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. 2018 Aug 23;16(8):e05377. doi: 10.2903/j.efsa.2018.5377

Table 17.

Calculated EP50 (endpoint mortality plus immobility) and corresponding HP5 values (and 95% confidence limits) for all 13 aquatic arthropods (see Table 9) and exposure profiles of exposure scenarios A‐F by using the GUTS‐RED‐SD model

Exposure scenarios
A B C D E F
EP50 values GUTS‐RED‐SD
1 Daphnia magna 13 (7–61) 5 (2–33) 18 (11–83) 7 (4–35) 3 (2–14) 5 (3–25)
2 Asellus aquaticus 762 (250–1,285) 391 (92–635) 1,035 (340–1,682) 420 (138–682) 181 (58–305) 303 (85–587)
3 Gammarus pulex 37 (6–62) 13 (1–23) 49 (6–85) 20 (2–34) 9 (0.1–15) 13 (1–23)
4 Neocaridina denticulata 42,500 (29,219–63,750) 14,375 (9,883–26,504) 57,500 (39,531–86,250) 22,500 (16,172–36,563) 9,688 (6,660–15,894) 14,375 (9,883–24,482)
5 Procambarus spec. 264 (206–330) 142 (106–174) 352 (275–467) 146 (119–192) 67 (54–92) 129 (105–162)
6 Chironomus riparius 93 (75–122) 38 (28–52) 127 (103–163) 51 (40–67) 23 (18–30) 37 (30–48)
7 Anax imperator 469 (432–501) 291 (272–304) 630 (582–674) 261 (243–286) 121 (114–126) 278 (241–283)
8 Cloeon dipterum 98 (75–110) 57 (40–64) 132 (101–153) 54 (42–61) 24 (18–27) 49 (30–57)
9 Notonecta maculata 1,162 (890–1,344) 542 (333–805) 1,572 (1,203–1,824) 640 (492–748) 276 (216–328) 437 (315–628)
10 Paraponyx stratiotata 557 (533–598) 344 (331–363) 747 (695–817) 313 (300–333) 143 (139–150) 320 (288–360)
11 Plea minutissima 444 (392–491) 271 (231–299) 596 (531–661) 247 (223–272) 112 (91–125) 247 (171–286)
12 Ranatra linearis 1,709 (1,282–2,016) 1,025 (793–1,170) 2,285 (2,000–2,633) 947 (760–1,111) 417 (313–484) 796 (569–1,057)
13 Sialis lutaria 109 (60–177) 50 (27–100) 146 (96–239) 60 (39–98) 26 (13–420) 40 (26–78)
Median HP5 (log‐normal) (95% confidence interval) 15 (5–80) 7.3 (2–40) 21 (6.6–110) 8.5 (2.6–47) 3.6 (0.9–20) 6.7 (1.9–35)