1 2 Supplementary Information 3 Assessing toxicity of copper nanoparticles across five cladoceran species 4 Lan Song*, 1, Martina G. Vijver1, Geert R. de Snoo1, Willie J.G.M. Peijnenburg1, 2 5 1 Institute of Environmental Sciences (CML), University Leiden, Leiden, The Netherlands 6 2 National Institute for Public Health and the Environment, Bilthoven, The Netherlands. 7 *Correspondences: song@cml.leidenuniv.nl 8 9 Supplementary Information 1. Measured concentrations versus the nominal concentrations 10 of all the CuNPs suspensions and Cu(NO3)2 at 0.1 and 0.01 mg/L, expressed as the mean ± 11 standard deviation. And the normalized percentage (%) of measured concentration versus 12 nominal concentrations, expressed as mean ± standard deviation. 13 Nominal concentration (mg/L) Percentage (%) Measured concentration (mg/L) 14 15 16 17 0.1 mg/L 0.01 mg/L 25 nm 0.132 ± 0.003 0.013 ± 0.001 132.7 ± 0.2 50 nm 0.123 ± 0.015 0.010 ± 0.002 109.7 ± 18.9 78 nm 0.063 ± 0.003 0.008 ± 0.002 70.8 ± 10.4 100 nm 0.064 ± 0.002 0.006 ± 0.000 62.1 ± 2.6 500 nm 0.156 ± 0.001 0.016 ± 0.001 158.2 ± 2.7 Cu(NO3)2 0.100 ± 0.000 0.001 ± 0.000 100±0.0 18 Supplementary Information 2. Body length was defined as the length from the top of the 19 eyespot to the base of the tail spine (a) was measured for each organism (Oda et al. 2011). 20 Width of carapace (b) and the thickness of the body (c) were measured as well. 21 22 23 Figure 5. The Simplified morphology of daphnids 24 Surface area of the species from family of daphniidae was treated as ellipsoid and calculated 25 by Knud Thomsen approximation (Klamkin 1976a, Klamkin 1976b) (Eq. 1). Body volumes 26 were calculated according Eq. 2 27 28 𝑎 𝑝 𝑏 𝑝 2 2 𝑎 𝑝 𝑐 𝑝 2 2 𝑏 𝑝 𝑐 𝑝 2 2 ( ) ( ) +( ) ( ) +( ) ( ) 𝑆 = 4𝜋 ( 3 4 𝑎 𝑏 1⁄ 𝑝 ) 𝑐 𝑉 = 3 𝜋 (2 × 2 × 2) 29 Where S is the surface area of organism. a, b and c are shown in Figure 1. p ≈ 1.61. 30 The body of C. sphaericus is close to spherical. The surface area and body volume of C. 31 sphaericus were calculated as Eq. 3 and Eq. 4 Eq. 1 Eq. 2 32 S= 4 π (a/2)2 Eq. 3 33 V = 4/3 π (a/2)3 Eq. 4 34 35 36 37 where S and V are the surface area and body volume of C. sphaericus, respectively. a is one-half of body length of C. sphaericus. 38 Supplementary Information 3. The relative toxic contribution of particulates in the CuNPs 39 suspensions and the relative toxic contribution of ions, expressed as mean ± standard 40 deviation. LC50 caused by particulates in each suspension is listed in table below. 41 42 The calculation detail has been reported in previous study (Song et al. 2014). Briefly, it was 43 assumed that the release of copper ions is independent of the concentration of CuNPs and 44 there are no interactions between Cu2+ and CuNPs. The toxicity of Cu2+ (ECu2+) in the copper 45 suspensions could be determined according to the concentration–response curve of Cu(NO3)2. 46 The total toxicity of copper suspensions was assessed experimentally. Therefore, the toxic 47 effect of the particle form of the CuNPs (ECuNPs) can be estimated using the response addition 48 model: 49 ECuNPs =1-[(1- Etotal)/(1- ECu2+)] 50 Where Etotal represents the total toxicity caused by the copper suspensions. ECuNPs and ECu2+ 51 represent the toxicity caused by the particle form of CuNPs and Cu2+, respectively. 52 53 54 Supplementary Information 4. 48-h LC50sus of CuNPs suspensions, SMP suspension and Cu(NO3)2 to five cladoceran species, plotted as the 55 mean of eight replicates ± standard deviation. LC50sus (mg/L) 25 nm 50 nm 78 nm 100 nm 500 nm Cu2+ D. magna 0.100 ± 0.02 0.136 ± 0.017 0.791 ± 0.035 0.096 ± 0.012 0.099 ± 0.01 0.020 ± 0.001 D. pulex 0.009 ± 0.001 0.044 ± 0.004 0.166 ± 0.014 0.062 ± 0.004 0.034 ± 0.004 0.017 ± 0.003 D. galeata 0.012 ± 0.001 0.061 ± 0.006 0.148 ± 0.017 0.040 ± 0.005 0.020 ± 0.003 0.015 ± 0.002 C. sphaericus 0.052 ± 0.011 0.045 ± 0.01 0.077 ± 0.005 0.032 ± 0.005 0.017 ± 0.002 0.013 ± 0.002 C. dubia 0.003 ± 0.001 0.002 ± 0.0003 0.015 ± 0.002 0.003 ± 0.001 0.006 ± 0.001 0.006 ± 0.001 56 Supplementary Information 5. Body length, surface area and body volume of neonates of each tested species, expressed as mean of ten 57 replicates ± standard deviation. Morphological data D. magna D. pulex D. galeata C. sphaericus C. dubia Body length (mm) 1.10 ± 0.04 0.86 ± 0.03 0.73 ± 0.01 0.23 ± 0.04 0. 21 ± 0.01 Surface area (mm2) 1.73 ± 0.11 0.93 ± 0.07 0.72 ± 0.10 0.14 ± 0.03 0.06 ± 0.005 0.19 ± 0.02 0.07 ± 0.01 0.05 ± 0.01 0.005 ± 0.002 0.001 ± 0.001 Body volume (mm3) 58 Supplementary Information 6. The total toxicity (%) caused by copper suspensions 59 (CuNPs) (green), and the toxicity (%) caused by particle forms of each copper suspension 60 (CuNPs) (red) and Cu2+ (blue) plotted against the total copper concentrations, respectively. 61 Results are expressed as means ± standard deviation. 62 63 64 Supplementary Information 7. The LC50particle caused by NPs only in each suspension (mg/L), the calculation is based on the results in 65 Supplementary Information 6. 66 67 LC50particle (mg/L) 25 nm 50 nm 78 nm 100 nm 500 nm D. magna 0.103 ± 0.012 0.152 ± 0.032 1.054 ± 0.103 0.099 ± 0.026 0.106 ± 0.032 D. pulex 0.007 ± 0.001 0.040 ± 0.005 0.164 ± 0.016 0.052 ± 0.003 0.030 ± 0.002 D. galeata 0.010 ± 0.001 0.055 ± 0.008 0.149 ± 0.022 0.033 ± 0.005 0.017 ± 0.002 C. sphaericus 0.052 ± 0.024 0.045 ± 0.021 0.075 ± 0.005 0.027 ± 0.004 0.015 ± 0.002 C. dubia 0.002 ± 0.001 0.002 ± 0.001 0.015 ± 0.002 0.003 ± 0.001 0.006 ± 0.001 68 Supplementary Information 8. The actual sizes of CuNPs are plotted against the 69 corresponding toxicities caused by particles in each CuNPs suspension to five cladoceran 70 species. 10 48-h LC50 (mg/l) 1 0.1 0.01 0.001 0 D. magna 71 72 100 D. pulex 200 300 Actual size (nm) D. galeata C. dubia 400 C. sphaericus 73 74 75 Reference 76 The American Mathematical Monthly, March. 280-283 77 Klamkin MS. 1976b.Corrections to" Elementary Approximations to the Area of N- 78 Dimensional Ellipsoids" The American Mathematical Monthly 83: 478 79 Oda S, Kato Y, Watanabe H, Tatarazako N, Iguchi T. 2011. Morphological changes in 80 Daphnia galeata induced by a crustacean terpenoid hormone and its analog. Environ Toxicol 81 Chem 30: 232–238 82 Song L, Connolly M, Fernández-Cruz ML, Vijver MG, Fernández M, Conde E, de Snoo GR, 83 Peijnenburg WJ, Navas JM. 2014. Species-specific toxicity of copper nanoparticles among 84 mammalian and piscine cell lines. Nanotoxicology 8: 383-393 Klamkin MS. 1976a. Elementary Approximations to the Area of N-Dimensional Ellipsoids.