Exotic Brome-Grasses in Arid and Semiarid Ecosystems of the Western US

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Stavi et al. 2008 ). Further research is needed to specifi cally address how various
control methods alter soil surface attributes and microtopography. Specifi cally,
there is need to further defi ne spatial and temporal patterns of germination,
establishment, and growth of Bromus , resident native species, and seeded species
under heterogeneous soil surface and vegetation conditions and over environ-
mental gradients (Chambers and MacMahon 1994 ).


  • Soil disturbances associated with mechanical control methods, revegetation, and
    seedbed preparation can have tremendous impacts on seed banks, resource avail-
    ability, and competition between B. tectorum and perennial grasses (Smith 1970 ;
    Beckstead and Augspurger 2004). Timing, frequency, and duration of distur-
    bances should be carefully studied for restoration sites to better defi ne restora-
    tion opportunities. In particular, future research should emphasize how the short
    period of time following soil disturbance can be utilized more opportunistically
    for the establishment of desired species (Young et al. 1969 ; Giunta et al. 1975 ).

  • The importance of soil resource availability in the invasion process is generally recog-
    nized (Davis et al. 2000), yet more mechanistic research is needed to develop a broader
    understanding of how invasive species management infl uences resource availability
    and recovery of native species (Jones et al. 2015 ). Although much research has empha-
    sized experimental manipulation of soil nitrogen availability to reduce invasive species
    abundance (Perry et al. 2010 ), future research will also need to clarify how combined
    treatment applications infl uence soil nutrient concentrations and resident plant species
    (Chambers et al. 2007 ; Hirsch- Schantz et al. 2014 ; Pyke et al. 2014 ).
    As research continually innovates by exploring mechanistic aspects of reducing
    Bromus populations and restoring ecological structure and function, adapting for
    the future will require bridging the gap between research and management. This
    may best be accomplished by in situ adaptive research and management experi-
    ments of how annual grasses, desirable resident plant species, environmental vari-
    ables, and edaphic factors respond to management treatments and activities over
    environmental gradients and at multiple locations (James et al. 2013b ).


References

Abatzoglou JT (2013) Development of gridded surface meteorological data for ecological applica-
tions and modelling. Int J Climatol 33:121–131
Abella SR (2014) Effectiveness of exotic plant treatments on National Park Service lands in the
United States. Invasive Plant Sci Manag 7:147–163
Aigner P, Woerly R (2011) Herbicides and mowing to control barb goatgrass ( Aegilops triuncialis )
and restore native plants in serpentine grasslands. Invasive Plant Sci Manag 4:448–457
Allen CR, Fontaine JJ, Pope KL et al (2011) Adaptive management for a turbulent future. J Environ
Manag 92:1339–1345
Andersen MR, Depuit EJ, Abernathy RH et al (1992) Value of mountain rye for suppression of
annual bromegrasses on semiarid mined lands. J Range Manag 45:345–351
Arkle RS, Pilliod DS, Hanser SE et al (2014) Quantifying restoration effectiveness using multi-
scale habitat models: implications for sage-grouse in the Great Basin. Ecosphere 5:31
Atkinson SY, Brown CS (2015) Attributes that confer invasiveness and impacts across the large
genus Bromus – lessons from the Bromus REEnet database. In: Germino MJ, Chambers JC,


T.A. Monaco et al.
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