271 (Girl Scouts) Alternative to Perc Testing 2000 ARGEO PAUL CELLUCCI
Governor
JANE SWIFT
Lieutenant Governor
COMMONWEALTH OF MASSACHUSETTS
EXECUTIVE OFFICE OF ENVIRONMENTAL AFFAIRS
DEPARTMENT OF ENVIRONMENTAL PROTECTION
ONE WINTER STREET, BOSTON, MA 02108 617-292-5500
September 22, 2000
Re: Revised Title 5 Policy on Alternative to Percolation Testing For
System Upgrades
Dear Board of Health Members:
BOB DURAND
Secretary
LAUREN A.LISS
Commissioner
Enclosed is the Department's revised Alternative to Percolation Testing Policy for System
Upgrades The revised policy reflects comments we received following issuance of the previous
version of the policy on January 7, 2000. Additionally, we submitted a draft version of the revised
policy to the Massachusetts Association of Health Boards for comment. Whereas the previous
version of the policy provided that all system upgrades with a variance from the requirement for
percolation testing designed for compacted soils would need an innovative/alternative(I/A)
treatment component, the revised policy does not automatically require I/A treatment systems on
such sites. The revised policy, unlike the previous version,also allows for a variance from the
percolation testing requirements even where both a reduction in the size of the soil absorption
system is necessary and the soils are compacted, provided that the system includes I/A treatment.
We also have made some revisions to the requirement for installation of a modified septic
tank. Under the revised policy,a modified septic tank is no longer required for all sites with
compacted soiis. And, in those cases where a modified septic tank would be necessary,we have
streamlined the requirements for the modified septic tank. Finally, along with some stylistic
changes, we have emphasized the need for the Board's concurrence as to whether the soils are
compacted or uncompacted as this factor,together with the soil class, is determinative of the
effluent loading rate for the system.
We appreciate the input the various Boards of Health provided us in the development of
this revised policy. Please note that the revised policy soon will appear on our Title 5 Publications
web site at www.state.ma.us/dep/btp/wwm.
Yours truly
Att-
Lealdon Langley, Dlregtor
Watershed Permitting Program
Cc: DEP Title 5 Regional contacts
This information is available in alternate format by calling our ADA Coordinator at t617t 574-6872.
DEP on the World Wide Web. bttp Owxw.state.ma.us/dep
0 Ported on Recycled Paper
schedule percolation testing during periods of low groundwater, or conduct dewatered percolation
testing. Additionally, the variance standards for new construction are more stringent than those
for system upgrades. Accordingly, the alternative described in this policy does not apply to cases
of new construction, including increases in design flow.
Title 5 requires percolation testing to be performed in the most restrictive soil layer of the
naturally occurring pervious material beneath a proposed soil absorption system (SAS). The
Department recognizes that at certain times, however, high groundwater conditions preclude
performance of standard percolation tests. During such times, the applicant may choose to
perform dewatered percolation testing. Provided that an immediate upgrade is not being required
by the local approving authority or DEP,or the upgrade timelines in 310 CMR 15.305, if
applicable, would not be violated, the applicant also may wait until groundwater has receded
and standard percolation testing can be performed. Alternatively, in accordance with this policy,
the applicant may apply for a variance from the requirements for percolation testing.
Dewatered percolation testing involves lowering the groundwater table to a point where
testing can be performed in accordance with Title 5. Since dewatered percolation testing
frequently is difficult and, in many cases, infeasible, attempting dewatered percolation testing is
not a prerequisite for obtaining a variance under this policy.
Impervious & extremely low permeability soils
In cases of impervious soils or soils with extremely low permeability,the alternatives set
forth in this policy are not appropriate as such soils simply cannot support an on-site system. Where
the Soil Evaluator, the local approving authority,or DEP determines that the soils are impervious or
of extremely low permeability, for example,due to the presence of ledge,greater than 40%clay,or
highly compacted till, and there is no feasible alternative(e.g. a shared system),then a tight tank to
eliminate a failed system, approved under 310 CMR 15.260,would be the only option.
Requirements for obtaining a variance from the percolation testing provisions
When an applicant proposes to upgrade a system, percolation testing cannot be performed
due to high groundwater and the soils are neither impervious nor of extremely low permeability,
the Department may approve a variance from the Title 5 percolation testing requirements. In
addition to complying with the other requirements of Title 5, the variance application to the local
approving authority and to the Department(DEP permit application BRPWP59b)must contain the
following:
1. documentation of a demonstration that percolation testing cannot be performed;
2. the Soil Evaluator's determination, along with the written concurrence of the local
approving authority, of whether the soils are uncompacted or compacted;
3. results of performance of a Particle Size Analysis by a soils laboratory;
4. the Soil Evaluator's determination of the soil type, which must be based on the Particle
Size Analysis and the USDA Soil Textural Triangle in Title 5; and
5. the Soil Evaluator's determination of the soil class under 310 CMR 15.243, which must
be based on the soil type. and
PERC9.DOC 9/5/2000 2
ARGEO PAUL CELLUCCI
Governor
JANE SWIFT
Lieutenant Governor
COMMONWEALTH OF MASSACHUSETTS
EXECUTIVE OFFICE OF ENVIRONMENTAL AFFAIRS
DEPARTMENT OF ENVIRONMENTAL PROTECTION
ONE WINTER STREET, BOSTON, MA 02108 617-292-5500
BOB DURAND
Secretary
LAUREN A.LISS
Commissioner
TITLE 5 ALTERNATIVE TO PERCOLATION TESTING POLICY FOR SYSTEM
UPGRADES
Effective Date: September 8, 2000 Policy#: BRP/DWM/PeP-P00-4
Program Applicability: BRP/DWM/Watershed Permitting/Title 5 Program
Supersedes Policy#: BRP/DWM/PeP-P00-1, dated January 7, 2000
Regulation Reference: 310 CMR 15.104
Approved by: Arleen O'Donnell (signed)
Purpose: This document contains the Title 5 Program's policy for reviewing applications
for variances from the percolation testing requirements of Title 5 for the upgrade
of on-site sewage treatment and disposal systems.
Applicability: This policy applies to applications for variances from the Title 5 requirements to
conduct percolation testing for proposed system upgrades only. The alternative to
percolation testing set forth in this policy may be used, under a variance from Title
5, when percolation testing is not possible due to high groundwater and the
applicant seeks to proceed with a system upgrade, rather than wait for groundwater
to recede to perform percolation tests.
The alternative outlined in this policy may be used only for the repair or upgrade of an
existing system when no increase in design flow is proposed. Under the Title 5 variance
provisions,310 CMR 15.410 through 310 CMR 15.412,approval for a variance from the
requirement for percolation tests must be obtained first from the Board of Health,when the
Board of Health is the local approving authority, and then from the Department.
Title 5, 310 CMR 15.104,requires percolation testing as part of the site evaluation for a
new system or a system upgrade. An applicant for a system to serve a new facility or for an
increase in design flow(i.e. "new construction" as defined in Title 5), in many cases, can wait and
This information is available in alternate format b)calling our ADA Coordinator at(617)574-6872.
DEP on the World Wide MD ide Web. M Mmw.magnel.state ma.us/dep
", Printed on Recycled Paper
6) Design Criteria— uncompacted vs. compacted soils
a) For uncompacted Class I and uncompacted Class H soils, the results of the particle
size analysis the soil type and the soil classification must be used to determine the effluent
loading rate based on the effluent loading rate table, below. The system upgrade must be designed
with that effluent loading rate and the requirements of Title 5.
b) For compacted soils and all Class III and all Class IV soils the design criteria, set
forth below, must be used to design the system upgrade. Where the soils are compacted or Class
III or Class IV soils, extremely low permeability could limit the soils' ability to adequately accept
a subsurface discharge. These systems, therefore,must have a conservative design, intended both
TO allow an on-site discharge and prevent breakout. hi addition to meeting Title 5 requirements,
the design criteria for a system upgrade in compacted soils and in Class III and Class IV soils arc
as follows:
1. in accordance with the Effluent Loading Rate table, below, the effluent loading rate is
limited to 0.15 gallons per day(gpd)per square foot (sf);
2. pressure distribution is required;
3. a four foot vertical separation to high groundwater elevation, or a five separation in
soils greater than 85% sand. Where the required separation to the high groundwater
elevation will not be met an Innovative/Alternative(VA) treatment technology
approved by DEP for Remedial Use is required and the local approving authority and
DEP may approve a reduction down to a minimum of a two foot separation to high
groundwater elevation, or a three foot separation in soils that are greater than 85%
sand;
4. where feasible, four feet of naturally occurring pervious material. Where there are not
four feet of naturally occurring pervious material, the applicant must satisfy the
requirements of 310 CMR 15.415 for the siting of a system upgrade with less than four
feet of naturally occurring pervious material and an I/A treatment technology approved
by DEP for Remedial Use is required. In such cases, the local approving authority and
DEP may approve a reduction to a minimum of two feet of naturally occurring
pervious material;
5. where feasible, a fully sized SAS. Where a fully sized SAS is not feasible,then an I/A
treatment technology approved by DEP for Remedial Use is required and the local
approving authority and DEP may approve a reduction of up to 50% in the required
SAS size;
6. a modified septic tank is required where there will be a reduction in the required four
or five foot separation to high groundwater elevation, or a reduction in the required
four feet of naturally occurring pervious material,or a reduction in the required SAS
size. The modified septic tank shall have a valve located in the septic tank discharge
pipe so that in the event of breakout or other hydraulic failure, the discharge pipe valve
could be closed and sealed and the discharge pipe beyond the valve removed,
converting the septic tank to a tight tank. If converted to a tight tank, the volume of the
septic tank, together with that of the pump chamber, may be used to meet the
requirements for tight tank size in 310 CMR 15.260(2)(a);
PERC9.00C 9/5/2000 .},
6. plans for a system upgrade designed in accordance with the criteria in this policy for the
soil type, class and determination of soil compaction.
1) Demonstration that percolation testing cannot be performed
Percolation testing must be attempted in the presence of the local approving authority, or
its authorized representative, and determined not to be possible due to high groundwater.
2) Determination of compacted vs. uncompacted soils
Without the benefit of percolation testing, more reliance is placed on the determination of
soil compaction. Since compacted soils can be extremely firm in place,but friable when removed
for a sample,the Soil Evaluator must make an in-situ determination of the soil structure and
consistence. The Soil Evaluator, with the written concurrence of the local approving
authority, must determine whether the soils in the area of the proposed SAS are compacted or
uncompacted. The Soil Evaluator must use the techniques described in Appendix 1.
For uncompacted soils, the Soil Evaluator can use the results of the particle size analysis
to determine the soil type and class, and, subsequently,the effluent loading rate. In compacted
soils, such as dense, compact till, the compacted nature of the material results in a significant
decrease in the amount of pore space necessary for groundwater flow and particle size analysis
results alone are inadequate for determining an effluent loading rate.
3) Particle Size Analysis
In the presence of the local approving authority or its authorized representative,the Soil
Evaluator must obtain a soil sample from the most restrictive layer of the four feet of naturally
occurring pervious material for the particle size analysis. Although for purposes of obtaining an
effluent loading rate, the particle size analysis is considerably more useful in the case of
uncompacted soils, the analysis still is useful to characterize compacted soils,particularly where
the soils have a high percentage of clay.
The particle size analysis,performed by a qualified soils laboratory, must be used to
determine the percentages of sand, silt and clay in the soil sample. The analysis must be
performed for both compacted and uncompacted soils. The particle size analysis must be
performed in accordance with Appendix 2.
4) Determination of soil type
Once the relative percentages of sand, silt and clay have been determined through particle
size analysis,the Soil Evaluator must use the USDA Soil Textural Triangle in 310 CMR
15.243(2) to determine the soil type.
5) Determination of soil class
Based on the soil type, the Soil Evaluator must classify the soil into one of the four soil
textural classes described in 310 CMR 15.243 (1).
PERC9.000 9/5/2000
3
Variance application process
Where the Board of Health is the local approving authority for the system upgrade and a
variance from the percolation testing requirements of the Code is sought, the variance first must
be granted by the Board of Health and then approved by the Department. The variance applicant
must satisfy the variance criteria in 310 CMR 15.410(1). DEP's approval of such variances will
be predicated on the applicant following the requirements of this policy.
The DEP variance application package BRPWP 59b must be used and is available at the
Department's Regional Offices, Boston service center, and the DEP web page,
www.state.ma.us dep. Such applications should be submitted to the appropriate DEP regional
office. The Department's Regional Offices and the Title 5 program in Boston may grant
approval for a variance from the percolation testing requirements of Title 5 due to high
groundwater,for a system upgrade, only in accordance with this policy.
APPENDIX I
On-site investigation techniques to determine if soils are compacted (compact till):
• Note the ease or difficulty of excavation by the backhoe(does the excavator
experience difficulty digging, does the bucket chatter across the surface of the
material making shallow cuts with each pass—these soils may be compacted).
• Pick at the side of a test hole with a knife or hand tool to feel for the ease or
difficulty of penetration(difficulty would suggest compacted material).
• Note the presence of angular shaped rock fragments (suggests compacted till).
• Note the speed at which groundwater weeps into the pit ( groundwater weeping
slowly into the pit would suggest dense, compacted material).
• Note the consistency of undisturbed soil clod (squeeze the clod of soil between
your thumb and index finger; initially compact till will resist crushing and then
with increased pressure will rupture suddenly). The consistency of soil in
compacted material will be firm,whereas in uncompacted material, the consistency
will be loose or friable.
• Note the soil saturation (compacted soils will appear moist, not saturated, due to
the lack of pore space).
Adapted from the DEP approved Title 5 Soil Evaluator Course Materials
APPENDIX 2
The standard method for Particle Size Analysis is the method of Gee and Bauder(1986) in
Methods of Soil Analysis, Part 1. Physical and Mineralogical Methods, 2nd Edition
published by the American Society of Agronomy-Soil Science Society of America. This method,
or another method acceptable to the Department, must be used by the soils laboratory. The soils
laboratory must:
PERC9.000. 9/5/2000 ' '
7. a variance condition that prohibits any increase in design flow and requires a notice,
recorded with the deed, that both prohibits any increase in design flow and references
DEP's approval letter of the variance.
Under a variance from the requirement for percolation testing issued under this policy,the
local approving authority and the Department may approve an PA system with one reduction
criterion(# 3, #4 or#5, as described above),but not more than one. For such systems, no
variance for the one reduction would be required beyond the variance from the requirement for
percolation testing. A system upgrade requiring more than one reduction would require local
approving authority and then DEP approval under BRPWP64c - approval of an alternative system
for remedial use. Such applications to DEP should be submitted to the appropriate DEP regional
office.
A system designed for compacted soils or Class III or Class IV soils,without the benefit of
percolation testing, is a high risk option; it does not guarantee that sewage breakout or backup will
not occur. Accordingly, any variance approval letter issued under this policy for such a system must
provide that should the system fail,the system owner shall immediately notify the Board of Health
and the Department, in writing,and then proceed with an appropriate upgrade. Additionally,
variance approval letters for systems designed under this policy with an VA treatment technology
and a reduction in the required separation to high groundwater,the depth of naturally occurring
pervious material or the SAS size, should contain a condition requiring the system owner to: a) by
45 days of a system failure, submit to the Department a complete application, including the local
approving authority approval, for tight tank approval; b)by 14 days of issuance of the
Department's tight tank approval, apply for a Disposal System Construction Permit from the local
approving authority; and c)by 14 days of issuance of the permit, complete conversion of the system
to or installation of the tight tank. Following any system failure,the Department and the local
approving authority may require such interim measures as they deem appropriate.
Effluent Loading Rates for systems designed with a variance approved under this policy
Soil Type
Uncompacted All compacted soils and
Class I and Class II Soils' all Class III and all Class IV Soils2
Class I > 85%sand 0.74 gpd/sf
70—85%sand 0.66 gpd/sf
Class II 0.33 gpd/sf
0.15 gpd/sf
1 The system must be designed based on the applicable effluent loading rate in this table and the
requirements of Title 5.
2 The system must be designed based on a 0.15 gpd/sf loading rate,the design
criteria on page 4 of this policy, and the requirements of Title 5.
PERC9.DOC 9/5/2000 5
• determine the relative percentages of sand, silt and clay from the soil sample that
passes through a#10 sieve, (which removes aggregate from the sample),
• use a#270 sieve to separate the sand fraction from the remaining combined silt and
clay fraction,
• establish the relative percentages of silt and clay in the sample by either pipet or
hydrometer method.
PERC9.DOC 9/5/2000