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Journal articles on the topic 'Non-native species'

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Author: Grafiati

Published: 4 June 2021

Last updated: 20 February 2023

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1

Deil, Ulrich, Miguel Alvarez, and Inge Paulini. "Native and non-native species in annual grassland vegetation in Mediterranean Chile." Phytocoenologia 37, no. 3-4 (December 1, 2007): 769–84. http://dx.doi.org/10.1127/0340-269x/2007/0037-0769.

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2

Pearce, Fred. "Non-native species boost biodiversity." New Scientist 235, no. 3141 (September 2017): 10. http://dx.doi.org/10.1016/s0262-4079(17)31701-3.

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3

Sladonja, Barbara, Danijela Poljuha, Marin Krapac, Mirela Uzelac, and Maja Mikulic-Petkovsek. "Dittrichia viscosa: Native-Non Native Invader." Diversity 13, no. 8 (August 15, 2021): 380. http://dx.doi.org/10.3390/d13080380.

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Dittrichia viscosa (L.) Greuter is a shrub native to the Mediterranean, however, declared as a very invasive species in Australia and North America. Environmental (climatic) and socio-economic (land abandonment) changes can trigger different adaptive mechanisms and cause changes in species behavior, influencing invasion dynamics. Motivated by the recently noticed change of D. viscosa behavior in its native Mediterranean habitat, we discuss the invasion properties, its behavior in the native habitat and new areas, and its management options. We review the species’ adverse effects and its positive ecosystem services in the Millennium Ecosystem Assessment framework. In this review, we provide information on the phytochemical properties of D. viscosa and highlight its potential use in ecological agriculture, phytopharmacy, and medicine. The presented data is useful for developing effective management of this contentious species, with emphasis on mitigating environmental and economic damages, especially in agriculture. The final aim is to achieve a balanced ecosystem, providing a high level of possible services (provisioning, regulating, cultural and supporting).

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4

Willmore, Christine. "Native good, non-native bad? Defining troublesome species." Environmental Law Review 17, no. 2 (June 2015): 117–27. http://dx.doi.org/10.1177/1461452915575652.

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5

CHIBA, SATOSHI. "Invasive Non-Native Species’ Provision of Refugia for Endangered Native Species." Conservation Biology 24, no. 4 (February 22, 2010): 1141–47. http://dx.doi.org/10.1111/j.1523-1739.2010.01457.x.

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6

Potter, Daniel A., and Bernadette M. Mach. "Non-Native Non-Apis Bees Are More Abundant on Non-Native Versus Native Flowering Woody Landscape Plants." Insects 13, no. 3 (February 28, 2022): 238. http://dx.doi.org/10.3390/insects13030238.

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Urban ecosystems can support diverse communities of wild native bees. Because bloom times are conserved by geographic origin, incorporating some non-invasive non-native plants in urban landscapes can extend the flowering season and help support bees and other pollinators during periods when floral resources from native plants are limiting. A caveat, though, is the possibility that non-native plants might disproportionately host non-native, potentially invasive bee species. We tested that hypothesis by identifying all non-native bees among 11,275 total bees previously collected from 45 species of flowering woody landscape plants across 213 urban sites. Honey bees, Apis mellifera L., accounted for 22% of the total bees and 88.6% of the non-native bees in the collections. Six other non-native bee species, accounting for 2.86% of the total, were found on 16 non-native and 11 native woody plant species. Non-Apis non-native bees in total, and Osmia taurus Smith and Megachile sculpturalis (Smith), the two most abundant species, were significantly more abundant on non-native versus native plants. Planting of favored non-native hosts could potentially facilitate establishment and spread of non-Apis non-native bees in urban areas. Our host records may be useful for tracking those bees’ distribution in their introduced geographical ranges.

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7

Roy, Helen E., Chris D. Preston, Colin A. Harrower, Stephanie L. Rorke, David Noble, Jack Sewell, Kevin Walker, et al. "GB Non-native Species Information Portal: documenting the arrival of non-native species in Britain." Biological Invasions 16, no. 12 (April 5, 2014): 2495–505. http://dx.doi.org/10.1007/s10530-014-0687-0.

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8

Haffele, Ryan D., Michael W. Eichholz, and Cami S. Dixon. "Duck Productivity in Restored Species-Rich Native and Species-Poor Non-Native Plantings." PLoS ONE 8, no. 7 (July 1, 2013): e68603. http://dx.doi.org/10.1371/journal.pone.0068603.

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9

Hossain, Ishrak, and ABM Mohsin. "Native and non-native ornamental aquarium fishes of Bangladesh." IJOTA (Indonesian Journal of Tropical Aquatic) 4, no. 1 (March 1, 2021): 1–13. http://dx.doi.org/10.22219/ijota.v4i1.14023.

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The study was conducted in Dhaka, Bangladesh. It was carried out for twelve (12) months from March 2018 to February 2019 to prepare a complete update checklist of native and non-native aquarium fishes of Bangladesh. During the current study, 270 varieties (230 freshwater, 36 marine, and 4 brackish water) belong to 149 species (109 freshwater 73 %, 36 marines 24 %, and 4 brackish water 3 %) of 38 families under 10 orders and 6 crossbreeds’ varieties were recorded. Considering the number of species maximum 83 (55.70 %) was found under the order Perciformes followed by Cypriniformes 24 (16.10 %), Characiformes 18 (12.08 %), Siluriformes 11 (7.38 %), Osteoglossiformes 05 (3.35 %), Atheriniformes 03 (2.01 %), Lepisosteiformes 02 (1.34 %), Polypteriformes 01 (0.6 %), Myliobatiformes 01 (0.67 %) and Cyprinodontiformes 01 (0.67 %). The top five popular species were guppy (13.16 %) followed by goldfish (12.39 %), molly (8.54 %), angelfish (6.23 %), platy (5.93 %). The number of fish species' increasing tendency was 5.96 times in the last 15 years, and 3.31 times in the last ten years. Local farms and aquarists breeders bred 76 varieties under 23 species due to its high demand and profitability. Pricing varied on varieties, species, size, and breeding status (local or abroad), availability, and ranged from BDT 40.00-80,000.00 per pair. According to the findings, aquarium fisheries are highly profitable and will be a potential sector in Bangladesh.

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10

Howell, Clayson, and Kate McAlpine. "Native plant species richness in non-native Pinus contorta forest." New Zealand Journal of Ecology 40, no. 1 (2016): 131–36. http://dx.doi.org/10.20417/nzjecol.40.15.

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11

SPEZIALE, KARINA L., SERGIO A. LAMBERTUCCI, CINTIA P. SOUTO, and FERNANDO HIRALDO. "Recovering Native Culture in a World of Non-native Species." Conservation Biology 28, no. 4 (February 13, 2014): 1129–31. http://dx.doi.org/10.1111/cobi.12251.

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12

Lembrechts, Jonas J., Jake M. Alexander, Lohengrin A. Cavieres, Sylvia Haider, Jonathan Lenoir, Christoph Kueffer, Keith McDougall, et al. "Mountain roads shift native and non-native plant species' ranges." Ecography 40, no. 3 (March 23, 2016): 353–64. http://dx.doi.org/10.1111/ecog.02200.

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13

Bergstrom, Dana M. "Maintaining Antarctica’s isolation from non-native species." Trends in Ecology & Evolution 37, no. 1 (January 2022): 5–9. http://dx.doi.org/10.1016/j.tree.2021.10.002.

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14

Schlaepfer, Martin A. "Do non-native species contribute to biodiversity?" PLOS Biology 16, no. 4 (April 17, 2018): e2005568. http://dx.doi.org/10.1371/journal.pbio.2005568.

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15

JESCHKE, JONATHAN M., SVEN BACHER, TIM M. BLACKBURN, JAIMIE T. A. DICK, FRANZ ESSL, THOMAS EVANS, MIRIJAM GAERTNER, et al. "Defining the Impact of Non‐Native Species." Conservation Biology 28, no. 5 (April 29, 2014): 1188–94. http://dx.doi.org/10.1111/cobi.12299.

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16

Xiong, Wen, Xiaoyun Sui, Shih-Hisung Liang, and Yifeng Chen. "Non-native freshwater fish species in China." Reviews in Fish Biology and Fisheries 25, no. 4 (September 22, 2015): 651–87. http://dx.doi.org/10.1007/s11160-015-9396-8.

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17

Nicholson, Daniel J., Christopher Hassall, and Julius A. Frazier. "Comparison of a native and a non-native insular reptile species." Journal of Tropical Ecology 31, no. 6 (September 17, 2015): 563–66. http://dx.doi.org/10.1017/s0266467415000462.

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Abstract:This study compared the life histories of Hemidactylus frenatus, a significant invasive gecko, and Phyllodactylus palmeus, a Honduran endemic, over 10 wk, June–August 2013 at 12 study sites on the Honduran island of Cayo Menor of the Cayo Cochinos archipelago where H. frenatus arrived in 2008. Three different life-history traits related to invasion success were measured: body size, fecundity and population size. During the study 140 natives and 37 non-natives were captured, weighed, measured and marked uniquely. The number of gravid females and number of eggs were also recorded. Phyllodactylus palmeus was the significantly larger of the two species (60% larger mass, 25% longer SVL) and had higher population abundance at all 12 study sites with some sites yielding no H. frenatus individuals. However, H. frenatus had a larger proportion of gravid females. Observations that the native species is more common despite being sympatric with a known aggressive invader suggest two possibilities: the island is at the start of an invasion, or that the two species co-exist in a more stable fashion.

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18

Grutters, Bart M. C., Elisabeth M. Gross, Ellen van Donk, and Elisabeth S. Bakker. "Periphyton density is similar on native and non-native plant species." Freshwater Biology 62, no. 5 (March 7, 2017): 906–15. http://dx.doi.org/10.1111/fwb.12911.

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19

ASLAN, CLARE E., ERIKA S. ZAVALETA, BERNIE TERSHY, DON CROLL, and ROBERT H. ROBICHAUX. "Imperfect Replacement of Native Species by Non-Native Species as Pollinators of Endemic Hawaiian Plants." Conservation Biology 28, no. 2 (December 20, 2013): 478–88. http://dx.doi.org/10.1111/cobi.12193.

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20

Gbedomon, Rodrigue C., Valère K. Salako, and Martin A. Schlaepfer. "Diverse views among scientists on non-native species." NeoBiota 54 (January 22, 2020): 49–69. http://dx.doi.org/10.3897/neobiota.54.38741.

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Conservation scientists have traditionally viewed non-native species (NNS) as potential threats to native biodiversity. Here, we question whether alternative views of NNS exist in the scientific community that stand in contrast to the dominant narrative that emerges from the literature. We asked researchers from the biological, social, and environmental sciences to participate in an anonymous poll regarding the perceived values and threats of NNS. Some 314 individuals responded, approximately half of whom were biologists and half were social or environmental scientists. We grouped responses into three statistical clusters defined by shared responses. We then analyzed the correlation of responses to individual questions and membership of clusters with predictor variables age, gender, and field of work. Overall, a majority of respondents in our sample supported statements that the species-component of biodiversity should include all species (55%) or some types of non-native species (an additional 32%), which contrasts with the manner in which major biodiversity assessments and indicators are constructed. A majority of respondents in our sample (65%) also supported that measurement of the impact of invasive species should be based on the net biological, social, and economic effects, which also represents a marked departure from current methods that focus only on the adverse effects of a subset of NNS considered as invasive. Field of work and age were correlated with clusters and numerous individual responses. For example, biologists were three-times more likely than non-biologists to support a definition of species richness that included only native species. Two clusters (Cluster 1 and Cluster 3), mainly composed of non-biologists and biologists, respectively, differed in their support for statements that NNS would provide useful ecosystem services in the future (66% and 40%, respectively). Thus, a key result of this study is that a variety of normative stances regarding NNS is present within the scientific community. Current international indicators of progress (e.g., Aichi Targets) capture only a “nativist” set of values, which, if our sample is representative of the scientific community, appears to be a minority view. Therefore, we argue that indicators should be modified to integrate the diversity of views that exist within the scientific community.

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21

BAUER, HANS-GÜNTHER, and FRIEDERIKE WOOG. "On the ‘invasiveness’ of non-native bird species." Ibis 153, no. 1 (November 24, 2010): 204–6. http://dx.doi.org/10.1111/j.1474-919x.2010.01085.x.

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22

SCHLAEPFER, MARTIN A., DOV F. SAX, and JULIAN D. OLDEN. "The Potential Conservation Value of Non-Native Species." Conservation Biology 25, no. 3 (February 22, 2011): 428–37. http://dx.doi.org/10.1111/j.1523-1739.2010.01646.x.

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23

Burfeind, Dana D., Kylie A. Pitt, Rod M. Connolly, and James E. Byers. "Performance of non-native species within marine reserves." Biological Invasions 15, no. 1 (June 26, 2012): 17–28. http://dx.doi.org/10.1007/s10530-012-0265-2.

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24

Zhan, Aibin, Lei Zhang, Zhiqiang Xia, Ping Ni, Wei Xiong, Yiyong Chen, G. Douglas Haffner, and Hugh J. MacIsaac. "Water diversions facilitate spread of non-native species." Biological Invasions 17, no. 11 (July 10, 2015): 3073–80. http://dx.doi.org/10.1007/s10530-015-0940-1.

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25

Sagoff, Mark. "Do Non-Native Species Threaten The Natural Environment?" Journal of Agricultural and Environmental Ethics 18, no. 3 (May 2005): 215–36. http://dx.doi.org/10.1007/s10806-005-1500-y.

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26

Simberloff, Daniel. "Non-native Species DO Threaten the Natural Environment!" Journal of Agricultural and Environmental Ethics 18, no. 6 (December 2005): 595–607. http://dx.doi.org/10.1007/s10806-005-2851-0.

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27

Strayer, David L. "Non‐native species have multiple abundance–impact curves." Ecology and Evolution 10, no. 13 (June 4, 2020): 6833–43. http://dx.doi.org/10.1002/ece3.6364.

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28

Chance, Donald P., Johannah R. McCollum, Garrett M. Street, Bronson K. Strickland, and Marcus A. Lashley. "Native Species Abundance Buffers Non-Native Plant Invasibility following Intermediate Forest Management Disturbances." Forest Science 65, no. 3 (January 25, 2019): 336–43. http://dx.doi.org/10.1093/forsci/fxy059.

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Abstract The biotic resistance hypothesis (BRH) was proposed to explain why intermediate disturbances lead to greater resistance to non-native invasions proposing communities that are more diverse provide greater resistance. However, several empirical data sets have rejected the BRH because native and non-native species richness often have a positive relation. We tested the BRH in a mature loblolly pine (Pinus taeda) forest with a gradient of disturbance intensities including canopy reduction, canopy reduction + fire, and canopy reduction + herbicide and fire. We analyzed data from the study using a combination of Pearson’s correlation and beta regressions. Using species richness, we too would reject BRH because of a positive correlation in species richness between native and non-native plants. However, native species abundance was greatest, and non-native species abundance was lowest following intermediate disturbances. Further, native and non-native species abundances were negatively correlated in a quadratic relation across disturbance intensities, suggesting that native species abundance, rather than richness, may be the mechanism of resistance to non-native invasions. We propose that native species abundance regulates resistance to non-native invasions and that intermediate disturbances provide the greatest resistance because they promote the greatest native species abundance.

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29

Beckmann, Sean, Paloma Avila, and Terence Farrell. "Effect of native and non-native snake scents on foraging activity of native rodents in Florida." Journal of Mammalogy 103, no. 1 (November 24, 2021): 136–45. http://dx.doi.org/10.1093/jmammal/gyab124.

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Abstract Rodents use direct and/or indirect cues of predators to assess predation risk. The responses to these cues are well studied with regard to mammalian predators, but less understood with regard to reptilian predators. These responses are of particular importance in tropical and subtropical regions where reptile diversity is high and the likelihood of establishment of invasive reptilian predators also is high. We hypothesized that rodents would respond to direct scent cues of snake predators and that rodents would show greater aversion to scents of native snake predators than non-native snake predators. To assess this, scents of three snake species, two native and one non-native, and a non-snake control odor were distributed in Sherman live traps using a randomized block design. A total of 69 rodents representing four species were captured. Responses varied by species reinforcing that some species utilize indirect cues to assess predation risk, whereas others use direct cues. Moreover, one species (Neotoma floridana) showed a preference for non-native Python scent, indicating a lack of the appropriate anti-predator behavior, suggesting that some native rodents are more at risk of attack from invasive snakes than other native rodents.

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30

Warren, Robert J., Stacey Noezil, and Chloe Mokadam. "Non-native plants rarely provide suitable habitat for native gall-inducing species." Biodiversity and Conservation 30, no. 10 (June 11, 2021): 2797–805. http://dx.doi.org/10.1007/s10531-021-02222-7.

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31

Hierro, José L., Özkan Eren, Liana Khetsuriani, Alecu Diaconu, Katalin Török, Daniel Montesinos, Krikor Andonian, et al. "Germination responses of an invasive species in native and non-native ranges." Oikos 118, no. 4 (April 2009): 529–38. http://dx.doi.org/10.1111/j.1600-0706.2008.17283.x.

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32

Martin-Albarracin, Valeria L., Martin A. Nuñez, and Guillermo C. Amico. "Replacement of native by non-native animal communities assisted by human introduction and management on Isla Victoria, Nahuel Huapi National Park." PeerJ 3 (October 20, 2015): e1328. http://dx.doi.org/10.7717/peerj.1328.

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One of the possible consequences of biological invasions is the decrease of native species abundances or their replacement by non-native species. In Andean Patagonia, southern Argentina and Chile, many non-native animals have been introduced and are currently spreading. On Isla Victoria, Nahuel Huapi National Park, many non-native vertebrates were introduced ca. 1937. Records indicate that several native vertebrates were present before these species were introduced. We hypothesize that seven decades after the introduction of non-native species and without appropriate management to maintain native diversity, non-native vertebrates have displaced native species (given the known invasiveness and impacts of some of the introduced species). We conducted direct censuses in linear transects 500 m long (n= 10) in parallel with camera-trapping (1,253 camera-days) surveys in two regions of the island with different levels of disturbance: high (n= 4) and low (n= 6) to study the community of terrestrial mammals and birds and the relative abundances of native and non-native species. Results show that currently non-native species are dominant across all environments; 60.4% of census records and 99.7% of camera trapping records are of non-native animals. We detected no native large mammals; the assemblage of large vertebrates consisted of five non-native mammals and one non-native bird. Native species detected were one small mammal and one small bird. Species with the highest trapping rate were red and fallow deer, wild boar, silver pheasant (all four species are non-native) and chucao (a native bird). These results suggest that native species are being displaced by non-natives and are currently in very low numbers.

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33

Saeed, Suhur, Nandita Deb, Linso Varghese, Bernice Thornhill, Ismail Al-Shaikh, and Christopher Warren. "Toxicity to residual chlorine: Comparison of sensitivity of native Arabian Gulf species and non-native species." International Journal of Scientific Research in Environmental Science and Toxicology 4, no. 1 (April 2, 2019): 1–11. http://dx.doi.org/10.15226/2572-3162/4/1/00126.

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Chlorine is extensively used as a powerful oxidizing agent in the countries surrounding the Arabian Gulf for water treatment and biofouling control. Its usage has been increasing significantly as demand for water grows considerably both in industry and for domestic use. This is due to the fact that it is a well-tested technology, has had a history of long-term worldwide industrial use and is of acceptable cost. While the Arabian Gulf waters support a range of coastal and pelagic marine habitats including mangrove forests, seagrass meadows and coral reefs, marine organisms in these waters are living close to their tolerance limits due to the extreme environmental stressors like temperature and salinity. Anthropogenic stressors such as chlorine may further exacerbate these natural stressors. In seawater, chlorine produces a mixture of hypochlorous acid and hypochlorite ion. These rapidly react with the bromide ion to form a mixture of hypobromous and hypobromite ion. Total residual oxidants formed by chlorination although are short lived and not persistent in seawater, they can be quite toxic. In the present study, toxicity data were obtained from 7 acute toxicity tests and 3 chronic toxicity tests using Arabian Gulf aquatic species from different trophic levels. The study also examined the effect of temperature and developmental stages on toxicity of chlorine. Furthermore, differences in the species sensitivity distribution between native and non-native species were compared. The main finding of the study showed that there was no significant difference between native and non-native species for chlorine toxicity. This would suggest that toxicity data from different geographic region can be used in deriving site- specific ecological risk assessment of chlorine. Keywords: Chlorine; Arabian Gulf; acute toxicity; chronic toxicity; risk assessment; species sensitivity distribution;

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34

Nishimura, Takeshi. "Determinants of Attitudes Regarding the Control of Non-Native Species and the Conservation of Native Species." Journal of Rural Problems 50, no. 1 (2014): 43–48. http://dx.doi.org/10.7310/arfe.50.43.

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35

Hunter, Molly E., Philip N. Omi, Erik J. Martinson, and Geneva W. Chong. "Establishment of non-native plant species after wildfires: effects of fuel treatments, abiotic and biotic factors, and post-fire grass seeding treatments." International Journal of Wildland Fire 15, no. 2 (2006): 271. http://dx.doi.org/10.1071/wf05074.

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Establishment and spread of non-native species following wildfires can pose threats to long-term native plant recovery. Factors such as disturbance severity, resource availability, and propagule pressure may influence where non-native species establish in burned areas. In addition, pre- and post-fire management activities may influence the likelihood of non-native species establishment. In the present study we examine the establishment of non-native species after wildfires in relation to native species richness, fire severity, dominant native plant cover, resource availability, and pre- and post-fire management actions (fuel treatments and post-fire rehabilitation treatments). We used an information-theoretic approach to compare alternative hypotheses. We analysed post-fire effects at multiple scales at three wildfires in Colorado and New Mexico. For large and small spatial scales at all fires, fire severity was the most consistent predictor of non-native species cover. Non-native species cover was also correlated with high native species richness, low native dominant species cover, and high seeded grass cover. There was a positive, but non-significant, association of non-native species with fuel-treated areas at one wildfire. While there may be some potential for fuels treatments to promote non-native species establishment, wildfire and post-fire seeding treatments seem to have a larger impact on non-native species.

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36

Thomas, Chris D., and G. Palmer. "Non-native plants add to the British flora without negative consequences for native diversity." Proceedings of the National Academy of Sciences 112, no. 14 (March 23, 2015): 4387–92. http://dx.doi.org/10.1073/pnas.1423995112.

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Plants are commonly listed as invasive species, presuming that they cause harm at both global and regional scales. Approximately 40% of all species listed as invasive within Britain are plants. However, invasive plants are rarely linked to the national or global extinction of native plant species. The possible explanation is that competitive exclusion takes place slowly and that invasive plants will eventually eliminate native species (the “time-to-exclusion hypothesis”). Using the extensive British Countryside Survey Data, we find that changes to plant occurrence and cover between 1990 and 2007 at 479 British sites do not differ between native and non-native plant species. More than 80% of the plant species that are widespread enough to be sampled are native species; hence, total cover changes have been dominated by native species (total cover increases by native species are more than nine times greater than those by non-native species). This implies that factors other than plant “invasions” are the key drivers of vegetation change. We also find that the diversity of native species is increasing in locations where the diversity of non-native species is increasing, suggesting that high diversities of native and non-native plant species are compatible with one another. We reject the time-to-exclusion hypothesis as the reason why extinctions have not been observed and suggest that non-native plant species are not a threat to floral diversity in Britain. Further research is needed in island-like environments, but we question whether it is appropriate that more than three-quarters of taxa listed globally as invasive species are plants.

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37

Heiman, KW, N. Vidargas, and F. Micheli. "Non-native habitat as home for non-native species: comparison of communities associated with invasive tubeworm and native oyster reefs." Aquatic Biology 2 (March 5, 2008): 47–56. http://dx.doi.org/10.3354/ab00034.

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38

Clements, Stephanie L., Shantel V. L. Catania, and Christopher A. Searcy. "Non-native species dominate herpetofaunal community patterns in both native and non-native habitat patches in urban Miami-Dade County." Biological Invasions 21, no. 5 (February 6, 2019): 1775–88. http://dx.doi.org/10.1007/s10530-019-01934-w.

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39

Aksu, Sadi, Sercan Başkurt, Özgür Emiroğlu, and Ali Serhan Tarkan. "Establishment and range expansion of non-native fish species facilitated by hot springs: the case study from the Upper Sakarya Basin (NW, Turkey)." Oceanological and Hydrobiological Studies 50, no. 3 (September 1, 2021): 247–58. http://dx.doi.org/10.2478/oandhs-2021-0021.

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Abstract Non-native species can enter new habitats and ecosystems in a variety of ways. Suitable ecological conditions must exist for non-native species to reproduce in newly colonized habitats. Hot springs are suitable habitats for tropical, aquarium, and ornamental fish species. This paper presents the results of research on the distribution of non-native and native species in relation to environmental factors in the Upper Sakarya Basin, where several such springs are present. The fish fauna in the basin includes native (60% – 21 species, 14 of which are endemic) and non-native (40% – 14 species) fish species. Most of the non-native species (seven species) were found only in warm springs (minimum water temperature 16°C). In addition, 75 fish species belonging to 26 families were found throughout the Sakarya Basin. Hot springs were found to play an important role in the establishment of non-native species. The Kernel Density Estimation (KDE) results revealed that the non-native species density was high in the Upper Sakarya Basin where hot springs are common. This confirms that minimum and maximum temperatures are the main drivers of changes in the distribution of non-native fish species. Two aquarium fishes, Bujurguina vittata and Xiphophorus spp., are reported for the first time in the present study for inland waters of Turkey.

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40

Xiang, Tao, Xianghong Dong, and Gaël Grenouillet. "Ecological and biological traits of non-native freshwater fish species differentiate them from native species in China." Ecological Indicators 131 (November 2021): 108218. http://dx.doi.org/10.1016/j.ecolind.2021.108218.

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Smiley-Walters, Sarah A., Terence M. Farrell, and H. Lisle Gibbs. "The importance of species: Pygmy rattlesnake venom toxicity differs between native prey and related non-native species." Toxicon 144 (March 2018): 42–47. http://dx.doi.org/10.1016/j.toxicon.2018.01.022.

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Flores-Moreno, Habacuc, Peter B. Reich, Eric M. Lind, Lauren L. Sullivan, Eric W. Seabloom, Laura Yahdjian, Andrew S. MacDougall, et al. "Climate modifies response of non-native and native species richness to nutrient enrichment." Philosophical Transactions of the Royal Society B: Biological Sciences 371, no. 1694 (May 19, 2016): 20150273. http://dx.doi.org/10.1098/rstb.2015.0273.

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Ecosystem eutrophication often increases domination by non-natives and causes displacement of native taxa. However, variation in environmental conditions may affect the outcome of interactions between native and non-native taxa in environments where nutrient supply is elevated. We examined the interactive effects of eutrophication, climate variability and climate average conditions on the success of native and non-native plant species using experimental nutrient manipulations replicated at 32 grassland sites on four continents. We hypothesized that effects of nutrient addition would be greatest where climate was stable and benign, owing to reduced niche partitioning. We found that the abundance of non-native species increased with nutrient addition independent of climate; however, nutrient addition increased non-native species richness and decreased native species richness, with these effects dampened in warmer or wetter sites. Eutrophication also altered the time scale in which grassland invasion responded to climate, decreasing the importance of long-term climate and increasing that of annual climate. Thus, climatic conditions mediate the responses of native and non-native flora to nutrient enrichment. Our results suggest that the negative effect of nutrient addition on native abundance is decoupled from its effect on richness, and reduces the time scale of the links between climate and compositional change.

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Irz, P., C. Argillier, and J. P. Proteau. "Contribution of native and non-native species to fish communities in French reservoirs." Fisheries Management and Ecology 11, no. 3-4 (June 2004): 165–72. http://dx.doi.org/10.1111/j.1365-2400.2004.00396.x.

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Brison, Jeremy, Michael A. Robinson, Danielle S. W. Benoit, Shin Muramoto, Patrick S. Stayton, and David G. Castner. "TOF-SIMS 3D Imaging of Native and Non-Native Species within HeLa Cells." Analytical Chemistry 85, no. 22 (November 5, 2013): 10869–77. http://dx.doi.org/10.1021/ac402288d.

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Sueiro, María Cruz, Evangelina Schwindt, María Martha (Pitu) Mendez, and Alejandro Bortolus. "Interactions between ecosystem engineers: A native species indirectly facilitates a non-native one." Acta Oecologica 51 (August 2013): 11–16. http://dx.doi.org/10.1016/j.actao.2013.05.001.

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van Breukelen, Natalie April. "Interactions between native and non-native cichlid species in a Costa Rican river." Environmental Biology of Fishes 98, no. 3 (July 19, 2014): 885–89. http://dx.doi.org/10.1007/s10641-014-0322-z.

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Sexton, Ian, Philip Turk, Lindsay Ringer, and Cynthia S. Brown. "Slash Pile Burn Scar Restoration: Tradeoffs between Abundance of Non-Native and Native Species." Forests 11, no. 8 (July 28, 2020): 813. http://dx.doi.org/10.3390/f11080813.

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The accumulation of live and dead trees and other vegetation in forests across the western United States is producing larger and more severe wildfires. To decrease wildfire severity and increase forest resilience, foresters regularly remove excess fuel by burning woody material in piles. This common practice could also cause persistent ecosystem changes such as the alteration of soil physical and chemical properties due to extreme soil heating, which can favor invasion by non-native plant species. The abundance and species richness of native plant communities may also remain depressed for many years after burning has removed vegetation and diminished propagules in the soil. This adds to the vulnerability of burned areas to the colonization and dominance by invasive species. Research into the use of revegetation techniques following pile burning to suppress invasion is limited. Studies conducted in various woodland types that investigated revegetation of pile burn scars have met with varying success. To assess the effectiveness of restoring pile burn scars in Rocky Mountain National Park, Colorado, we monitored vegetation in 26 scars, each about 5 m in diameter, the growing season after burning. Later that summer, we selected 14 scars for restoration that included soil scarification, seed addition, and pine duff mulch cover. We monitored the scars for four years, pre-restoration, and three years post-restoration and found that the cover of seeded species exceeded the surrounding unburned areas and unseeded controls. The restoration seeding suppressed cover of non-native species as well as native species that were not seeded during restoration. Our results suggest that restoration of pile burn scars could be a useful tool to retard the establishment of invasive plant species when there are pre-existing infestations near scars. However, this must be weighed against the simultaneous suppression of native species recruitment. Monitoring for periods more than three years will help us understand how long the suppression of native and non-native species by restoration species may persist.

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Gonzales, E. K., Y. F. Wiersma, A. I. Maher, and T. D. Nudds. "Positive relationship between non-native and native squirrels in an urban landscape." Canadian Journal of Zoology 86, no. 5 (May 2008): 356–63. http://dx.doi.org/10.1139/z08-006.

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Paradoxically, non-native species sometimes displace native species that appear to be well adapted to local landscapes. That many landscapes have been altered by humans, creating habitat suitable for non-native species, helps explain this apparent paradox. We asked whether the abundance of native Douglas ( Tamiasciurus douglasii (Bachman, 1839)) and northern flying ( Glaucomys sabrinus (Shaw, 1801)) squirrels was best explained by the abundance of non-native eastern grey squirrels ( Sciurus carolinensis Gmelin, 1788), the proportion of urban development, or both using available squirrel abundance data from wildlife shelters and land-use maps. There was no evidence that non-native squirrels replaced native squirrels given that their abundances were positively related, whereas native squirrels varied negatively with the amount of development. The best model explaining variation in the abundance of Douglas and northern flying squirrels incorporated both eastern grey squirrels and development, which is consistent with the hypothesis that regional declines in native squirrels are more likely to be predicated by the alteration of native conifer habitats by humans independent of the effects of non-native squirrels.

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SIMONOVIC, P., A. TOŠIĆ, M. VASSILEV, A. APOSTOLOU, D. MRDAK, M. RISTOVSKA, V. KOSTOV, et al. "Risk assessment of non-native fishes in the Balkans Region using FISK, the invasiveness screening tool for non-native freshwater fishes." Mediterranean Marine Science 14, no. 2 (June 21, 2013): 369. http://dx.doi.org/10.12681/mms.337.

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A high level of freshwater fish endemism in the Balkans Region emphasizes the need for non-native species risk assessments to inform management and control measures, with pre-screening tools, such as the Fish Invasiveness Screening Kit (FISK) providing a useful first step. Applied to 43 non-native and translocated freshwater fishes in four Balkan countries, FISK reliably discriminated between invasive and non-invasive species, with a calibration threshold value of 9.5 distinguishing between species of medium and high risk sensu lato of becoming invasive. Twelve of the 43 species were assessed by scientists from two or more Balkan countries, and the remaining 31 species by a single assessor. Using the 9.5 threshold, three species were classed as low risk, 10 as medium risk, and 30 as high risk, with the latter category comprised of 26 moderately high risk, three high risk, and one very high risk species. Confidence levels in the assessments were relatively constant for all species, indicating concordance amongst assessors.

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Nichols, William F., and Virginia C. Nichols. "Newly Documented Non-Native Plant Species For New Hampshire." Rhodora 117, no. 972 (October 2015): 485–89. http://dx.doi.org/10.3119/15-18.

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