Growth and biomass of Populus irrigated with landfill leachate
Introduction
Poplars (Populus spp.) have been extensively studied in short rotation woody biomass production systems for multiple uses such as fiber, fuel and environmental benefits (Dickmann, 2001, Isebrands and Karnosky, 2001, Coleman and Stanturf, 2006). Exemplary traits that have contributed to the success of such uses include: ease of rooting, quick establishment, fast growth, and elevated rates of photosynthesis and water usage (Ceulemans et al., 1992, Pontailler et al., 1999, Zalesny et al., 2006). Broad genetic diversity among poplar genomic groups and selection of specific genotypes within such groups increase the potential enhancement of growth and establishment for various uses across heterogeneous sites (Heilman and Stettler, 1985, Heilman et al., 1994). The combination of appropriate cultural practices and well-suited genotypes helps to maximize poplar performance for improved biomass yields (Buhler et al., 1998, Stanturf et al., 2001).
Environmental benefits have been realized from poplar culture when used as components in riparian buffers along streams (Schultz et al., 2004) and as vegetative filters for phytoremediation applications (Licht and Isebrands, 2005). Several phytoremediation projects utilized wastewater in the form of landfill leachate as an irrigation and fertilization source for poplar trees (Shrive et al., 1994, Erdman and Christenson, 2000, Zalesny and Bauer, in press). Proper clonal selection practices must be utilized given the genetic variability within the genus Populus (Rajora and Zsuffa, 1990, Eckenwalder, 1996) and the variable concentrations of inorganic and organic components in the leachate (Gettinby et al., 1996). Leachate production occurs through natural degradation processes aided by the movement of water through the landfill profile (Christensen and Kjeldsen, 1989). Due to the variation associated with residential, commercial, and industrial waste material, the leachate is highly variable and compositional changes occur seasonally and annually (Shrive et al., 1994, Kjeldsen et al., 2002).
A great deal of information has been reported using poplars for short rotation forestry (Heilman, 1999, Riemenschneider et al., 2001), but there are relatively fewer reports about using poplars for leachate phytoremediation systems. Thus, researchers and resource managers need information that is currently lacking about tree establishment with leachate irrigation. Such information will help increase the success of using poplars for remedial benefits, especially with ecologically damaging contaminants such as those found in most leachate. Overall, the use of short rotation woody crop management for remediation supports improved environmental quality and secondary benefits such as carbon sequestration, a harvestable product, aesthetic improvements, and erosion control (Isebrands and Karnosky, 2001, Duggan, 2005).
This project expands on our previous work investigating phyto-recurrent selection, which was defined as a method using crop and tree improvement strategies to identify and select superior performing clones for remediation projects (Zalesny et al., in press). Clonal selections were made after three successive cycles of evaluation (i.e. three separate greenhouse studies) testing 23 traits relating to height growth, leaf development, and root initiation at 14 (cycle 1; 25 clones), 45 (cycle 2; 12 clones), and 30 (cycle 3; 12 clones) days after planting. The best eight clones were selected for testing in the current in situ study (cycle 4) out of the original 25 genotypes belonging to six distinct genomic groups: (1) (Populus trichocarpa Torr. & Gray × Populus deltoides Bartr. ex Marsh) × P. deltoides ‘BC1’; (2) P. deltoides × P. deltoides ‘DD’; (3) P. deltoides ‘D’; (4) P. deltoides × Populus maximowiczii A. Henry ‘DM’; (5) P. deltoides × Populus nigra L. ‘DN’; (6) P. nigra × P. maximowiczii ‘NM’.
The overall objective of all phyto-recurrent selection cycles was to test the effectiveness of poplars for uptake of inorganic and organic contaminants found in landfill leachate. More specifically, the objective of the current study was to test for differences in growth and biomass distribution of eight Populus clones when irrigated with municipal solid waste landfill leachate or fertilized well water (control) (N, P, K) for two growing seasons. In addition to actual phytoremediation success, tree growth and biomass accumulation are important for evaluating the overall effectiveness of the biological attenuation system. These data will serve as a basis for researchers and resource managers making decisions about future leachate remediation projects.
Section snippets
Site and leachate description
The study was conducted at the Oneida County Landfill (municipal solid waste) located 6 km west of Rhinelander, Wisconsin, USA (45.6°N, 89.4°W). Temperature, precipitation, and growing degree days across the experimental period are listed in Table 1. The landfill soils are classified as mixed, frigid, coarse loamy Alfic Haplorthods (Padus Loam, PaB), with 0–6% slopes, and are considered well to moderately well drained with loamy deposits underlain by stratified sand and gravel glacial outwash.
Tree growth
The survival rate of the trees at the time of harvest was the same for each treatment at 78% (50/64). Height did not differ between leachate and well water (control) treatments, but there were differences among clones. The treatment × clone interaction was significant (Table 4). Populus nigra × P. maximowiczii “NM’ clones NM2 and NM6 had the greatest height across both irrigation treatments (Fig. 1). Despite substantial clonal variation among genotypes belonging to the P. deltoides × P. maximowiczii
Discussion
Although leachate irrigation did not enhance tree growth and biomass for most genotypes in the current study, significant productivity reductions associated with the leachate also were not observed. Therefore, there is a great potential for remediation of landfill leachate using Populus. Selection within the clonal variation that resulted from variable responses to leachate or well water (control) treatments will serve as a basis for researchers and resource managers making decisions about
Conclusion
Overall, given that every leachate source should be regarded as unique, there is an essential need for initial genotype screening followed by the establishment and evaluation of test plots to ascertain clonal performance prior to large-scale deployment. The lack of overall differences in response to treatments in the current study was a result of extensive genotypic screening during phyto-recurrent selection cycles 1–3 that reduced the variability among the clones deployed, relative to the
Acknowledgements
This research was funded by Iowa State University – Department of Natural Resource Ecology and Management, USDA Forest Service Northern Research Station – Research Work Unit RWU-NRS-4158, and a Grant-in-Aid of Research from Sigma Xi, the Scientific Research Society. We are grateful to Neil Nelson and Adam Wiese for continual support throughout all stages of the project. In addition, we thank Bart Sexton (Oneida County Solid Waste Department) for detailed collaboration and for assistance at the
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2021, Forest Ecology and ManagementCitation Excerpt :Using treated wastewater for irrigation may also help to pay for the costs of wastewater purification (Stewart and Salmon, 1986; Cozzi et al., 2015). Now, the success of irrigating with treated wastewater requires selecting suitable poplar species and clones, reducing the distance between stands and wastewater treatment plants, and determining the optimal stand area and irrigation method and management (Stewart and Salmon, 1986; Zalesny, 2007; Cozzi et al., 2015). For instance, in Victoria, Australia, when using wastewater to irrigate poplars through a fixed-sprinkler irrigation system, it was not profitable at financial interest rates between 3% and 7%.
Willow and poplar for the phyto-treatment of landfill leachate in Mediterranean climate
2021, Journal of Environmental ManagementCitation Excerpt :In other cases the leachate used in the field was pre-treated in a nitri/denitrification facility at the landfill site, thereby starting with a very different composition from leachate emanating directly from an actual landfill (Aronsson et al., 2010). Moreover, most available information on the phyto-treatment of this pollutant comes from Northern Temperate Regions (Godley et al., 2004; Smesrud et al., 2012; Zalesny, 2007) where the actual composition of LL is very different compared to that originated under Mediterranean climate conditions, where the combination between low precipitation and high temperature (i.e. high evapotranspiration) often results in more concentrated (i.e. higher electro-conductivity, pH, Cl, and NH4–N) LL (Vadillo et al., 1999). Therefore, information on the safe use of LL is still incomplete especially for Mediterranean countries, where the wide range of leachate types makes it difficult to draw a reliable picture of the potential of using green approaches for such applications.
Poplar rotation coppice at a trace element-contaminated phytomanagement site: A 10-year study revealing biomass production, element export and impact on extractable elements
2020, Science of the Total EnvironmentCitation Excerpt :Different genotypes of the same poplar species may exhibit variable tolerance to trace elements (TE) because of intraspecific genetic dissimilarity (Castiglione et al., 2009). For instance, a large variation in poplar genotypic responses to leachate irrigation has been found (Zalesny et al., 2007), and high variability occurs in foliar trace element concentrations within a selection of 14 poplar genotypes (Pottier et al., 2015). A number of works have been dedicated to the study of poplar responses to soil contamination in controlled pot or hydroponic (Cicatelli et al., 2010; De Oliveira and Tibbett, 2018; Langer et al., 2012; Lingua et al., 2008; Migeon et al., 2012), tank (Zalesny and Bauer, 2007), or lysimeter (Dimitriou and Aronsson, 2011, 2010) set ups.