Aggregate lab data for the MARSH soil series. This aggregation is based on all pedons with a current taxon name of MARSH, and applied along 1-cm thick depth slices. Solid lines are the slice-wise median, bounded on either side by the interval defined by the slice-wise 5th and 95th percentiles. The median is the value that splits the data in half. Five percent of the data are less than the 5th percentile, and five percent of the data are greater than the 95th percentile. Values along the right hand side y-axis describe the proportion of pedon data that contribute to aggregate values at this depth. For example, a value of "90%" at 25cm means that 90% of the pedons correlated to MARSH were used in the calculation. Source: KSSL snapshot (updated 2020-03-18). Methods used to assemble the KSSL snapshot used by SoilWeb / SDE
Pedons used in the lab summary:
MLRA | Lab ID | Pedon ID | Taxonname | CI | NSSL / NASIS Reports | Link To SoilWeb GMap |
---|---|---|---|---|---|---|
22A | 05N0019 | 04NV005001 | Marsh | 7 | Primary | Supplementary | Taxonomy | Pedon | Water Retention | Correlation | Andic Soil Properties | 39.1642456,-119.8968735 |
Monthly water balance estimated using a leaky-bucket style model for the MARSH soil series. Monthly precipitation (PPT) and potential evapotranspiration (PET) have been estimated from the 50th percentile of gridded values (PRISM 1981-2010) overlapping with the extent of SSURGO map units containing each series as a major component. Monthly PET values were estimated using the method of Thornthwaite (1948). These (and other) climatic parameters are calculated with each SSURGO refresh and provided by the fetchOSD function of the soilDB package. Representative water storage values (“AWC” in the figures) were derived from SSURGO by taking the 50th percentile of profile-total water storage (sum[awc_r * horizon thickness]) for each soil series. Note that this representation of “water storage” is based on the average ability of most plants to extract soil water between 15 bar (“permanent wilting point”) and 1/3 bar (“field capacity”) matric potential. Soil moisture state can be roughly interpreted as “dry” when storage is depleted, “moist” when storage is between 0mm and AWC, and “wet” when there is a surplus. Clearly there are a lot of assumptions baked into this kind of monthly water balance. This is still a work in progress.
Siblings are those soil series that occur together in map units, in this case with the MARSH series. Sketches are arranged according to their subgroup-level taxonomic structure. Source: SSURGO snapshot (updated 2024-10-24), parsed OSD records (updated 2025-02-20) and snapshot of SC database (updated 2025-02-20).
Select annual climate data summaries for the MARSH series and siblings. Series are sorted according to hierarchical clustering of median values. Source: SSURGO map unit geometry and 1981-2010, 800m PRISM data (updated 2024-10-23).
Geomorphic description summaries for the MARSH series and siblings. Series are sorted according to hierarchical clustering of proportions and relative hydrologic position within an idealized landform (e.g. top to bottom). Most soil series (SSURGO components) are associated with a hillslope position and one or more landform-specific positions: hills, mountain slopes, terraces, and/or flats. Proportions can be interpreted as an aggregate representation of geomorphic membership. The values printed to the left (number of component records) and right (Shannon entropy) of stacked bars can be used to judge the reliability of trends. Small Shannon entropy values suggest relatively consistent geomorphic association, while larger values suggest lack thereof. Source: SSURGO component records (updated 2024-10-23).
There are insufficient data to create the 3D mountains figure.
Soil series competing with MARSH share the same family level classification in Soil Taxonomy. Source: parsed OSD records (updated 2025-02-20) and snapshot of the SC database (updated 2025-02-20).
Select annual climate data summaries for the MARSH series and competing. Series are sorted according to hierarchical clustering of median values. Source: SSURGO map unit geometry and 1981-2010, 800m PRISM data (updated 2024-10-23).
Geomorphic description summaries for the MARSH series and competing. Series are sorted according to hierarchical clustering of proportions and relative hydrologic position within an idealized landform (e.g. top to bottom). Proportions can be interpreted as an aggregate representation of geomorphic membership. Most soil series (SSURGO components) are associated with a hillslope position and one or more landform-specific positions: hills, mountain slopes, terraces, and/or flats. The values printed to the left (number of component records) and right (Shannon entropy) of stacked bars can be used to judge the reliability of trends. Shannon entropy values close to 0 represent soil series with relatively consistent geomorphic association, while values close to 1 suggest lack thereof. Source: SSURGO component records (updated 2024-10-23).
There are insufficient data to create the 3D mountains figure.
Soil series sharing subgroup-level classification with MARSH, arranged according to family differentiae. Hovering over a series name will print full classification and a small sketch from the OSD. Source: snapshot of SC database (updated 2025-02-20).
Click a link below to display the diagram. Note that these diagrams may be from multiple survey areas.
Soil associations and relief in Buffalo County. 1. Silty soils of the rolling limestone uplands and Steep stony and rocky land: Dubuque, Fayette, Steep stony and rocky land. 2. Loamy soils of the rolling to hilly sandstone uplands: Gale, Hixton. 3. Sandy soils of the rolling to hilly sandstone uplands: Boone, Hixton. 4. Sandy soils of stream terraces: Sparta, Plainfield. 5. Silty soils of stream terraces: Bertrand, Richwood. 6. Loamy terrace soils underlain by sand on stream terraces: Meridian, Tell. 7. Wet organic and mineral soils of bottom lands: Peat and Muck, Ettrick, Wallkill. 8. Soils of overflow bottom lands: Loamy alluvial lands, Marsh (Soil Survey of Bayfield County, WI; 1961).
Map units containing MARSH as a major component. Limited to 250 records.
Map Unit Name | Symbol | Map Unit Area (ac) | Map Unit Key | National Map Unit Symbol | Soil Survey Area | Publication Date | Map Scale |
---|---|---|---|---|---|---|---|
Marsh | 106 | 20 | 55042 | 1v8k | az671 | 2000 | 1:24000 |
Marsh | Mh | 715 | 457433 | hbzx | ca672 | 1966 | 1:20000 |
Marsh | Ma | 1114 | 498663 | jqwx | co631 | 1972 | 1:24000 |
Marsh | Ma | 1413 | 498548 | jqs6 | co632 | 1968 | 1:24000 |
Marsh | MZ | 803 | 468183 | hq5p | hi950 | 1966 | 1:24000 |
Marsh | MZ | 605 | 467866 | hpvg | hi960 | 1967 | 1:24000 |
Marsh | MZ | 877 | 468461 | hqgn | hi990 | 1966 | 1:24000 |
Marsh | 354 | 348 | 402679 | 2zv8t | ia007 | 1970 | 1:15840 |
Marsh, deep loess | 354 | 1990 | 406135 | 2zv8s | ia071 | 1968 | 1:20000 |
Marsh | 354 | 324 | 406380 | fmw1 | ia077 | 1968 | 1:15840 |
Marsh, deep loess | Z354 | 9 | 3291380 | 2zv8s | ia077 | 1968 | 1:15840 |
Marsh | 354 | 464 | 408458 | 2zv8t | ia111 | 1976 | 1:15840 |
Marsh | 354 | 1094 | 410278 | frxs | ia147 | 1973 | 1:15840 |
Marsh | 354 | 264 | 410801 | fsgn | ia161 | 1975 | 1:15840 |
Marsh | Ma | 1343 | 80797 | 2q2c | id665 | 1967 | 1:20000 |
Marsh | Mh | 697 | 79952 | 2p63 | id770 | 1968 | 1:24000 |
Marsh | Mh | 384 | 272468 | 94j9 | in089 | 1967 | 1:15840 |
Marsh | Mb | 2087 | 272542 | 94lp | in113 | 1974 | 1:15840 |
Marsh | 9985 | 145 | 1151987 | 17nqw | ks171 | 1963 | 1:24000 |
Marsh | 9985 | 3529 | 1443687 | 1kg8k | ks185 | 1975 | 1:24000 |
Marsh | Mh | 1263 | 1588081 | 1q9jf | mi041 | 1969 | 1:24000 |
Marsh | Ma | 1441 | 187359 | 68yv | mi121 | 1966 | 1:15840 |
Marsh | Me | 991 | 192688 | 6ghr | mi139 | 1967 | 1:15840 |
Marsh | Mb | 904 | 3015048 | 6bkg | mi163 | 1974 | 1:12000 |
Marsh | Mc | 8522 | 395951 | f90m | mn003 | 1972 | 1:15840 |
Marsh | 1053 | 2346 | 396123 | f965 | mn013 | 1975 | 1:12000 |
Marsh | Ma | 5432 | 428033 | gcdj | mn139 | 1988 | 1:20000 |
Marsh | Mh | 762 | 428275 | gcnb | mn147 | 1967 | 1:20000 |
Marsh | MR | 3472 | 2375429 | 2kqtr | ms011 | 1956 | 1:20000 |
Marsh | MR | 4252 | 2108931 | 28sj1 | ms027 | 1956 | 1:24000 |
Marsh | MA | 3656 | 2027392 | 261nr | ms053 | 1956 | 1:20000 |
Marsh | Me | 1592 | 347100 | cn5s | mt611 | 1971 | 1:24000 |
Marsh-Crooked Creek complex | Mc | 230 | 476111 | hzff | nv612 | 1968 | 1:24000 |
Fresh water marsh | FW | 494 | 2711241 | 230w | or071 | 1967 | 1:24000 |
Marsh | Mh | 437 | 1479563 | 1lnlv | pa101 | 1971 | 1:15840 |
Marsh-Stiversville complex, 15 to 35 percent slopes, severely eroded | MaE3 | 5410 | 524084 | klby | tn117 | 1999 | 1:24000 |
Culleoka flaggy loam, eroded steep phase | Ch | 1338 | 527755 | kq5c | tn119 | 1955 | 1:20000 |
Culleoka clay loam, severely eroded moderately steep phase | Cd | 723 | 527751 | kq57 | tn119 | 1955 | 1:20000 |
Culleoka flaggy clay loam, severely eroded steep phase | Cf | 545 | 527753 | kq59 | tn119 | 1955 | 1:20000 |
Culleoka loam, eroded moderately steep phase | Ck | 402 | 527756 | kq5d | tn119 | 1955 | 1:20000 |
Culleoka flaggy clay loam, severely eroded moderately steep phase | Ce | 56 | 527752 | kq58 | tn119 | 1955 | 1:20000 |
Culleoka flaggy loam, eroded moderately steep phase | Cg | 32 | 527754 | kq5b | tn119 | 1955 | 1:20000 |
Marsh channery silt loam, 12 to 35 percent slopes, severely eroded | MaE3 | 189 | 560633 | ltcy | tn135 | 2000 | 1:24000 |
Hicks silt loam, 5 to 12 percent slopes, eroded | HnC2 | 968 | 523526 | kkry | tn187 | 1961 | 1:15840 |
Hicks silt loam, 2 to 5 percent slopes, eroded | HnB2 | 251 | 523525 | kkrx | tn187 | 1961 | 1:15840 |
Hicks silty clay loam, 5 to 12 percent slopes, severely eroded | HoC3 | 138 | 523527 | kkrz | tn187 | 1961 | 1:15840 |
Marsh | Mh | 1405 | 70112 | 2byp | wa619 | 1968 | 1:24000 |
Marsh | Mr | 841 | 426214 | g9hv | wi009 | 1970 | 1:20000 |
Marsh | Mb | 1647 | 423299 | g6gt | wi021 | 1972 | 1:15840 |
Marsh | Mb | 1645 | 753534 | t93k | wi025 | 1972 | 1:15840 |
Marsh | Mf | 1243 | 425515 | g8s9 | wi039 | 1967 | 1:15840 |
Marsh | Mf | 478 | 423720 | g6xd | wi047 | 1974 | 1:20000 |
Marsh | Mf | 429 | 3268668 | g78c | wi059 | 2023 | 1:15840 |
Marsh | Ma | 336 | 424844 | g82n | wi065 | 1964 | 1:15840 |
Marsh | Ma | 1151 | 426092 | g9cx | wi077 | 1969 | 1:20000 |
Marsh | Mf | 15 | 3403304 | g94x | wi079 | 2023 | 1:15840 |
Marsh | Mf | 261 | 425991 | g98n | wi089 | 1967 | 1:15840 |
Marsh | Mf | 1226 | 3268804 | g78c | wi101 | 2023 | 1:15840 |
Marsh | Mc | 676 | 426339 | g9mw | wi105 | 1970 | 1:20000 |
Marsh | Mf | 1787 | 423909 | g73h | wi117 | 1974 | 1:15840 |
Marsh | Mf | 1857 | 425638 | g8x8 | wi127 | 1967 | 1:15840 |
Marsh | Mf | 430 | 425748 | g90t | wi131 | 1967 | 1:15840 |
Marsh | Mf | 3496 | 3403455 | g94x | wi133 | 2023 | 1:15840 |
Marsh | Ma | 557 | 157374 | 58rl | wy613 | 1969 | 1:20000 |
Approximate geographic distribution of the MARSH soil series. To learn more about how this distribution was mapped, or to compare this soil series extent to others, use the Series Extent Explorer (SEE) application. Source: generalization of SSURGO geometry (updated 2024-10-30).