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PLACE · LANDSCAPE HISTORY

The arc of DFW landscape practice.

The region the drawings sit inside was not a blank page before the first designed garden reached it. Pre-settlement ecology composed a prairie-and-oak mosaic across the seam of two ecoregions; mid-century residential practice wrote a second, partial, and often-argumentative landscape over the first; the native-revival turn of the 1990s and 2000s began to reconcile the two; and Winter Storm Uri in February 2021 enforced a recalibration that any serious regional practice has been working through ever since. This page traces that arc — not as public-realm tourism and not as nostalgia, but as the editorial frame that underwrites the rest of the Place section.

Pre-settlement ecology — prairie-and-oak mosaic.

Before the plow reached it in the 1840s, the land between the Red River and the Brazos was not a forest, not a desert, and not the lawn-and-ornamental landscape that later arrivals would recognize. It was a grassland-and-woodland mosaic in which the Blackland Prairie held tallgrass communities across heavy calcareous clay and the Eastern Cross Timbers carried a post oak savannah across sandy loam a few miles west. The tallgrass matrix — big bluestem (Andropogon gerardii), Indiangrass (Sorghastrum nutans), switchgrass (Panicum virgatum), little bluestem (Schizachyrium scoparium), sideoats grama (Bouteloua curtipendula) — assembled a grassland at shoulder height in favorable years, interleaved with prairie forbs that carried color through the calendar. Canopy concentrated along stream bottoms and in scattered upland motts of escarpment live oak (Quercus fusiformis), eastern red cedar (Juniperus virginiana), cedar elm (Ulmus crassifolia), and sugar hackberry (Celtis laevigata). West of the Trinity, post oak (Q. stellata) held the canopy over a grassland understory.

What maintained the mosaic was not a static climax ecology but a regular disturbance regime. Low-intensity grassland fires — some set by lightning, some set by Indigenous land management — recurred on a roughly three-to-five-year interval across the tallgrass matrix. Fire prevented woody encroachment where soil and hydrology might otherwise have allowed canopy to close; it recycled nutrients back into the surface soils that clay vertisols hold tightly; and it maintained the species composition that had co-evolved with it over millennia. The bison herds that ranged the tallgrass contributed a second disturbance layer — selective grazing, trampling, and nutrient cycling through dung. Remove either disturbance and the matrix shifts. Remove both and it collapses.

Conversion — the fastest-transformed prairie in North America.

Anglo settlement arrived in the 1840s and read the Blackland Prairie as one of the most fertile cotton soils on the continent. Within a single generation, the calcareous clays that had carried the tallgrass matrix for thousands of years were under the plow at a conversion rate that is, as a matter of historical record, among the fastest wholesale transformations of a native ecosystem in North American history. By the end of the nineteenth century, row-crop cotton had substantially displaced the prairie matrix; fire suppression followed as settler agriculture cleared the conditions that fire had maintained. The bison were gone by the 1880s. The remnants that survived — rail corridors that never got broken to plow, cemetery parcels preserved on adjacent land, the occasional easement margin — represent a fraction of one percent of the pre-settlement Blackland.

The Eastern Cross Timbers fared slightly better because its sandy loam was less attractive to row-crop cotton, but the post oak savannah structure was substantially altered as fire suppression allowed woody encroachment and as subdivision-era grading reshaped the soil column across much of what is now residential DFW. By the time Dallas and Fort Worth had grown from settlement towns into mid-twentieth-century cities, neither ecoregion survived in anything like its pre-settlement form. What remained was the substrate — the calcareous clay, the Woodbine sandy loam, the USDA-zone envelope, the rainfall-and-evaporation regime — and a remnant set of native canopy species that had proven willing to coexist with lawn, irrigation, and compacted clay fill.

Mid-century practice — what Dallas and Fort Worth planted, and what persisted.

The post-war expansion that built Preston Hollow, the Park Cities, Lake Highlands, Lakewood, and the inner-ring Fort Worth neighborhoods brought with it a residential landscape practice that was, on average, substantially indifferent to the underlying ecoregion. The typical 1950s-through-1980s DFW residential landscape consisted of a front lawn in St. Augustine or hybrid bermuda, foundation shrubs from the Gulf-coast ornamental catalog, one or two shade trees of uncertain provenance, and a thin ornamental border along property lines. Pecan (Carya illinoinensis) was overplanted across the metro relative to what its soil tolerances could actually sustain; red maple (Acer rubrum) and pin oak (Quercus palustris) were planted with regularity on Blackland-clay lots where their acid preferences guaranteed iron chlorosis within a decade; sweetgum (Liquidambar styraciflua) followed the same pattern. Entire subdivisions installed landscapes built against the ground rather than with it.

What persisted tended to be the subset of species that cooperated with the substrate in spite of the design intent. Live oak — both Q. fusiformis and Q. virginiana, and the hybrid intermediates that extend through the metro — carried mid-century residential plantings across the DFW service area and still anchors most of the mature canopy on pre-1980s lots. Cedar elm and eastern red cedar persisted wherever they were allowed to. Mexican plum (Prunus mexicana) and Texas redbud (Cercis canadensis var. texensis) held understory. The acid-loving imports quietly failed, often on rolling fifteen-to-twenty-year replacement cycles that contemporary homeowners read as normal rather than diagnostic. What did not persist, almost universally, were the native grasses. Tallgrass forbs were absent from the residential palette entirely through most of the century; the notion that a prairie species might belong in a residential garden would not meaningfully return until the 1990s.

The native-revival turn, from the 1990s forward.

The reorientation of DFW residential landscape practice toward regional natives was neither sudden nor uniform. Its institutional anchors came from outside the metro in the 1980s — the founding of the National Wildflower Research Center in Austin in 1982 by Lady Bird Johnson and Helen Hayes (renamed the Lady Bird Johnson Wildflower Center in 1998 and absorbed into the University of Texas at Austin in 2006), and the growing influence of the Native Plant Society of Texas founded in 1980 — both of which put regional native species on a visible institutional footing that had not existed before. In DFW specifically, a combination of drought-year pressure (the 1990s produced several severe single-year deficits), rising municipal water cost, and generational turnover in residential practice began shifting the working palette toward species that cooperated with calcareous clay and the drought-cycle climate rather than arguing with both.

Through the 2000s and 2010s, that turn compounded. Native grasses — sideoats grama, little bluestem, Mexican feathergrass (Nassella tenuissima), Gulf muhly (Muhlenbergia capillaris) — entered the ornamental palette in a way they had not been available in prior decades, and serious regional practitioners began specifying them as structural elements rather than accent plantings. Native perennials followed: salvias, blackfoot daisy, Texas sage (Leucophyllum frutescens), and the Asteraceae forbs that the pre-settlement prairie had carried. The canopy palette contracted back toward the species that had actually persisted through the mid-century — the live oaks, cedar elm, eastern red cedar, post oak on Cross Timbers sites — and expanded to include Shumard red oak (Q. shumardii), chinquapin oak (Q. muehlenbergii), and bur oak (Q. macrocarpa) where conditions allowed. By the late 2010s, the phrase “native or adapted” had become a working shorthand on residential specifications across most serious DFW practices, and the mid-century catalog-ornamental palette had been substantially narrowed.

The current moment — post-Uri recalibration.

In February 2021, Winter Storm Uri held DFW under freezing air for five consecutive days and produced soil temperatures lower than anything in the region's recorded horticultural memory. The event killed species that had been specified across the metro for decades — queen palms and the tender Pittosporum cultivars that had been routine, certain Podocarpus specimens, an entire tier of borderline-hardy imports that had been sold as zone 8 but were effectively zone 9a plants on a mild DFW winter average. It split irrigation manifolds that had passed every previous winter. It cracked mortar joints in terraces that had never flinched. The industry's first response was to write the event off as a generational anomaly. The serious-practice response was to treat it as a data point that should change the work.

The recalibration that followed has two directions. The negative direction is a contraction — species removed from working palettes, borderline zone 9a specimens treated as the zone 9a plants they actually are, irrigation and hardscape details revised to anticipate freeze events rather than survive them on luck. The positive direction is a re-weighting toward species with a documented record on the other side of the event: the live oaks that held through Uri with measurable damage but demonstrable recovery, eastern red cedar as the reliable DFW-native evergreen structure, the native grasses and forbs that went dormant and returned in spring. Post-Uri design is not a break from the native-revival turn; it is an intensification of it. The case for regional specificity — for reading the ground that the drawing sits on and letting the drawing grow from that reading — is stronger now than it was before February 2021.

What is also becoming visible in the current moment, and deserves saying plainly: regional specificity is not a regional preference. It is the ground truth on which resilient design in DFW actually depends. The Blackland Prairie is not a theme to be gestured at; it is the substrate under most of east Dallas and all of Collin County. The Cross Timbers is not a reference to include; it is the soil series under Preston Hollow and the Denton-county edge of Prosper. USDA zone 8a and 8b are not marketing decoration; they are the temperature envelope a planting has to survive. A landscape practice serious about the region reads those conditions first and lets the designed response grow from them. See the design philosophy for how that reading shapes the practice; see the resilience section for the specific post-Uri discipline; see the working native palette for the practical reference that carries this page into specification.

A note on public-realm reference.

Klyde Warren Park, the 5.2-acre deck park over Woodall Rodgers Freeway designed by OJB Landscape Architecture and opened in 2012, is the most visible public-realm landscape in the Alterra service area and the clearest demonstration in Dallas that a designed landscape at civic scale can carry regional specificity without sacrificing ambition. It is a legitimate reference point for the register a DFW resident might hope a residential garden could aspire to — not at 5.2 acres of scale, but in the discipline around spatial composition, planting-community coherence, seasonal durability, and material quality. The Lady Bird Johnson Wildflower Center in Austin holds the corresponding reference for horticultural authority at the regional scale. Neither of these is the client's garden. Both of them shape the expectation a client walks into a first conversation carrying.