Identification of 16SrXXX-A Phytoplasma Associated with Salt cedar (Tamarix chinensis Lour.) witches'-broom (SCWB) in Southern Xinjiang of China

Salt cedar is an ornamental shrub/moderate tree species native to Asia and East Europe, and grows in salt-alkali soil, desert and other dry areas, which plays an important role in wind prevention and sand fixation as well as maintaining ecological balance. Salt cedar witches’-broom (SCWB), which was extremely pernicious to Salt cedar. It was first observed and reported in Xi’an, China in 2005 (Zhao et al.2005). Witches' broom symptoms were observed on 20 out of 150 (13.3%) salt plants surveyed from the Alar region and 10 out of 86 (11.6%) plants from the Akesu region in southern of Xinjiang in May 2020. The damaged plants compared with asymptomatic plants (Fig.1A), the major symptoms included branches clustered, intersegment shorten and coarsen, giving rise to the formation of clusters (Fig.1B). Total plant DNA was extracted from phloem tissues with asymptomatic symptoms and phloem tissues with witches'-broom symptoms by a CTAB-based DNA extraction method (Green et al.1999). The 16S rRNA gene and the phytoplasma universal primers P1/P7 and rpF1/rpR1 of the rp (ribosomal protein) gene were used for Polymerase chain reaction (PCR) amplification by using the extracted plant total DNA as the template. The PCR product was used as the template and the R16F2n/R16R2 prmer was used for nested PCR amplification of the 16S rRNA gene after the amplification was completed. The results show that no product was obtained in asymptomatic plants. When DNA samples from witches’-broom symptomatic plants were used as templates, fragments with lengths 1219 bp and 1174 bp, corresponding to 16S rRNA gene and rp gene, were obtained. 16S rRNA gene was sequenced and deposited in GenBank under accession number MW447513. BLAST analysis revealed that the partial 16S rRNA sequence of the phytoplasma associated with P. aphylla witches’ broom showed highest sequence identity (99.67%) to salt cedar witches’ broom phytoplasma, ‘Candidatus Phytoplasma tamaricis’ (Accession Number: FJ432664). Phylogenetic and molecular evolutionary analyses were conducted using MEGA-X (Kumar et al., 2018). Results showed taht the SCWB and 16S rXXX group’s‘Candidatus Phytoplasma tamaricis’, (GenBank accession: FJ432664) have the highest affinity (Fig.2A). A virtual restriction fragment length polymorphism(RFLP) was done to determinethe subgroup ( Zhao et al. 2009). The 16S rDNA sequence from the Tamarix chinensis plant showed 99.3% similarity with that of the “Candidatus Phytoplasma tamaricis” reference strain (GenBank accession: FJ432664), suggesting that the phytoplasma in this study belongs to “Candidatus Phytoplasma tamaricis”-related strain. Therefore, it can be stated that SCWB belongs to the 16S rXXX group. The partial rp sequences only shared 84.74% sequence similarity with that of ‘Candidatus Phytoplasma prunorum’ (MG383523) of Apple proliferation group, a known subgroup 16S rX. Blast analysis based on the partial rp sequences showed that it shares less than 90% similarity with that of any known phytoplasma (Fig 2B), we suspect that this is due to a lack of sequenced rp gene sequences for the 16S rXXX group. To our knowledge, this is the first report of Salt Cedar Witches' Broom phytoplasma in Xinjiang province, China. As a consequence, we guess the SCWB phytoplasma rp gene belongs to 16S rXXX-rp group, which is also the first report about the 16SrXXX-rp group. Because SCWB1 is the only strain in the 16S rXXX group, and it is the representative strain of the 16S rXXX-A subgroup (Zhao et al. 2009). So, the SCWB disease we found in southern Xinjiang belongs to the 16S rXXX-A subgroup.

AEDES AEGYPTI SURVIVORSHIP ON SALT TOLERANT CALIFORNIA LANDSCAPE PLANTS

Aedes aegypti has expanded its range in the United States to include various arid and desert geographies, with notable introduction into various parts of California. Because resources are limited in arid environments, it is currently an important topic to understand how Ae. aegypti interacts with its surrounding environment for survival and proliferation. Three common plant species in peridomestic landscape, i.e., salt cedar (Tamarix aphylla), arrow weed (Pluchea sericea) and four wing saltbush (Atriplex canescens), were collected for survival bioassays to understand how Ae. aegypti is persisting in arid, chaparral landscapes in California, USA. These three plant-species along with a 10% sucrose solution (positive control) and reverse osmosis water solution (negative control-) were added to cages of Ae. aegypti to assess their survival at 24h, 48h, and 96h. It was found, in comparison with the negative control and four wing salt bush, that arrow weed and to a lesser extent salt cedar, promoted survival of Ae. aegypti in the first 24h. After the first day, only arrow weed significantly supported mosquito survival out to 96h as compared to the controls. Arrow weed and salt cedar are both riparian plants producing some nectaries which could be energy resources provided through stem sap or nectar to Ae. aegypti amidst peridomestic chaparral in California.

Remotely Sensed Changes in Vegetation Cover Distribution and Groundwater along the Lower Gila River

Introduced as a soil erosion deterrent, salt cedar has become a menace along riverbeds in the desert southwest. Salt cedar replaces native species, permanently altering the structure, composition, function, and natural processes of the landscape. Remote sensing technologies have the potential to monitor the level of invasion and its impacts on ecosystem services. In this research, we developed a species map by segmenting and classifying various species along a stretch of the Lower Gila River. We calculated metrics from high-resolution multispectral imagery and light detection and ranging (LiDAR) data to identify salt cedar, mesquite, and creosote. Analysts derived training and validation information from drone-acquired orthophotos to achieve an overall accuracy of 94%. It is clear from the results that salt cedar completely dominates the study area with small numbers of mesquite and creosote present. We also show that vegetation has declined in the study area over the last 25 years. We discuss how water usage may be influencing the plant health and biodiversity in the region. An examination of ground well, stream gauge, and Gravity Recovery and Climate Experiment (GRACE) groundwater storage data indicates a decline in water levels near the study area over the last 25 years.

Copper Complexation by Dissolved Organic Matter in arid Soils: A Voltametric Study

A voltammetric method was used to estimate the complexing capacity of water extracts from both desert soils sampled at the root zone of creosote and salt cedar plants, and in soils from interspace or background regions where no vegetative influence was apparent. The copper complexing capacity of water extracts of these desert soils was influenced by contact time and pH. In soils from the root zones of creosote and salt cedar plant, copper complexation capacities at pH 8 were from 5 µM to 60 µM after five min contact periods, while 18 h contact periods yielded copper complexation capacities of 40 µM–80 µM. Soils with no vegetative influence had copper complexing capacities of less the 2 µM. The copper complexing capacities of these soils are well correlated with the concentration of organic carbon in the water extract (r2 = 0.86). The abundance of soluble organic matter in the root zone of desert shrubs has the potential to control the solution speciation of Cu2+. The formation of soluble complexes should also have an important influence on the plant uptake and transport of copper, as well as other heavy metals in the root zones of desert shrubs and beyond.