Stormwater Atlas

← Practices

Manufactured Treatment Device

Generated 8/13/2026, 10:42:39 AM · composer-2.5:run-21133007-265c-47a8-8d25-711e7159a0bb

Provisional practice synthesis — not a design manual or adopted regulation. Numbers come from atlas design_parameters; verify against source PDFs. Controlling state/local criteria apply when more stringent.

National baseline

Among Tier A manuals that mention manufactured treatment devices, numeric guidance for this practice is largely expressed through site-wide water-quality volume (WQv), drawdown, and seasonal high water table (SHWT) separation requirements that apply to the development or BMP portfolio—not as device-specific depth, detention, or setback numbers for the unit itself. Where WQv depth is stated (n=30), the mode and median are both 1 inch, with reported values from about 0.37 to 1.61 inches across jurisdictions such as Boston, Baltimore, Chesapeake, Detroit, and many state manuals. Maximum drawdown time appears in 36 manuals with a mode of 72 hours and median of 48 hours, spanning roughly 4 to 120 hours (e.g., Florida FSESCI Tier 1 at 4 hours, Mississippi at 120 hours, and many manuals at 48 or 72 hours). SHWT separation is documented in 36 manuals with a mode of 24 inches and median of 36 inches, over a range of 12 to 120 inches. Committee discussion should treat these figures as the temperate, Type II–ish jurisdictional sizing context in which MTDs are typically sized and credited, pending practice-specific baselines where manuals do not isolate MTD geometry or hydraulics.

Matrix summary

From Tier A manuals mentioning manufactured treatment (37/76), extracted site-wide numerics show WQv depth n=30 with mode and median 1 inch (range 0.37–1.61 in.), max drawdown n=36 with mode 72 hours and median 48 hours (range 4–120 hr), and SHWT separation n=36 with mode 24 in. and median 36 in. (range 12–120 in.); these counts reflect jurisdictional sizing context cited alongside MTD practice mentions, not a unified national standard for device geometry or performance.

Cross-state parameters

Site water-quality depth (not practice-specific)

n=30 · mode=1 · median=1 · range=0.37–1.61 inches

StateSlugValue
MAboston-ma1 inches
MDbaltimore-md1 inches
VAchesapeake-va1 inches
MIdetroit-mi1 inches
AZflagstaff-az1 inches
TXhouston-tx0.5 inches
MNminneapolis-mn1.25 inches
VAnorfolk-va1 inches
ORportland-or1.61 inches
NVlas-vegas-nv0.37 inches
CTct-state1.3 inches
TXdallas-tx1.5 inches
GAga-state1.2 inches
INindiana-manual1 inches
IAia-state-ch11.25 inches
MEmaine-manual1 inches
MAma-state-draft1 inches
MImichigan-manual1 inches
MOkansas-city-marc-bmp1.37 inches
NEne-ndot-stf0.5 inches
NHnh-state1 inches
NYny-state1.2 inches
NCnc-state1 inches
OHohio-rainwater0.75 inches
PApa-state1.2 inches
PAphiladelphia-pa1.5 inches
RIri-state1 inches
HIhawaii-dot-pcbmp1 inches
COdenver-co0.6 inches
VTvt-state1 inches
WVwest-virginia-manual1 inches

Max drawdown / dewatering time

n=36 · mode=72 · median=48 · range=4–120 hours

StateSlugValue
ALalabama-handbook40 hours
NMalbuquerque-nm-gsi96 hours
CAca-casqa-municipal72 hours
CAca-caltrans-construction96 hours
IDboise-id48 hours
VAchesapeake-va48 hours
ILchicago-il72 hours
OHcolumbus-oh72 hours
AZflagstaff-az24 hours
TXhouston-tx48 hours
ORportland-or30 hours
WAseattle-wa24 hours
NVlas-vegas-nv72 hours
CTct-state48 hours
CAlos-angeles-ca96 hours
DEde-wet-ponds-draft24 hours
FLfl-fsesci-tier14 hours
IDidaho-bmp-catalog72 hours
INindiana-manual24 hours
MEmaine-manual48 hours
MDmd-state24 hours
MAma-state-draft72 hours
MOkansas-city-marc-bmp40 hours
MNmn-state-200848 hours
MSms-state-vol2120 hours
MTbillings-mt72 hours
MTmt-deq872 hours
NEne-ndot-stf72 hours
NJnj-state72 hours
PApa-state72 hours
PAphiladelphia-pa72 hours
RIri-state48 hours
SCsouth-carolina-manual72 hours
HIhawaii-dot-pcbmp48 hours
TNtn-state24 hours
VTvt-state48 hours
WAwa-state-western48 hours
WVwest-virginia-manual48 hours

SHWT separation

n=36 · mode=24 · median=36 · range=12–120 inches

StateSlugValue
ALalabama-handbook24 inches
NMalbuquerque-nm-gsi36 inches
WAbellevue-wa60 inches
IDboise-id36 inches
VAchesapeake-va12 inches
ILchicago-il24 inches
MIdetroit-mi24 inches
TXhouston-tx48 inches
MNminneapolis-mn36 inches
ORportland-or60 inches
NCraleigh-nc12 inches
CAsan-diego-ca120 inches
NVlas-vegas-nv24 inches
CTct-state36 inches
DEde-wet-ponds-draft24 inches
DCdc-guidebook24 inches
IDidaho-bmp-catalog36 inches
INindiana-manual36 inches
MEmaine-manual12 inches
MDmd-state48 inches
MAma-state-draft24 inches
MOkansas-city-marc-bmp36 inches
MNmn-state-200836 inches
MSms-state-vol224 inches
MTbillings-mt36 inches
MTmt-deq812 inches
NJnj-state12 inches
NYny-state24 inches
OHohio-rainwater48 inches
PApa-state24 inches
PAphiladelphia-pa24 inches
RIri-state36 inches
HIhawaii-dot-pcbmp36 inches
TNtn-state24 inches
TXtx-edwards-rg34848 inches
VTvt-state36 inches
WAwa-state-western60 inches
WVwest-virginia-manual24 inches

Regional modifiers

Cold climate and shorter seasons

Northern and mountain jurisdictions often pair WQv near 1 to 1.25 inches (e.g., Minneapolis 1.25, Iowa chapter proxy 1.25, Maine and Michigan state guidance at 1 inch) with drawdown commonly at 48 hours (Minnesota state 2008, Maine, Vermont, Washington western) or 72 hours (Montana Billings, Montana DEQ-8, Nebraska NDOT STF). SHWT separation frequently sits at 36 inches (Minnesota, Idaho BMP catalog, Missouri MARC, Montana Billings) though Montana DEQ-8 lists 12 inches. Cold-climate MTD siting and maintenance access may need to align with these longer or stricter site-wide rules even when the device is proprietary.

States: MN, ME, MI, VT, WA, MT, ID, IA, NH. Sources: minneapolis-mn, mn-state-2008, maine-manual, michigan-manual, vt-state, wa-state-western, billings-mt, mt-deq8, idaho-bmp-catalog, ia-state-ch1, nh-state, kansas-city-marc-bmp

Coastal and high water table

Coastal and low-lying manuals sometimes specify tighter SHWT separation at 12 inches (Chesapeake VA, Raleigh NC, Maine, Montana DEQ-8, New Jersey chapter proxy) while others use 24 to 48 inches in the same regions (Norfolk-adjacent Chesapeake drawdown 48 hours; Maryland state 48 inches SHWT; Houston 48 inches). WQv remains commonly 1 inch in Chesapeake, Norfolk, and Baltimore contexts. MTD installations in these areas inherit site-wide separation minima that may constrain vault depth and infiltration assumptions more than device-rated performance alone.

States: VA, NC, ME, NJ, MD, TX. Sources: chesapeake-va, raleigh-nc, maine-manual, nj-state, md-state, houston-tx, norfolk-va, baltimore-md

Arid and semi-arid

Arid jurisdictions show wider spread on site-wide WQv and drawdown: Las Vegas lists 0.37 inch WQv with 72-hour drawdown and 24-inch SHWT; Flagstaff uses 1 inch WQv, 24-hour drawdown; Denver 0.6 inch WQv; Albuquerque GSI 96-hour drawdown with 36-inch SHWT. California municipal and Caltrans construction manuals cite 72 to 96-hour drawdown. MTD sizing in these climates should be read against lower WQv depths and sometimes longer drawdown targets at the site scale rather than a single national MTD hydraulic standard.

States: NV, AZ, CO, NM, CA. Sources: las-vegas-nv, flagstaff-az, denver-co, albuquerque-nm-gsi, ca-casqa-municipal, ca-caltrans-construction, los-angeles-ca

Karst and Edwards-related groundwater

Where karst or sensitive aquifer guidance appears in the matrix, SHWT separation can reach 48 inches (Texas Edwards RG-348, Ohio rainwater manual, Houston), contrasting with 12-inch minima elsewhere. WQv and drawdown in those slugs align with broader state or city values (e.g., Ohio 0.75 inch WQv, 48-inch separation). MTD projects in karst-influenced jurisdictions may face stricter vertical separation context without a distinct MTD-only numeric baseline in Tier A extracts.

States: TX, OH. Sources: tx-edwards-rg348, houston-tx, ohio-rainwater

Open issues

Tier A coverage mentions manufactured treatment in 37 of 76 scanned manuals, but nearly half of the pool lacks extracted numeric values for WQv depth (45 missing), drawdown (38 missing), and SHWT separation (38 missing), so national numeric consensus for MTD-specific design—treatment flow path, internal storage, maintenance frequency, and independent verification—is not established from this matrix. Site-wide mode values (1 inch WQv, 72-hour drawdown mode with 48-hour median, 24-inch SHWT mode with 36-inch median) describe jurisdictional stormwater sizing context, not verified facility specifications for proprietary devices. Extreme drawdown outliers (4 hours in Florida FSESCI Tier 1, 120 hours in Mississippi) and SHWT span (12 to 120 inches, including San Diego 120 inches) indicate regional policy divergence that the synthesis does not resolve into a single MTD design envelope. Chapter proxies and draft manuals in the extract set add uncertainty for committees seeking adopted language.