Wubs et al., (2016)
|
Soil/plant communities
|
Soil inoculation
|
1 – 2.5 l/m2 (over 5000 m2)
|
Nearby remnant
|
↑ richness acari/collembola, ↑ biomass microbes
|
↑ succession rate of desired plant species
|
Emam, (2016)
|
Soil/plant communities
|
Soil inoculation
|
0.16 l/m2
(over 10m2)
|
40-year-old stockpiled soil
|
Not measured
|
↑ soil N content
|
Lance et al., (2019) |
Soil/plant communities |
Soil inoculation |
50 g/plant |
Nearby remnant |
Not measured |
↑ soil C:N ratio and
phosphorous |
Lance et al., (2020) |
Soil/plant communities |
Soil inoculation |
50 g/plant |
Nearby remnant |
∆ microbe community composition |
Not
measured |
Rowe, Brown and Paschke, (2009)
|
Soil/plant communities
|
Soil inoculation
|
0.16 l/m2
(over 1.5 m2)
|
Nearby remnant
|
Not measured
|
∆ plant community composition
|
Soteras, Renison and Becerra, (2014) |
Soil/plant communities |
Soil
inoculation |
30 g/plant |
Nearby remnant |
No microbe community changes
detected |
No changes in primary productivity |
Grove et al., (2019) |
Soil/plant communities |
Soil inoculation |
3 l/plant |
Nearby remnant |
No microbe community changes detected |
No changes in above ground biomass |
van der Bij et al., (2018)
|
Soil/plant communities
|
Sod inoculation
|
3.33 l/m2
(over 15 m2)
|
Nearby remnant
|
↑ acari, nematode, collembola abundance/∆ microbe community
|
Not measured
|
Benetková et al., (2020)
|
Soil and litter communities
|
Soil and litter inoculation
|
33% surface coverage of
100 m2 plots
|
Nearby remnant
|
↑ number of nematode genera
|
Not measured
|
Moradi et al., (2018)
|
Soil communities
|
Soil inoculation
|
400 l/m2
(over 30 m2)
|
Nearby remnant
|
↑ number of earthworms and millipedes
|
↓ soil carbon and C:N ratio than overburden soil
|
Faist et al., (2020)
|
Biocrust communities
|
Soil inoculation
|
0.5 l/m2
(over 3 m2)
|
Nearby remnant
|
Not measured
|
Weak ↑ in soil stability, highly spatially dependant
|
Chiquoine, Abella and Bowker, (2016)
|
Biocrust communities
|
Soil inoculation
|
30% surface coverage of
1 m2 plots
|
Pre-disturbance community
|
↑ cyanobacteria density
|
Partial recovery of soil stability
|
Fisseha, Tamrat and Zerihun, (2019) |
Soil communities |
Rhizosphere
trap cultures |
Not measured |
Remnant trees |
Not measured |
No changes
in primary productivity |
Pywell et al., (2011)
|
Plant communities
|
Soil inoculation
|
24 kg/m2
(over 500 m2)
|
Nearby remnant
|
Not measured
|
No significant differences in plant reassembly
|
Middleton and Bever, (2012)
|
Plant communities
|
Soil inoculation
|
13.5
ml/seedling
|
Nearby remnant
|
Not measured
|
↑ growth of late-successional plants
|
Nishihiro, Nishihiro and Washitani, (2006)
|
Wetland plant communities
|
Lake sediment
|
100 l/m2 (over 5,300 –
27,800 m2)
|
Nearby fishing lake
|
Not measured
(methodological paper)
|
Not measured
|
Brown and Bedford, (1997) |
Wetland plant communities |
Wetland soil
inoculation |
150 l/m2 (over 0.75m2) |
Nearby remnant |
Not measured |
↑ plant growth |
Brown, Smith and Batzer, (1997) |
Wetland macroinvertebrates |
Wetland
soil inoculation |
100 l/m2 (over 550 – 950
m2) |
Nearby remnant |
↑ macroinvertebrate abundance |
Not measured |
Dumeier, Lorenz and Kiel, (2020)
|
Freshwater benthic invertebrates
|
Capturing whole communities
|
0.05 kg/m2 of habitat substrate (over 500
m2)
|
Nearby remnant
|
Not measured
(methodological paper)
|
Not measured
|
Haase and Pilotto, (2019)
|
Freshwater benthic invertebrates
|
Capturing whole communities
|
31,250 cm2 habitat per stream
|
Nearby remnant
|
Not measured
(methodological paper)
|
Not measured
|
Haskell et al., (2012)
|
Plant communities
|
Dead wood transplants
|
50% surface coverage of
9 m2 plots
|
Nearby Remnant
|
Not measured
|
↑ plant growth/regulated soil temperatures
|