Hypoxia: Problems and Scientific Challenges Prof. Rudolf Wu School of Biological Sciences The University of Hong Kong (rudolfwu@hku.hk) Hypoxia: An Old Problem with New Insights Hypoxia: Trend During the last few decades, anthropogenic input of nutrients into our coastal environment has increased ca. three folds, and is expected to double or triple if no action is taken Hypoxia: Trend Decrease in dissolved oxygen recorded over large coastal areas worldwide (including USA, China, Norway, UK, Sweden, Germany, Denmark, the Black Sea, Adriatic Seas) in the last 30-80 years Diaz & Rosenberg, 1995; Rabalais, 2001 Total area>245,000 km2 Number of Dead Zones doubled every 10 years since the 1960s Diaz & Rosenberg, 2008 Hypoxia Has Caused Major Changes in Structure and Functions of Ecosystems – – – – Mass mortality of fish and benthos Changes in species composition Changes in trophic relationships Decrease in biodiversity and species richness – Decrease in fisheries production Phil, 1994; Wu, 2002; Gray et al., 2002 Wu, 2002; Gray et al., 2002 Generalized Changes in Structure and Functions of Ecosystems Normoxia Suspended feeders Diversity, Species richness Demersal fish Larger body size Predator Hypoxia Deposit feeders Meiofauna, Nanoplankton Pelagic fish Short life cycle Wu, 2002 New Scientific Evidence further show that….. Hypoxia is an endocrine disruptor Common carp (Cyprinus carpio) Male Estradiol Testosterone 10 0.3 9 8 7 (ng/ml) 0.2 6 5 4 3 ** 7.0 mg/L 7.0 mg/L 1.0 mg/L 1.0 mg/L 0.1 *** 2 1 0 0 ** p<0.01; *** p<0.001 Wu et al, 2003 Female 10 8 (ng/ml) 6 7.0 mg/L 1.0 mg/L 4 2 *** * 0 Testosterone Estradiol * p<0.05; *** p<0.001 Wu et al, 2003 Hypoxia impairs fish reproduction • Gonadal • Fertility development • Gamete quality • Gametogenesis • Offspring survival • Spawning • Reproductive behavior • Fecundity Common carp Zebrafish Atlantic croaker Gulf killifish (Wu et al. 2003) (Shang et al. 2006) (Thomas et al. 2006,2007) (Landry et al. 2007) Sperm Motility 80 70 60 * 50 µmS-1 7 mg/L 1 mg/L 40 30 * 20 * 10 0 Curvilinear velocity Straight Line velocity Actual Path velocity * p < 0.05 Wu et al, 2003 Reproductive Impairment 100 90 80 % 70 60 50 40 *** *** 30 20 10 0 7 mg/L 1 mg/L *** *** Fertilization Hatching Larval Survival Egg to Larvae *** p < 0.001 Wu et al, 2003 Follow-up questions: What caused the observed endocrine disruption? • A smaller gonad and reduced hormone production due to reduced energy intake and reduced growth? • Hypoxia affects synthesis and metabolism of sex hormones? • Hypoxia affects GnRH and gonadotropins? In vitro evidence • In vitro studies using H295R human adrenocortical carcinoma cell line and primary cell culture of medaka gonads StAR Cholesterol CYP17 17α-OH- CYP11A Pregnenolone CYP17 DHEA Pregnenolone 3β-HSD 3β-HSD 3β-HSD Progesterone CYP17 CYP17 Androstene-dione 17α-OHProgesterone 17β-HSD CYP21 CYP21 11-Deoxy-corticosterone Testosterone 11-Deoxycortisol CYP11B1 CYP19 CYP11B1 Corticosterone 17β-Estradiol Cortisol CYP11B2 Zona reticularis Aldosterone Zona fasciculata Zona glomerulosa Hypoxia is a teratogen Zebrafish (Danio rerio) Hypoxia delays development 24hpf 48hpf Control Hypoxia (0.5mg/l) Shang & Wu, 2004 Hypoxia caused spine and cardiac malformations ** Malformation (%) 20 * ** 15 5.8 mg/L 0.8 mg/L * p < 0.05; ** p < 0.01 10 5 0 48h 72h 96h Time (hour) 120h 168h Shang & Wu, 2004 Under hypoxia, apoptosis concentrates in the head but not the tail Control Hypoxia Shang & Wu, 2004 Gonads differentiate into ovaries Sex differentiation begins 3-HSD (-) CYP11A (-) CYP19A (ND) CYP19B (-) Sex differentiation/ reversal completed Female 3-HSD (-) CYP11A (-) CYP19A (+) CYP19B (NC) T/E2 (+) Female 3-HSD (+) CYP11A (-) CYP19A (+) CYP19B (+) T/E2 (+) (B) 40 dpf (C) 60 dpf 23-25 dpf 10-12 dpf Larval 3 dpf 42 dpf Spawning Male 3-HSD (-) CYP11A (-) CYP19A (+) CYP19B (+) T/E2 (NC) Male 3-HSD (-) CYP11A (-) CYP19A (-) CYP19B (NC) T/E2 (NC) 3-HSD (-) CYP11A (-) CYP19A (-) CYP19B (-) (A) 10 dpf Final maturation of the gonads (D) 120 dpf 60 dpf Juvenile 30 dpf 120 dpf Adult 90 dpf Shang et al, 2006 Hypoxia tips sex balance & favors a male biased population male female *** 100% 90% 80% 70% % in F1 60% 61.9% 74.4% 50% 40% 30% 20% 10% 0% Normoxia Hypoxia *** p < 0.001 Shang, Yu & Wu, 2006 Where the girls are? Will this affect reproductive success of the natural population? Is the observed male biased phenotypic or geneotypic? Will the same happens to species with XY chromosomes? Phenotypic & gonadal Sex in genotypic females (O. latipes) are altered by hypoxia Cheung, 2006; Wu, 2009 Will the same occur in higher vertebrates? • Salamanders (Ambystoma sp.): delayed development and hatching, less developed and deformed embryos • Australian frog (Crinia georgiana): delayed embryonic development, increased malformation • Male albino rats: reduced numbers of sertoli cells and Leydig cells in testis • Male Wistar rats: lower levels of LH and testosterone Seymonr et al., 2000; Shevantaeva & Kosyuga, 2006; Farias et al., 2007 Will the same occur in invertebrates? 10 A 80 60 40 20 0 No.of offspring % copulation 100 *** 7.50 4.50 1.0 4 2 *** 7.50 4.50 3.50 50 D C Fecundity No. of broods 6 0 3.50 B 8 0.5 Methyl farnesoate? 40 30 20 10 0.0 *** 7.50 4.50 0 3.50 -1 Dissolved oxygen (mg O2 L ) *** 7.50 4.50 3.50 Dissolved oxygen (mg O2 L-1) Ecdysteroid? *** p<0.005 Wu & Orr, 2005 Is the situation getting better or getting worse? The situation is likely to get worse because….. • Growth of treatment facilities is unlikely to catch up with growth of population and industry, especially in developing counties • Contributions from atmospheric fallout and nonpoint source are significant • Trans-boundary issues are difficult to resolve Global Warming Increase Temperature Increase freshwater input Increase nutrient flux Increase stratification Nutrient enrichment Enhanced productivity Sediment Hypoxia Increase metabolic rate Risk Assessment • • • • • • Ecological consequence Area affected Socioeconomic loss No. people affected Probability of occurrence Trend Very serious Very large Very big Very large Very high Getting worse The new scientific evidence presented here calls for an urgent re-assessment of this old problem Will the same happen in humans? • Patients suffering from sleeping apnea have lower sex drive and testosterone level (Saaresranta & Polo, 2003) • Sex ratio in human depends on level of sex hormones of father and mother during conception, and high testosterone level during conception favors subsequent birth of sons (James, 2004) Summary of effects of hypoxia on The HPG axis in female zebrafish ER GnRH FSH Pituitary FSH CYP19A (+) E2 Blood E2 Ovary CYP19A Brain sGnRH FSH-R HMGR LH (+)? Progestin ? Proposed Work Collaborate with fisheries authorities and undertake a scientific global review, focusing on : – Trend analysis (spatial and level in the last 50 years) – Changes in structure and trophodynamics of marine communities (plankton, benthos, fish) – Identification of sensitive groups (bioindicators) Proposed Work Collaborate with fisheries authorities and undertake a scientific global review, focusing on : – Reproductive status and reproductive impairment of fish in hypoxic areas vs normoxic areas – Endocrine disruption, malformation, sex ratio – Deciphering effects of hypoxia from those caused by other anthropogenic activities (chemicals) prevailing simultaneously in the marine environment?? – Identifying information gaps and further studies 70 9 *** 50 *** 40 30 *** 20 10 No. of cysts/lobule zebrafish 60 8 common carp *** 7 6 5 4 3 2 *** 1 0 SPG SPC SPD 0 SPG SPC ** SPD common carp 300 Diameter (m)/Lobule % of each stage in testis Hypoxia affects spermatogenesis 250 200 *** 150 Normoxia Hypoxia ** p < 0.01; *** p < 0.001 100 50 0 Normoxia Hypoxia Wu et al., 2003; Shang et al., 2006 70 zebrafish Atlantic croaker PNS *** 60 50 CA PYS SYS TYS 100% 40 80% *** 30 20 *** 10 0 Oo PreV Vit *** *** p < 0.001 60% 40% PreO Ovarian cell stage Normoxia % of oocytes % of each stage in oocyte Hypoxia affects Oogenesis 20% Hypoxia 0% Control 2.7 mg/L 1.7 mg/L Shang et al., 2006; Thomas et al., 2007 Landry et al., 2007