few questions on the septic permit
application last week.
He confirmed that all work will be located within the existing barn structure;so conservation commission
review is needed since that's the case.
Thanks!
Sarah I.LaValley
Conservation, Preservation and Land Use Planner
City of Northampton
Office of Planning and Sustainability
210 Main Street,Room ii
Northampton MA,oio6o
413-587-1263
°nor''
Daniel Wasiuk <dwasiuk@northamptonma.gov> Wed, Jun 22, 2016 at 3:10 PM
To: Sarah LaValley <slavalley@northamptonma.gov>
Thanks Sarah!
[Quoted text hidden]
Daniel Wasiuk
Health Inspector
Northampton Health Department
413-587-1217 office
dwasiuk@northamptonma.gov
Sarah LaValley <slavalley@northamptonma.gov> Wed, Jun 22, 2016 at 3:11 PM
To: Daniel Wasiuk <dwasiuk@northamptonma.gov>
I left out an important word I just noticed! "so NO conservation commission review is needed since that's
the case"
Thanks!
I of 2 6/22/2016 3
City of Northampton Mail - 123 Meadow Street Composting Toilet https:/mail.google.com'mail/u/0/?ui=2&ik=6523cdbe9e&view=
Sarah I. LaValley
Conservation,Preservation and Land Use Planner
City of Northampton
Office of Planning and Sustainability
210 Main Street,Room H.
Northampton MA,oio6o
413-587-1263
it'It : •
[Quoted text hidden]
Daniel Wasiuk <dwasiuk@northamptonma.gov> Wed, Jun 22, 2016 at 3:15 PM
To: Sarah LaValley <slavalley@northamptonma.gov>
I was just reviewing the engineer's email to me and it did not"align"with what you had stated...so thank you
kindly for the clarification. I appreciate your assistance with this one! Be well.
Daniel
[Quoted text hidden]
2 of-) 6/22/2016 3
• COMMONWEALTH OF MASSACHUSETTS
•
-** — EXECUTIVE OFFICE OF ENVIRONMENTAL AFFAIRS
=vr� DEPARTMENT OF ENVIRONMENTAL PROTECTION
ONE WINTER STREET, BOSTON, MA 02108 617-292-5500
MITT ROMNEY ELLEN ROY HERZFELD
Governor
Secret
KERRY
HEALEY
Ao Governor ROBERT W.GOLLEDGE,
Lieutenant
Commissio
Revised April 2005
Using Composting Toilets and Greywater Systems in Massachusetts
COMPOSTING TOILETS
Required Approvals
Homes: Title 5 (310 CMR 15.000)allows composting toilets for Remedial Use and also
certifies them for General Use in new residential construction where a system in full compliance
with Title 5 could otherwise be installed. The local approving authority (typically the Board of
Health)must also approve installation of a composting toilet through a Disposal System
Construction Permit and Certificate of Compliance. Check with your local Board of Health for
its approval procedures.
Commercial or Public Facilities: Massachusetts General Laws of 2002 (Chapter 176, §3)
allow the use of composting toilets for remedial use or new construction of commercial and
public facilities without meeting the full compliance requirement of Title 5. As with residential
facilities,they must obtain approval from their local approving authority. DEP is the approving
authority for state and federal facilities.
Plumbing Approvals: Since a composting toilet is a plumbing fixture, the Board of
Registration of Plumbers and Gas Fitters must also approve the unit. For a list of approved units,
see http:Micense.reg.state.ma.us/pubLic/pb_product.asp. In addition,the local plumbing
inspector must approve any installation of indoor plumbing fixtures.
Composting Toilet Technology
Composting toilets use a biological process in which various types of organisms degrade
human waste under controlled conditions to a humus-like end product. This process is influenced
by environmental factors such as temperature,moisture,pH,aeration and the ratio of carbon to
nitrogen:
■ Compost temperature must be maintained above 55°C for three days for composting
to proceed effectively and kill pathogenic organisms. At lower temperatures,.bacterial
activity is inhibited,the composting process slows,and pathogens may not be
destroyed.
This information is available in alternate format.Call Donald M.Comes,ADA Coordinator at 617-556-1057.TDD Service-1-800-298-2207.
DEP on the World Wide Web: http://www.mass.govidep
0 Printed on Recycled Paper
Using Composting Toilets and Greywater Systems in Massachusetts Revised April 2005
■ Moisture must be maintained between 40-60%for best results. All organisms require
water, but too much moisture in the compost pile may create anaerobic conditions.
On the other hand,very low water content will retard microbial activity.
• Normally,there is no need to influence the pH of a composting toilet. The ideal pH
range for most bacteria is from 6 to 7.5. Fresh human excreta are slightly acid(below
6)but after a few days in compost pile the pH usually begins to rise to the optimum
range.
• Proper mixing,porosity and maintenance of aerobic conditions are necessary for
rapid decomposition and for the destruction of pathogenic organisms. Under
anaerobic conditions, the decomposition is slower,heat given off is only a fraction of
that from aerobic conditions,and foul-smelling gases are released.
• To achieve rapid decomposition,the optimum range for the carbon/nitrogen balance
is 20:1 to 30:1. Human excreta and especially urine are rich in nitrogen. It may be
necessary at times to add high carbon materials like sawdust, grass and kitchen wastes
to keep the carbon/nitrogen ratio in the optimum range. Manufacturers of composting
toilet systems often recommend such materials and provide instructions on how often
to use them;they may even sell pre-packaged bulking agents.
Types of Composting Toilets
There are two types of composting toilets generally available:
Separate Composting Units: These are toilets connected to a separate, relatively large
composting unit located near the toilet. Waterless composting toilets are typically installed in a
bathroom directly above the composting unit with a straight chute directly connecting them. A
foam flush toilet can be offset from the composting unit and connected to it via a standard pipe.
The composting unit consists of a receptacle and a storage chamber. A properly
operating composting process will decompose the pile to less than 10%of the original volume by
the time the compost is ready to be removed. Excess liquid is drained to the lowest part of the
composting unit where it is either evaporated or collected. This is a slow process, and it may take
a few years before the first time there is a need to remove humus from the storage unit. After
that, annual removal is generally sufficient.
Self-contained Units: These are smaller units in which the toilet seat,receptacle and
composting tank are a single self-contained unit. Some designs incorporate heaters and
mechanical aeration to maintain a balance of moisture and aerobic conditions necessary for
proper composting. Self-contained units are designed to evaporate all excess liquid so that there
is no discharge other than the finished compost. Compost has to be removed from these units
several times per year; disposal options for the finished compost are described below.
Liquid By-product
If the composting toilet produces a liquid by-product that is not recycled through the
toilet,the liquid by-product must be disposed of in one of the following ways:
a) Discharged through a greywater system on the property that includes a septic tank
and leaching system in compliance with Title 5 (310 CMR 15.100-15.293);
2
Using Composting Toilets and Greywater Systems in Massachusetts Revised April 2005
b) Stored properly and removed and disposed of by a licensed septage hauler;
c) Disposed of using an alternate method specifically approved by DEP.
Composted Solids
Title 5 (310 CMR 15.289(3)(a)(3))requires that composting toilet systems be designed
to store compostable and composted solids for at least two years, either inside the composting
chamber(systems with large separate composting units) or in a separate compost container
(smaller self-contained units), unless DEP has specifically approved an alternate system.
Compost from a system may be removed by the owner, a maintenance person, or a
licensed septage hauler. Compost has the potential to contain pathogenic organisms, and
caution and good hygiene are necessary when dealing with this material. The composted
material must be disposed of in one of the following ways:
a) Burial on the site or in another manner and location approved by the local Board of
Health, and covered with a minimum of six inches of clean compacted earth;
b) By a licensed septage hauler.
Places to try before you buy
Manufacturers should be able to give you a list of facilities you can visit. In addition.
there are a number of public facilities in Massachusetts that use composting toilets:
• Halibut Point State Park, Rockport,MA
• Johnny Appleseed Tourist Information Center,Route 2, Lancaster,MA
• Mass. Audubon, Visitor's Center, Wellfleet, MA
• Nickerson State Park, Brewster,MA
• Salisbury Beach, Salisbury,MA
• Walden Pond State Reservation,Concord,MA
• Wallum Lake, Douglas,MA
• Waquoit Bay National Estuarine Research Reserve, Waquoit, MA.
GREYWATER SYSTEMS
If a facility using a composting toilet generates greywater(i.e. wastewater from sinks,
showers,washing machines, etc.),a soil absorption system still is needed for its safe treatment
and disposal. A 2002 study by University of Massachusetts in Amherst(Greywater
Characterization And Treatment Efficiency) indicates that greywater,while containing less of
many pollutants than combined domestic wastewater,is still contaminated. It may contain toxic
chemicals, nutrients such as phosphorus and nitrogen, and pathogens, including bacteria and
viruses.
There are three approval options for greywater systems: Remedial Use, General Use for
New Construction, and Piloting Approvals. In addition to the information below, see DEP's
Technology Approval Process for UA Systems.
3
Using Composting Toilets and Greywater Systems in Massachusetts Revised April 2005
Remedial Use
Remedial Use Approvals(310 CMR 15.284)may be used for greywater systems in all
types of existing facilities(residential,commercial,or public)that meet three criteria:
a) Design flow of less than 10,000 gallons per day;
b) Served by an existing system which has failed, is failing or does not conform to Title
5 standards;
c)There is no proposed increase in the design flow from the facility.
Under remedial use, an existing cesspool may be used as a leaching pit under the
following conditions:
• The cesspool is pumped and cleaned when the other system components are installed;
• The bottom of the cesspool is located at least two feet above the high groundwater
elevation;
• The cesspool meets the design criteria of Title 5 (310 CMR 15.253) for depth,
separation between units, and inspection access, or the cesspool is replaced by a
precast concrete leaching pit meeting these requirements;
• The requirements of 310 CMR 15.242 on effluent loading rates are satisfied.
When greywater is to be discharged to a facility's existing soil absorption system and that
system has failed, a new soil absorption system is required. The soil absorption system may be
reduced by 40% from the size required by its Title 5 design flow(310 CMR 15.242). A new
septic tank also is required if a filter system approved by the DEP is not installed;note that to
date DEP has not approved any greywater filter systems. Since filters are plumbing fixtures
installed in a building,they would need to be on the list approved by the Board of Registration of
Plumbers and Gas Fitters,and an inspection by the local plumbing inspector is required.
Approval Process for Remedial Use: A Disposal System Construction Permit and
Certificate of Compliance must be obtained from the local Board of Health; no application to
DEP is required unless variances from Title 5 are being requested. If DEP variances are needed,
the applicant must apply for the variances first to the Board of Health and then to the appropriate
Regional Office of DEP using form BRP WP 59b(DEP Approval of Variance). See
http://www.mass.gov/dep/brp/wwm/t5forms.htm#ia for DEP Forms and Applications.
General Use for New Construction
Under Title 5,New Construction includes facilities built on an undeveloped lot and any
situation in which a facility increases its design flow,e.g., adding a bedroom to a home or adding
seats to a restaurant. In a facility with a composting toilet, if there is a greywater discharge or a
discharge from a drain equipped with a garbage grinder, a septic tank and soil absorption system
are required. A filter system specifically approved by DEP for this type of application can be
used instead of the septic tank;note that to date DEP has not approved any such filters. Since
filters are plumbing fixtures installed in a building,they would need to be on the list approved by
the Board of Registration of Plumbers and Gas Fitters,and an inspection by the local plumbing
inspector is required.
For greywater systems in New Construction,the size of the soil absorption system may
be reduced by 40%. However, in residential construction the site must be capable of providing
100%leaching capacity. This ensures that there will be available land for waste disposal in case
4
Using Composting Toilets and Greywater Systems in Massachusetts Revised April 2005
the current or subsequent property owners remove the composting toilets. Installations at
commercial and public facilities do not have to meet this requirement for a site with 100%
leaching capacity(2002 MGL,chapter 176, §3).
There is currently no nitrogen removal credit established for the use of composting
toilets; therefore,the loading on the lot cannot exceed 440 gallons per day per acre in a nitrogen
sensitive area(310 CMR 15.214).
Approval Process for New Construction: A Disposal System Construction Permit and
Certificate of Compliance must be obtained from the local Board of Health or approving
authority. No application to DEP is required, unless DEP variances to Title 5 are needed, in
which case the application also must be submitted to the appropriate Regional Office of DEP
using application form BRP WP 59b(DEP Approval of Variance). See
http://www.mass.gov/dep/brp/wwm/t5forms.htm#ia for DEP Forms and Applications.
Greywater Piloting Approvals
DEP issues Piloting Approvals for innovative greywater systems such as greywater
gardens. Piloting Approvals for New Construction must meet the conditions in 310 CMR 15.285.
The applicant must also show that a fully complying Title 5 system could be constructed on the
site, should the piloting project fail and require replacement. In addition, greywater systems with
Piloting Approval may be installed as Remedial Use systems to replace a failed,failing, or
nonconforming system.
DEP has approved alternative greywater systems to serve homes and public facilities
such as state parks and rest areas. Based on performance data from the Greywater Piloting
Program and information from the University of Massachusetts study, DEP has proposed
regulatory changes to Title 5 for greywater systems. In the meantime,DEP will continue to
accept applications for Piloting Approvals of greywater disposal or reuse projects.
Approval Process for Piloting: Applicants for a Piloting Approval must show through
available laboratory data, field-testing,previous use and other information that the system is
likely to be capable of providing a level of protection at least equivalent to a conventional Title 5
system. For installations in homes, commercial facilities, and local public facilities, the
applicant must first obtain Board of Health approval and then submit DEP application BRP
WP64b(Installation of Alternative Systems)to the Boston DEP. For state and federal public
facilities,applicants should submit BRP WP63 (Disposal System Construction Permit for State
and Federal Facilities)to the Boston DEP. See
http://www.mass.gov/dep/brp/wwm/t5forms.htm#ia For DEP Forms and Applications.
5
COMMONWEALTH OF MASSACHUSETTS
EXECUTIVE OFFICE OF ENVIRONMENTAL AFFAIRS
20141-7---=---=--7---- OF ENVIRONMENTAL PROTECTION
ONE WINTER STREET, BOSTON, MA 02108 617-292-5500
•
MITT ROMNEY STEPHEN R.PRIT(
Governor
Se
KERRY HEALEY ROBERT W.GOLLED
Lieutenant Governor Commi
INSPECTION AND SAMPLING IN TITLE 5 I/A SINGLE FAMILY HOME REMEDIAL AND
GENERAL USE TREATMENT SYSTEMS WITH DESIGN FLOWS LESS THAN 2000
GALLONS PER DAY
Effective date: January 1,2006 Policy/SOP/Guideline#:BRP/DWM/PeP-P06-1
Program Applicability: BRP, Watershed Permitting, Title 5
Approved by: Assistant Commissioner Regulation Reference:310 CMR 15.284, 15.287(2),
Glenn Haas 310 CMR 15.289(3)
• 310 CMR 15.202(4)(c)
Supersedes Policy/SOP/Guideline: NONE
PURPOSE:
This policy presents the Department's position on the appropriate inspection and sampling
schedule for Remedial Use and General Use Innovative/Alternative (I/A)Title 5 systems
installed at Single Family Homes(SFH).This policy amends the provisions for inspection
and sampling contained in Title 5,310 CMR 15.000 and the Department's approvals and
certifications for I/A Systems.
APPLICABILITY:
This policy is for SFH owners and operators who own,operate and/or maintain Remedial
and General Use systems,and for boards of health and Department staff that monitor
operation of such systems. This policy applies only to I/A systems that serve SFH facilities
with design flows of less than 2000 gallons per day(gpd).This policy does not prohibit
the local approving authority from requiring more frequent inspection and/or sampling.
This policy does not apply to nitrogen reducing systems Certified for General Use or
to Provisional or Piloting systems or to Remedial or General Use commercial
systems or systems with design flows of 2000 gpd or greater.
This information is available in alternate format.Call Donald 11.Comes,ADA Coordinator at 617-556-1057.TDD Service-1-800-298-2207.
DEP on the World Wde Web: http:l!www.mass.gov/dep
Phntea on Recycled Paper
I.e
Policy/SOP/Guideline#:
Page 2 of 4
INTRODUCTION:
Over 2000 Remedial and General Use UA Systems have been installed at SFH in
Massachusetts since the promulgation of 310 CMR 15.000 in 1995. Remedial Use systems,
installed to replace failed onsite systems,are designed to reduce biochemical oxygen demand
(BOD5) and total suspended solids(TSS)to 30 milligrams per liter(mg/L)or less. General Use
I/A systems can be installed either for nitrogen reduction or when the owner can demonstrate the
capability to install a standard Title 5 system. Some boards of health are requiring General Use
systems to be installed for new construction to meet local environmental limits.
The Department requires quarterly inspection and effluent sampling for pH, BOD5 and
TSS for the first year of operation in remedial situations. When approved by the Department,
sampling is reduced to an annual event after the first year. All SFH I/A systems Certified for
General Use must be inspected on a quarterly schedule, four times per year. The above
inspection provisions were adopted based on the Board of Certification of WWTP Operators
recommendations to ensure that the systems are correctly maintained and operated.
The Department has been collecting operating data on aerobic I/A systems, i.e.- trickling
filters, submerged media, RSF or other systems. This database indicates that these systems are
producing a higher quality effluent than required by the regulations; median BOD5 and TSS
values are 9.5 mg/L and 7.6 mg/L, respectively. Inspection reports for both Remedial and
General Use systems indicate that problems occur at a low incidence and are generally detected
by the onsite alarm system.
Accordingly, the Department will reduce the inspections required per year for SFH
Remedial and General Use systems and condition the requirement for sampling and laboratory
testing on SFH Remedial Use systems.
TEXT:
The Remedial Use technology approvals oblige the owner to have quarterly operation and
maintenance(0 & M) inspections conducted for the life of the system. In addition, the system
for the first year of operation must have quarterly effluent sampling for pH, BOD5 and TSS and
then an annual sample for those parameters. General Use systems that are not certified for
nitrogen reduction require quarterly inspection, without sampling, for the life of the system.
The I/A Program has reviewed the operations of the over 2000 aerobic Remedial and
General use I/A Systems installed on SFH in Massachusetts and has developed a new policy for
inspection and sampling. The continued sampling of the Remedial Use aerobic I/A systems is not
necessary except in special circumstances for the following reasons:
1. Systems approved by the Department for Remedial Use must have previously received
general use approval in other states.
2. There is generally a reasonable amount of information on operations in those states.
3. Field sampling of SFH systems only duplicates a process that has already been conducted in
other states.
4. The Department has reviewed over 4500 data points and found these systems provide good
effluent quality.
Pane 2 of 4
Policy/SOP/Guideline#:
Page 3 of 4
The Program has determined that under almost all circumstances a visual examination of
the effluent wastewater followed by simple field testing will demonstrate that the systems are
operating at secondary treatment standards, 30 mg/L of BODS and TSS. The Department will
now require that system operators perform and provide documentation for the following field
tests:
1. Visual examination of the effluent for color, turbidity and effluent solids,
2. Effluent pH to determine if the wastewater is between 6 and 9 standard units,
3. Dissolved oxygen,2 mg/L or more,to ensure that the system is operating,and
4. Turbidity, less than or equal to 40 NTU.
If the effluent does not pass all of the field tests than the operator will be required to collect a
sample for laboratory analysis.
Based on the preponderance of inspection reports submitted since 1996,the Program has
also determined that conducting four inspections per year is unnecessary for SFH systems. The
Program has determined that quarterly inspection does not improve operation or reduce system
failures. Remedial Use system will now require two inspections per year. During those
inspections the operator will conduct and document the field tests described above. Should the
system fail the field test, the operator will be required to collect an effluent sample for laboratory
testing. If the laboratory tests indicate that the system is not in compliance, the operator must
conduct a follow up inspection and field-testing to pinpoint the problem within 60 days of the
original inspection date. Should the subsequent inspection and field-test fail the operator shall
conduct a full evaluation within 30 days:
1. Including if necessary laboratory testing,and
2. Prepare and submit a report to the local approving authority that details the problems
and includes recommendations for repairing the system.
General Use systems are presumed equivalent to a standard Title 5 system. The Program
has determined that an annual inspection with one field test as described above is adequate.
Table 1, next page,presents the Program's inspection and sampling requirements for SFH
I/A systems with design flows of less than 2000 gpd. The table does not include inspection
requirements that the technology supplier specifies is necessary for start up and shut down of
these systems.
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Policy/SOP/Guideline#:
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Table 1. INSPECTION AND SAMPLING REQUIREMENTS FOR SFH REMEDIAL
AND GENERAL USE SYSTEMS
System Inspection Schedule Field Test Laboratory, Test
Type
Remedial Twice per year Visual,pH, DO,Turbidity pH. BOD5 and TSS'
General' Once per year Visual,pH, DO,Turbidity pH, BOD5 and TSS'
1 =Laboratory Test required only if system does not pass Field Test, follow up Inspection and Field Test within 60
days if Laboratory Test results do not meet the secondary treatment limits.
2=Systems Certified for General Use but not certified for nitrogen reduction.
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