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Previous attempts to reverse the degradation of a coastal wetland and restore nesting habitat for an endangered bird showed that adding nitrogen could temporarily increase the height of Spartina foliosa, but not produce self-sustaining tall canopies. We asked if increased effort (up to five years of N fertilization) would shift canopy attributes across the hypothesized threshold. Thirty plots were treated with 0–5 yr of urea addition, and all were followed for 5 yr. Canopies were robust while urea was being added, but Spartina reverted to short stature soon after fertilization ended, supporting R. J. Hobbs and D. A. Norton's concept of an irreversible transition. However, specific outcomes depended on the choice of response variable (six comparisons), the choice of reference data (initial conditions, same-year data, and pooled data), and the choice of statistical design (repeated measures vs. complete design), indicating the need to assess experiments thoroughly before making strong recommendations for ma...

Fish assemblages from small intertidal creeks (first-order) and from larger subtidal creeks (third- and fourth-order) were sampled seasonally for 1 year at Tijuana Estuary and Sweetwater Marsh in southern California, USA. First-order creeks were dominated by Gillichthys mirabilis, Fundulus parvipinnis, and Clevelandia ios at both sites. At Sweetwater Marsh, species composition and species richness differed between creek orders, as did size structure of F. parvipinnis, one of the most abundant marsh residents; a greater proportion of small juveniles was collected from first-order creeks. At Tijuana Estuary, the larger system, elevations of first-order creeks were higher and fish use of creeks was lower than at Sweetwater Marsh. Shallow habitats are used extensively by several marsh residents, and may provide nursery habitat for juvenile F. parvipinnis. Intertidal creeks should be considered in designs of marsh restoration projects where the creation of habitat for resident fishes is a priority.

Although tidal wetland vegetation patterns are typically related to elevation, we hypothesized that the vertical range of a species may shift where the topography is more heterogeneous. We examined plant species occurrences in relation to elevation, proximity to the bay, and proximity to tidal creeks at a near-pristine wetland in San Quintin Bay, Baja California, Mexico. At the whole-wetland scale, most species occurred primarily within a 30-cm elevation band (the marsh plain). However, Spartina foliosa occurred only at the bayward margin, even though “suitable” elevations were present further inland. A similar pattern was found in San Diego Bay. At the microtopographic scale, three species on the marsh plain were strongly influenced by elevation, whereas four species responded to both elevation and proximity to tidal creeks. The latter species tended to “avoid” the lower 10 cm of the marsh plain except near a tidal creek. Species richness was thus greater (by 0.6 species at the lowest 10-cm class) at the tidal creek margin. Better drainage near creeks is the hypothesized cause. Our results help explain why species that are transplanted to constructed wetlands do not always grow at the full range of elevations they occupy in natural wetlands. We recommend that species be introduced to their modal elevation (determined from nearby reference marshes) and that salt-marsh construction designs include topographic heterogeneity (complex tidal creek networks). The analysis of broad-scale and fine-scale patterns of occurrence also suggests new habitat nomenclature. Elevation-based terms (“low,”“middle,” and “high” marsh) should be replaced by a system that considers elevation, landscape position, and conspicuous species. We suggest three habitat designations: (a) the high marsh—a 30- to 70-cm elevation range with Salicornia subterminalis; (b) the marsh plain—a 30-cm elevation range with heterogeneous topography and up to nine common species; and (c) cordgrass habitat—the bayward portion of the marsh plain and lower elevations, all occupied by Spartina foliosa. Although these habitats do not have discrete boundaries, separate terms are needed for wetland restoration plans and these designations will improve recognition that vegetation patterns respond to horizontal, as well as vertical, position.

Differential tolerance of low salinity, competition for nitrogen (N), and facilitation by altering N supply all may act to determine the pattern of seasonal succession of Enteromorpha intestinalis (L.) Link and Ulva expansa (Setch) S. and G. in estuaries and lagoons of southern California. Low salinity negatively affected both of these algae. However, when N was in sufficient supply, salinities of 15 ppt favored E. intestinalis while oceanic salinity (35 ppt) favored U. expansa; neither alga had a clear advantage at 25 ppt. When starved of N, E. intestinalis and U. expansa competed directly for nutrients. When grown alone, they had similar N uptake and growth rates; when grown together, E. intestinalis was the superior competitor, negatively affecting growth of U. expansa. In addition, U. expansa facilitated the growth of E. intestinalis when N was in short supply; when grown together, there was a positive effect of U. expansa on E. intestinalis. The mechanism of this effect may have been the release or ‘leaking’ of DON when U. expansa no longer had sufficient tissue N to grow. Thus, E. intestinalis would be favored immediately after a rain, but would be replaced by U. expansa when N is available and tidal action reestablishes oceanic salinity. However, at the end of the rainy season when N becomes scarce, E. intestinalis would outcompete U. expansa. We hypothesize that U. expansa may facilitate the dominance of E. intestinalis by leaking N that can be assimilated by E. intestinalis.